HomeMy WebLinkAbout98.11-16-2016 Board Item 23 Attachment - Final Initial Study-Mitigated Negative Declaration.pdf Orange County Water District
Water Production Enhancement
Project
Final Initial Study/Mitigated Negative Declaration
Mitigation Monitoring Program
State Clearinghouse No. 20160811067
Prepared By
Orange County Water District
18700 Ward Street
Fountain Valley, CA 92708
Contact: Daniel Bott U
October 2016 SINCE 1933
Table of Contents
SECTION PAGE
SECTION 1.0 INTRODUCTION................................................................................ill
SECTION 2.0 PROEECT DESCRIPTION.................................................................211
SECTION 3.0 DEVELOPMENT OF MITIGATION MONITORING REPORTING
PROGRAM........................................................................................311
SECTION 4.0 REQUIREMENT TO APPROVE AND IMPLEMENT MITIGATION
MONITORING PLAN.........................................................................411
TABLE
Table 1: Water Production Enhancement Project Mitigation Monitoring Program........4C2
OCWD Water Production Enhancement Project
%L;J Final ISMND Mitigation Monitoring Program i
Section 1
SECTION 1.0 INTRODUCTION
The following is a Mitigation Monitoring Report Program 1MMPDfor the Orange County
Water District Water Production Enhancement Project Final Initial Study/Mitigated
NegatiDa Declaration mS/MNDOprepared pursuant to Section 15097 of the CEQA
Guidelines and Section 21081.6 of the Public Resources Code. This MMP lists all
applicable mitigation measures from the Draft IS/MND for the Orange County Water
District Water Production Enhancement Project IS/MND. The appropriate timing of
implementation and responsible party are identified to ensure proper enforcement of the
mitigation measures from the Draft IS/MND.
4_'^ OCWD Water Production Enhancement Project
Final ISMND Mitigation Monitoring Program 1-1
Section 2
SECTION 2.0 PROJECT DESCRIPTION
Proposed Project
The proposed project inEbILes the construction and operation of a flow e0ualiEPtion tank
and pump station on the Orange County Sanitation District Plant No. 2 wastewater
treatment facility site. The secondary effluent from the flow eDualioation tank would
proElde an additional 6,000 acrelfeet per year of secondary effluent for treatment at the
Orange County Water District Groundwater Replenishment System [GWRS0adLanced
recycled water treatment facility, increasing the GWRS total full build out treatment
capacity to 134,000 acre feet per year.
Project Purpose
The OCWD Water Production Enhancement Project consists of a secondary effluent
flow ellialiCation tank proposed at OCSD® Plant No. 2 in order to receiCe maximum
water production at the OCWD GWRS water treatment facility. OCSD® Plant No. 2 is a
wastewater treatment facility which has Earying influent land effluentDflows of
secondary effluent. During the day, wastewater flows into OCSD® Plant No. 2 can peak
aboEle 140 million gallons per day [MGDD These peak flows cannot be pumped to the
GWRS facility due to the limits of the conD;yance facilities, i.e. effluent pump station
and pipeline; that deliCer the secondary effluent to GWRS. Therefore, a secondary
effluent flow eELaliEstion tank has been proposed at OCSDEs Plant No. 2 Site to capture
these peak flows during the day and store them in the 6Emillion gallon tank until
nighttime. During low flows at night, the flow eDualiDation tank would drain into the
effluent pump station to supplement the low secondary effluent inflows and allow the
GWRS to treat these peak flows which would haEB otherwise been discharged to the
ocean. The Water Production Enhancement Project in[bl as three construction
actidties: 10construction of flow e0uali0ation tank, 20construction of a pump station,
and 3Dconstruction of conCeyance piping and flow meter moult.
Project Location
The OCSD Plant No. 2 Site is located at 22212 Brookhurst Street within the City of
Huntington Beach. OCSD Plant No. 2 site is composed of 110 acres, and is deCeloped
with wastewater treatment structures, offices, and paced parking areas and roadways.
The site is bounded by Hamilton AElonue to the north, Brookhurst Street to the west,
Talbert Marsh and Talbert Marsh Bike Trail to the south and the Santa Ana RIEer and
the Santa Ana RiE,er Trail to the east. Primary regional access to Plant No. 2 would from
Interstate 405 from the Brookhurst Street exit. Primary local access would be from
Brookhurst Street and Pacific Coast Highway.
° OCWD Water Production Enhancement Project
Final ISMND Mitigation Monitoring Program 2-1
Section 3
SECTION 3.0 DEVELOPMENT OF MITIGATION MONITORING
REPORTING PROGRAM
The basic elements of the Mitigation Monitoring Program are the mitigation measures
identified by each impact category addressed in the Draft IS/MND. The deEblopment of
the program was based on the following procedures necessary to initiate and complete
the monitoring process.
• Identification of the key periods and eCents in the project implementation
schedule.
• Identification of the key personnel and agencies responsible for endronmental
monitoring.
• Monitoring of the implementation of the mitigation measures and documentation
that the measures hale been properly and thoroughly implemented.
• DeCelopment of the written document on the implementation of all the mitigation
measures, identification of any areas of non[Eompliance, and proposed actidties
to bring the project into compliance with the mitigation monitoring and reporting
program.
OCWD Water Production Enhancement Project
Final ISMND Mitigation Monitoring Program 3-1
Section 4
SECTION 4.0 REQUIREMENT TO APPROVE AND IMPLEMENT
MITIGATION MONITORING PLAN
The OCWD has the authority to re uire and enforce the prodsions of California
Resource Code Section 21081.6. The OCWD will be responsible for approing the
Mitigation Monitoring Program and for preparing the written report documenting the
implementation of project mitigation measures.
Table 1 summariUas the mitigation measures that haCe been adopted for the Project,
specifies the timing for implementation of each measure and identifies the responsible
parties for ensuring implementation and the satisfactory completion of each measure.
The procedures for implementing the Mitigation Monitoring Program are:
Monitoring Procedures
1. An En ironmental Monitor, appointed by OCWD, will be responsible for coordinating
redew of project plans and actidties, the construction site, and/or operations to ensure
that the mitigation measures are properly and thoroughly implemented through the
course of the project.
2. Written documentation that each mitigation measure in Table 1 has been
implemented will be prepared. This documentation can be on an OCWD mitigation
monitoring checklist or a similar form that clearly indicates the timing or schedule for
implementation, whether the measure has, in fact, been implemented, or in the case of
measures that are ongoing, that a process has been de-eloped to ensure continued
implementation of the measure.
Reporting Procedures
1. The Endronmental Monitor appointed by OCWD on this project will be responsible
for periodically redewing the program in Table 1 with the OCWD Endronmental
Compliance Addsor.
2. The Endronmental Monitor will prepare a written report for the OCWD documenting
the completion of the implementation of all the mitigation measures. For those
measures not implemented or for actidties that do not fully comply with mitigation
measures included in Table 1, an explanation of the areas of noncompliance will be
prepared, including a proposal to bring those elements of the project into compliance
with the Mitigation Monitoring Program.
° OCWD Water Production Enhancement Project
QJ Final ISMND Mitigation Monitoring Program 4-1
Section 4
Table 1: Water Production Enhancement Project Mitigation Monitoring Program
Mitigation Measure Responsible for Monitoring Verification
Implementation
Aesthetics
A-1: All onsite lighting shall be directed OCWD During
away from adjacent residential, business Construction
uses and away from the Santa Ana Ri[Br
rightlbf[way.
A-2: During operation of the project the
OCWD During
onsite lighting creates a light or glare issues Operation
for sensitilb receptor properties, OCWD will
implement correctilb measures to resol Ce
the issue. Such corrective measures may
include prodding additional shielding on
light fixtures, relocating lighting fixtures and
reducing the intensity of lighting.
Cultural Resources
CR-1: Prior to earth mo ing actidties, a OCWD During
DAalifed archaeologist meeting the Construction
Secretary of the Interiors Professional
Qualifications Standards for archaeology
[U.S. Department of the Interior, 2008avill
conduct cultural resources sensitidly
training for all construction personnel.
Construction personnel shall be informed of
the types of cultural resources that may be
encountered, and of the proper procedures
to be enacted in the scent of an inadvertent
discovery of archaeological resources or
human remains. OCWD will ensure that
construction personnel are made available
for and attend the training and retain
documentation demonstrating attendance.
CR-2: Prior to the start of any ground OCWD During
disturbing acti 7ties, OCWD will retain an Construction
archaeological monitor to observe all
ground[disturbing actilties.Archaeological
monitoring will be conducted by a monitor
familiar with the types of archaeological
resources that could be encountered and
shall work under the direct super Ision of
the ualified archaeologist. Monitoring may
be reduced or discontinued by the ualified
archaeologist, in coordination with OCWD,
based on obserlations of subsurface soil
stratigraphy and/or the presence of older Co
horl Con deposits.The monitor will be
empowered to halt or redirect ground)
disturbing act!dties away from the ❑cinity of
a discovery until the Dialifed archaeologist
has elaluated the discolary and
OCWD Water Production Enhancement Project
Final ISMND Mitigation Monitoring Program 4-2
Section 4
determined appropriate treatment. The
monitor will keep daily logs detailing the
types of acti0ties and soils obser[Bd, and
any discolbries.After monitoring has been
completed, the Dualified archaeologist shall
prepare a monitoring report that details the
results of monitoring.The report shall be
submitted to OCWD, SCCIC,and any
Natilb American groups who reDuest a
copy.
CR-3: In the event of the discolary of OCWD During
archaeological materials, OCWD or its Construction
contractor shall immediately cease all work
actidties in the area within approximately
100 feet0of the discovery until it can be
elaluated by the dalified archaeologist.
Prehistoric archaeological materials might
include obsidian and chart flakedr3tone
tools ®.g., projectile points, knives,
scrapersoor toolmaking debris; culturally
darkened soil ®nidden®containing healo
affected rocks, artifacts, or shellfish
remains; and stone milling e3,ipment [e.g.,
mortars, pestles, handstones,or milling
slabsq and battered stone tools, such as
hammerstones and pitted stones. Historic7l
period materials might include stone or
concrete footings and walls; filled wells or
prides; and deposits of metal,glass, and/or
ceramic refuse. Construction shall not
resume until the Elualifed archaeologist has
conferred with OCWD on the significance of
the resource. SWRCB shall be afforded the
opportunity to determine whether the
disco, ery reyires addressing under
Section 106 PostTtedew Discoveries
prodsions prodded in 36 CFR 800.13.
If it is determined that the discolbred
archaeological resource constitutes a
historic property under Section 106 of the
NHPA or a historical resource under CEOA,
avoidance and preser:13tion in place shall
be the preferred manner of mitigation.
Preser ation in place maintains the
important relationship between artifacts and
their archaeological context and also serves
to a oid conflict with traditional and religious
values of groups who may ascribe meaning
to the resource. Preservation in place may
be accomplished by, but is not limited to,
avaidance, incorporating the resource into
open space, capping, or deeding the site
into a permanent conserEation easement. In
the event that preserEation in place is
OCWD Water Production Enhancement Project
Final ISMND Mitigation Monitoring Program 4-3
Section 4
demonstrated to be infeasible and data
recoCery through ezcalbtion is the only
feasible mitigation albilable, an
Archaeological Resources Treatment Plan
that proddes for the adelliate recolbry of
the scientifically conseCuential information
contained in the archaeological resource
shall be prepared and implemented by the
Ilualifed archaeologist in consultation with
OCWD. The appropriate Nat!Ce American
representati as shall be consulted in
detemrining treatment for prehistoric or
Nance American resources to ensure
cultural values ascribed to the resource,
beyond that which is scientifically important,
are considered.
CR-4: Prior to issuance of a grading permit OCWD During
and prior to start of any ground[disturbing Construction
act!dties, OCWD will retain a Natilb
American monitor to obseria all ground
disturbing act!dties. The monitor shall be
obtained from a Tribe that is traditionally
and culturally affiliated with the area,
according the NAHC list. The monitor shall
be empowered to halt or redirect ground
disturbing acti Dties away from the Gcinity of
a discolbry until the dalifed archaeologist
has eLaluated the discoLary and
determined appropriate treatment.
Monitoring may be reduced or discontinued,
in coordination with OCWD and the
Ilualifed archaeologist, based on
obserCations of subsurface soil stratigraphy
and/or the presence of older CQioriCon
deposits.
CR-5: Prior to the start of any ground OCWD During
disturbing actidties, OCWD shall retain a Construction
Dialifed paleontologist meeting the Society
of Vertebrate Paleontology SVP❑
Standards ESVP, 2010C The dallfied
paleontologist shall contribute to any
construction worker cultural resources
sensitiDty training either in person or ❑a a
training module proDded to the ❑lalified
archaeologist.The training session shall
focus on the recognition of the types of
paleontological resources that could be
encountered within the project site and the
procedures to be followed if they are found.
The dalified paleontologist shall also
conduct periodic spot checks in order to
ascertain when older deposits are
encountered and where monitoring shall be
reDjired.
OCWD Water Production Enhancement Project
Final ISMND Mitigation Monitoring Program 4-4
Section 4
CR-6: Prior to the start of any ground OCWD During
disturbing act!Ities, OCWD shall retain a Construction
paleontological monitor to obserJa all
ground disturbing act! !ties within older
Quaternary deposits. Paleontological
resources monitoring shall be performed by
a Dualified paleontological monitor, or cross❑
trained archaeological/paleontological
monitor, under the direction of the ❑lalifed
paleontologist.The monitor shall halls the
authority to temporarily halt or client work
away from exposed fossils in order to
reco[Br the fossil specimens. Monitoring
may be reduced or discontinued by the
Dualified paleontologist, in coordination with
OCWD, based on obserlbtions of
subsurface soil stratigraphy and/or other
factors and if the Dualified paleontologist
determines that the possibility of
encountering fossiliferous deposits is low.
The monitor shall prepare daily logs
detailing the types of act!Aties and soils
obserCed, and any disco Caries.The
Dualified paleontologist shall prepare a final
monitoring a report to be submitted to
OCWD and fled with the local repository.
Any recoCered significant fossils shall be
curated at an accredited facility with
retrielable storage.
CR-7: If construction or other project OCWD During
personnel discolar any potential fossils Construction
during construction, regardless of the depth
or presence of a monitor,work in the ❑cinity
[within 100 feet0of the find shall cease until
the Dualified paleontologist has assessed
the discolary and made recommendations
as to the appropriate treatment.
Geology/Soils
GEO-1: The OCWD will ensure that all OCWD Design and
structures for the proposed project are Construction
designed and constructed in compliance
with current engineering practices, including
the California Uniform Building Code and all
applicable seismic engineering guidelines.
GEO.2: Prior to the start of construction OCWD Prior to
OCWD shall file a Notice of Intent INC IO Construction
with the State Water Resources Control
Board and prepare and implement Storm
Water Pollution Pre ention Plan to minim!]:
potential erosion impacts.
GEO.3:The OCWD will ensure that all OCWD Design and
structures for the proposed project are Construction
OCWD Water Production Enhancement Project
Final ISMND Mitigation Monitoring Program 4-5
Section 4
designed and constructed in compliance
with building site specific geotechnical
studies and the California Uniform Building
Code.
Hazards
HZ-1: Any use of halardous materials OCWD Construction
inmlLad with the proposed project must be and Operation
conducted in accordance with applicable
federal, state and local regulations.
HydrologyfNater Quality
HWQ-1: OCWD will coordinate with OCSD OCWD During Design
on the capacity of existing drainage OCSD
systems to race![])surface water runoff
generated from the proposed project and
would participate in any drainage
improvements reDtired accommodate the
surface water runoff flows.
Land Use
LU-1: OCWD will prodde residents and OCWD Prior to
business owners with notifications of Construction
upcoming construction act!i ties.
LU-2: Prior to construction of the Flow OCWD Prior to
E uali ation Tank OCWD will obtain Construction
appro al of Coastal Development Permit
from the City of Huntington Beach.
Traffic/Transportation
T-1: OCWD will be responsible for OCWD Prior to
preparing adeDiate detour and access Construction
plans to ensure the safe movement of
11ahicles and pedestrians during the
construction period.
Utility/service Systems
U-1: OCWD will in.Estigate all alailable OCWD During
altematilbs, and then select the best Construction
method of solid waste disposal and
reduction of solid waste stream as reDlired
in the California Integrated Waste
Management Act prior to the start of
construction.
° OCWD Water Production Enhancement Project
Final ISMND Mitigation Monitoring Program 4-6
1
Orange County Water District FILED
18700 Ward Street OC1 2 0 2016
Fountaintwin Valley, CA 92708
(714) 378-3200 ORANGE COUNTY CLERK-RECORDER DEPARTMEm
_ _
NOTICE OF DETERMINATION BY DEPUTY
TO: Office of Planning and Research FROM: Orange County Water District
1400 Tenth Street, Room 121 18700 Ward Street
Sacramento,CA 95814 Fountain Valley, CA 92708
Orange County Clerk Recorder
P.O. Box 238
Santa Ana,CA 92702-0238
Subject: Filing of Notice of Determination in compliance with Section 21108 or 21152 of the Public
Resources Code
Project Title:Water Production Enhancement Project
Applicant:Orange County Water District, 18700 Ward Street, Fountain Valley,CA 92708
State Clearinghouse Number: SCH 2O16081067
Lead Agency Contact Person: Dan Boh i "" � �
Area Code/Telephone Number: (714)37d�3256
Project Location 22212 Brookhurst Street
City of Huntington Beach Orange County
Project Description: Construction and operation of a 6 million gallon flow equalization tank, pump station
and associated plpmg.
This is to advise that the OrenrlP County Water District(Lead Agency) Irns approved tlh_ nl ova described
project on October u.Lo1b r ul ns made the following determination e.g i d,r-J the nb.ve. 1 r.nld,ed
( project:
X The project will nel nave a sgn rficant effect on the environment.
❑ An Fevlronmcnlnl Impart I&po,I was prepared torthis project pu,v,mnl to the p,ovislons of I LI 0A
X A MltIlj to I Nogalry Dods,: IlotI w 1 1 =p.u,ed to 1 II I Is [),oleo pu,suenf to the provisions of CEQA.
X Mitigation ,ucasucs wem m.,de a ,amdiroe of the opp,oval lo. Ihis pm]"L
❑ A Statonu:nt of Uve m. ,o, ConRdc,t,fioit was adopted for this project
❑ Finding,were nc,de pwsuant to the provisions of CEQA.
This r.to aedily Ihot the I e it Mitigated Negative L ecla,etion with comments and responses and record of
project approval is available to t blic at the Orange County Water District 18700 Ward Street,
Fountain Valley CA 92708.
V�
Signature Date Title
County Clerk: Please post for 30 days in accordance with Section 21152(c)of the California EP Ym r, T E D
Quality Act. Recorded In Official Records, orange couunty
Hiii�iiiiiiiliiiiiiiiiiiiiiuii Clerk-Recorder
iaiiiiiiii1iiiiiiiiii'IVIII III IIIIIIIII2210,25 OCT 20 2015
A $ R 0 0 0 8 7 8 1 6 1 9 $ ;+ LOCH NGUYEN.CLERK RECORDER
201685001134 8:12 am 10/20/16
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CAI IFORNIA DEPARTMENT OFFISH AND WILDLIFE
2015 ENVIRONMENTAL FILING FEE CASH RECEIPT
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SEE INSTRUCTIONS ON REVERSE. TYPE OR PRINTOLCARI Y `,CI J011iCII 11G
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ORAN41 I OI JN FY WA I I It 111`,I RICT 10 I�PIJ 16
- ,LN I, ' 411 AVENGV OFF WNG I LIMI GI NIIN'Ill
Oran' ]II:HSOU 1114
t21lII CI II11 F -
WATF R PR(IDUf.TION F NI IANCFMFNT PROJFCT
P1111 t l AIrI u.Aru NAMI I-In rtJl NUMBER
DANDOTI ORAW I CtHINIY WAIL P DISTRICT ( 114 ) 378-3258
PIaxII r I N•I•I I .ANI A(jnla CITY ISTATE nPI..,III
18700 WARD 4,Hkl I I FOUNTAIN VALLEY CA ),708
PR0 iAPPUCANI It PuvA arym,pnaL'nov
Laval Public Ayer y _ ❑',�ii -ti,istact O Other Special District 13Stia Arn i,, �E P6vate Entity
CHECK APPLICABLE FEES:
❑EnNronmectal Ilnpael Revue li n!1 $3,070.00 $ 0.00
0 Mioy;n L'I It— nw.['l, a il"ll tmi))INi, $2.210.25 $ 2,210,26
❑A,t, iennl „ W:ill vI j r i r I er Adler R2SOIIICES Control BOaYD only) $850.00 $ ODD
❑ t t I .,nbin:I I. t I L:.I,me I (CRP) $1,04375 $ 0.00
❑o, ey Aen,unzlnaiv, l a $50.00 $ 0.00
❑ 1I ,.nqm..,,Lu.nnl
❑CI,I 1N Nn I1¢,:I na all ulion, 11 10
❑Ot er $
PAYMENT METHOD:
❑cast, ❑flea Dll— ❑DtHer TOTAL RECEIVED $ 2,210.26
SIGNATURE PRINTED NAME AND TITLE
X U Lr¢ C�e,yl DULCE CUEVAS,DEPUTY CLERK
ORIGINAL-PROJECT AWLICAW COPY.CDFWIA59 COPY.LEAD AGENCY COPY.COUNTY CLERK DIG 751.11111,
Orange County Water District
Water Production Enhancement
Project
Draft Initial Study/Mitigated Negative Declaration &
CEQA-Plus Federal Consultation Review
Prepared By
Orange County Water District
18700 Ward Street
Fountain Valley, CA 92708
Contact: Daniel Bott U
N .SINCE 1933
October 2016
Table of Contents
Section Page
SECTION 1.0 INTRODUCTION................................................................................................1-1
1.1 Purpose of Endronmental Redew.............................................................................111
1.2 Statutory Authority and Relluirements.......................................................................111
1.3 Technical Information and Studies ............................................................................1 12
SECTION 2.0 PROJECT DESCRIPTION.................................................................................2-1
2.1 Background................................................................................................................211
2.2 Study Area.................................................................................................................211
2.3 Proposed Project Actidties........................................................................................211
2.4 Proposed Project.......................................................................................................212
2.5 Construction Phasing Plan ........................................................................................215
2.6 Construction Ellipment ............................................................................................2[8
2.6 Permits and Appromis...............................................................................................217
SECTION 3.0 ENVIRONMENTAL CHECKLIST EVALUATIONS............................................3-1
SECTION 4.0 ENVIRONMENTAL ANALYSIS.........................................................................4-1
4.1 Aesthetics..................................................................................................................411
4.2 Agricultural Resources/Forest Resources...............................................................4[15
4.3 Air Quality................................................................................................................4E16
4.4 Biological Resources...............................................................................................4[29
4.5 Cultural Resources..................................................................................................4137
4.6 Geology/Soils...........................................................................................................4156
4.7 Greenhouse Gas Emissions....................................................................................4160
4.8 HaCards/Hallardous Materials .................................................................................418
4.9 Hydrology/Water Quality..........................................................................................4171
4.10 Land Use/Planning ..................................................................................................4EB2
4.11 Mineral Resources...................................................................................................4[B4
4.12 Noise........................................................................................................................41844
4.13 Population/Housing..................................................................................................4197
4.14 Public Serl7ces........................................................................................................4197
4.15 Recreation ...............................................................................................................4198
Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA.Plus Federal Consultation Review i
Table of Contents
4.16 Transportation/Traffic...............................................................................................4199
4.17 Utilities/SerdceSystems .......................................................................................41103
SECTION 5.0 CEQA-Plus Federal Consultation Review......................................................5-1
5.1 Purpose .....................................................................................................................511
5.2 Federal Endangered Species Act ESAQ Section 7 ..................................................511
5.3 Magnuson Sterns Fishery Censer ation and Management Act, Essential Fish
Habitat: ......................................................................................................................515
5.4 National Historic Preserlation Act, Section 106........................................................515
5.5 Federal Clean Air.....................................................................................................5111
5.6 Coastal Zone Management Act...............................................................................5113
5.7 Coastal Barriers Resources Act...............................................................................5114
5.8 Farmland Protection Policy Act................................................................................5114
5.9 Flood Plain Management.........................................................................................5E14
5.10 Migratory Bird Treaty Act.........................................................................................5115
5.11 Protection of Wetlands.............................................................................................5115
5.12 Wild and Scenic Ri-ers Act......................................................................................5116
5.13 Safe Drinking Water Act, Sole Source AD fifer Protection .......................................5116
5.14 Endronmental 11istice..............................................................................................5116
SECTION 6.0 REFERENCES...................................................................................................6-1
Figure
Figure 1: Regional Location Map...............................................................................................213
Figure 2: OCSD Plant 2 Wastewater Treatment Site.................................................................214
Figure 3: Study Area OExisting Views........................................................................................412
Figure 4: Study Area Views OSanta Ana Rilar Trail..................................................................413
Figure 5: Study Area Views OSanta Ana Ri Cer Trail..................................................................414
Figure 6: Study Area Views OPCH O Talbert Marsh..................................................................416
Figure 7: Study Area Views OTalbert Park.................................................................................417
Figure 8: Project Viewsheds OSanta Ana Ri Cer Trail.................................................................419
Figure 9:Project Viewsheds Talbert Park.................................................................................401
Figure 10: Project Viewsheds EPacific Coast Highway...........................................................4C12
Figure 11: Project Viewsheds OBrookhurst St. .......................................................................4113
Figure 12: Area of Potential Effects.........................................................................................4147
Figure 13: FEMA Flood Ha1Brd Areas OOCSD Plant 2 Wastewater Treatment Site...............4EB1
Orange County Water District Water Production Enhancement Project
l✓ Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review it
Table of Contents
Table
Table 1: Flow EQ Tank, Pump Station, 0 Pipeline/Meter Vault Construction............................216
Table 2: Flow EQ Tank, Pump Station, and Pipeline/Meter Vault Worker 0 Daily Trip Summary.........216
Table 3: Study Area Air Quality Data Summary EE20121201411.................................................4117
Table 4: South Coast Air Basin Attainment Status ..................................................................4E19
Table 5: SCAQMD Regional Air Quality Significance Thresholds...........................................4123
Table 6: SCAQMD LocaliDad Significance Thresholds............................................................4E24
Table 7: Proposed Regional Construction Emissions..............................................................4125
Table 8: Operation Emissions..................................................................................................4126
Table 9: LocaliDad Daily Construction Emissions....................................................................4E28
Table 10: Special Status Plant Species...................................................................................4131
Table 11: Special Status Wildlife Species................................................................................4C33
Table 12: Estimated Total Construction Related GHG Emissions...........................................4166
Table 13: Estimated Construction and Operational Related GHG Emissions. ........................4166
Table 14: Beneficial Uses........................................................................................................4174
Table 15: Beneficial Uses Santa Ana Rimer/Orange County Groundwater Basin....................4175
Table 16: Water Quality Objecti as mg/1-11.............................................................................4176
Table 17: Noise Le-als and Human Response........................................................................4186
Table 18: City of Huntington Beach Exterior Noise Standards ................................................4187
Table 19: City of Huntington Beach Interior Noise Standards .................................................41B7
Table 20: Existing Ambient Noise LeCels.................................................................................4189
Table 21: Construction EDtipment Noise IeCels......................................................................4191
Table 22: Estimated Construction Noise Le Gels [dBa0............................................................4191
Table 23: Caltrans Vibration Damage Potential Threshold Criteria.........................................4194
Table 24: Caltrans Vibration Annoyance Potential Criteria Maximum PPV.............................4194
Table 25: Peak Particle Velocity IPPVGof Vibration Impacts...................................................4195
Table 26: Decibel Notation SVDBOLelels of Vibration Impacts................................................4195
Table 27: Groundbome Vibration leCels at Offsite Sensiti Ce uses Compared to Caltrans and
FTA Vibration Damage potential threshold..............................................................4196
Table 28: Project Construction Traffic Trips...........................................................................4d00
Table 29: Capacity Orange County Landfills .........................................................................4E104
Table 30: Federal Listed Plant Species.....................................................................................SIB
Table 31: Federal Listed Wildlife Species..................................................................................513
Table 32: De Mimimis Le Cels...................................................................................................5112
Table 33: SIP Conformity Elaluation.......................................................................................503
6 Orange County Water District Water Production Enhancement Project
�✓° Draft Initial Study/Mitigated Negative Declaration$CEQA-Plus Federal Consultation Review III
Table of Contents
Appendices
Appendix A: OCWD Water Production Enhancement Project []Air Quality and Greenhouse
Gas Emissions Technical Report fly 2016
Appendix B: OCWD Water Production Enhancement Project []Biological Assessment
August 2016
Appendix C: Groundwater Replenishment System Final Expansion Project and Water
Production Enhancement Project 0 Phase I Cultural Resources Study August
2016
Appendix D: OCWD Water Production Enhancement Project 0 Noise and Vibration
Technical Report August 2016
e Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration$CEQA-Plus Federal Consultation Review iv
Section 1
SECTION 1.0 INTRODUCTION
1.1 Purpose of Environmental Review
The California Envronmental Quality Act [CEQADreojires that all state and local
goEarnment agencies consider the endronmental conseouences of projects o[Br which
they ham discretionary authority before taking action on those projects. This Initial
Study has been prepared to disclose and eDaluate short®erm construction related
impacts and longterm operational impacts associated with the implementation of the
Orange County Water District Water Production Enhancement Project. Pursuant to
Section 15367 of the State CEQA guidelines, the Orange County Water District
[OCWDdis the Lead Agency and has the principal responsibility for appro ing and
implementing the proposed Water Production Enhancement Project. As the Lead
Agency, OCWD is reDuired to ensure that the project complies with CEQA and that the
appropriate leD3l of CEQA documentation is prepared. Through preparation of an Initial
Study as the Lead Agency, OCWD would determine whether to prepare an
Envronmental Impact Report 1EIRQ Negati[13 Declaration or Mitigated Negati[D
Declaration IIMNDDfor the project. If the Lead Agency finds that there is no eddence
that the project, either has proposed or as modified to include mitigation measures
identified in the Initial Study prior to its public circulation, would not Cause a significant
effect on the endronment, the Lead Agency shall prepare a NegatiEb Declaration or
Mitigated Negati[B Declaration for the project. Section 15382 of CEQA Guidelines
defines a [significant effect on the endronmentDas a substantial, or potentially
substantial adDarse change in any of the physical conditions within the area affected by
the project including land, air water, mineral, flora, fauna, ambient noise, aesthetic
endronment and objects of cultural significance. Based on the conclusions of this Initial
Study, OCWD has determined that the appropriate IeCel of endronmental
documentation for the Water Production Enhancement Project is a Mitigated NegatiCe
Declaration.
1.2 Statutory Authority and Requirements
This Initial Study/Mitigated Negati113 Declaration has been prepared in accordance with
the CEQA, Public Resources Code Section 21000 at Se¢, State CEQA Guidelines, and
the OCWD CEQA Envronmental Procedures. The endronmental analysis for the
proposed project is based on OCWD Envronmental Checklist Form. The Checklist
Form is consistent with Initial Study renlirements prodded in Section 15063 of the State
CEQA Guidelines.
(D� Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 1-1
Section 1
1.3 Technical Information and Studies
The following Technical Studies ha a been and incorporated into the Orange County
Water District Water Production Enhancement Project Initial Study eCaluation.
• Appendix A: OCWD Water Production Enhancement Project []Air Quality and
Greenhouse Gas Emissions Technical Report Culy 2016
• Appendix B: OCWD Water Production Enhancement Project DBiological Assessment
August 2016
• Appendix C: Groundwater Replenishment System Final Expansion Project and Water
Production Enhancement Project 0 Phase I Cultural Resources Study August 2016
• Appendix D: OCWD Water Production Enhancement Project 0 Noise and Vibration
Technical Report August 2016
(D� Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 1-2
Section 2
SECTION 2.0 PROJECT DESCRIPTION
2.1 Background
The Groundwater Replenishment System IGWRSDis an adilanced water treatment
facility constructed by the Orange County Water District 1OCWD13and the Orange
County Sanitation District [OCSDothat takes secondary treated wastewater and through
adllancement treatment treats the water to exceed drinking water standards. The
GWRS supplements local water supplies by prodding reliable, high Duality source of
treated water to recharge the Orange County Groundwater Basin and to protect the
Orange County Groundwater Basin from seawater intrusion. The final build1but of the
GWRS would produce approximately 128,000 acre feet of new water supplies per year.
To increase the amount wastewater flows generated from OCSD to the GWRS, OCWD
has proposed a Water Production Enhancement Project that inColCes the construction
and operation of an abole ground flow entalilation storage tank and associated pump
station at OCSD Plant No. 2 wastewater treatment facility site. With the operation of the
flow elluali[lation tank, the GWRS would produce approximately 6,000 acre feet of new
water supplies per year to replenish the Orange County Groundwater Basin. With the
Water Production Enhancement Project the GWRS total full build[but treatment capacity
would be increased to 134,000 acre feet per year.
2.2 Study Area
The OCSD Plant No. 2 Site is located at 22212 Brookhurst Street within the City of
Huntington Beach. OCSD Plant No. 2 site is composed of 110 acres, and is de[Bloped
with wastewater treatment structures, offices, and paled parking areas and roadways.
As shown in Figure 1, the site is bounded by Hamilton ACenue to the north, Brookhurst
Street to the west, Talbert Marsh and Talbert Marsh Bike Trail to the south and the
Santa Ana Ricer and the Santa Ana Ricer Trail to the east. Primary regional access to
Plant No. 2 would from Interstate 405 from the Brookhurst Street exit. Primary local
access would be from Brookhurst Street and Pacific Coast Highway.
2.3 Proposed Project Activities
The OCWD Water Production Enhancement Project consists of a secondary effluent
flow elualiriation tank proposed at OCSD® Plant No. 2 in order to recei[e maximum
water production at the OCWD GWRS water treatment facility. OCSD® Plant No. 2 is a
wastewater treatment facility which has larying influent land effluentoflows of
secondary effluent. During the day, wastewater flows into OCSD® Plant No. 2 can peak
abo[la 140 million gallons per day 1MGD11 These peak flows cannot be pumped to the
GWRS facility due to the limits of the conilayance facilities, i.e. effluent pump station
and pipeline; that dell[er the secondary effluent to GWRS. Therefore, a secondary
effluent flow eouali[lation tank has been proposed at OCSD[s Plant No. 2 Site to capture
t� Orange County Water District Water Production Enhancement Project
V Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 2-1
Section 3
these peak flows during the day and store them in the 61tlnnillion gallon tank until
nighttime. During low flows at night, the flow eilualiDAon tank would drain into the
effluent pump station to supplement the low secondary effluent inflows and allow the
GWRS to treat these peak flows which would haElS otherwise been discharged to the
ocean. This secondary effluent flow eDualiDation tank would be expected to deliEBr an
additional 6,000 acrettleet of secondary effluent for treatment at the GWRS facility.
2.4 Proposed Project
The Water Production Enhancement Project inCOlCes three construction actidties: 1❑
construction of flow eDJaliCation tank, 2Dconstruction of a pump station, and 311
construction of conCeyance piping and flow meter moult. The improCements proposed in
the Water Production Enhancement Project are shown in Figure 2.
A 6Emillion gallon [MGDflow eoualil ation tank would be constructed at the north end of
OCSD Plant No. 2 Site. The 61MG tank would be a circular welded steel tank
approximately 200111eeet in diameter and 301teet tall from existing grade. The flow
e0ualiDstion tank would haCe a 4Lpump CB duty ❑ 1 standby0pump deepq approximately
5000inear feet of 36tl1nch diameter connection piping with a meter Exult d51t x 202 x
10mt deepDconnected to the operations of the tank. The pump station would be housed
in a 301tt x 401 t x 203t block wall building.
The site preparation work for the flow emaliDation tank, pump station, and pipeline/Exult
would inEDIEB excaoating and hauling approximately 1000 cubic yards ECYDof soil. In
addition to dirt remoElaI, an existing concrete parking lot would need to be demolished
for the tank pad. For this dirt excaDation work, four dump trucks would be doing fiEB
round trips each of-er a period of 4 days to haul the dirt off site. For the demo work, four
dump trucks would be doing three round trips each oDar a period of 14 days to haul the
concrete/asphalt off site.
The flow eELaliCation tank would be constructed on concrete piles. Approximately 30❑
piles would be reDiired for supporting the emaliDStion tank. To construct the pilings, 12❑
inch diameter holes would be drilled into the ground with an auger drill rig.
Approximately 40 CY of dirt from pile drilling actidty would be remoEEd. Once the pile
drilling is completed, the rebar support cages for the piles would be installed into the
drilled holes with a crane. Approximately 40 CY of concrete would be filled into the
holes with the rebar and cured. The piles would be supporting a Moot thick concrete
pad matching the diameter of the tank. This equates to 2,330 CY of concrete for the
tank pad. The pump station and meter moult would also reD,aire approximately 100 CY of
concrete to construct these structural facilities.
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 2-2
p
5 NF WER AUE
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ARF1E DAVE
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� WRS Faclhty .� � ty
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OCSD Easement
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W
2
T
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�i
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\� W
T i
OCSD
3 Plant No. 2 f '
N
o 1,000 2,000 Water Production Enhancement Project
W i E 6MMML====J Feet Regional ocation Ma
Figure 1
S
r �
Contractor
Laydown Area
Construction:
Flow EQ Tank
. ^ L Construction:
..- ♦ _ Flow EQ r
Control / Meter
BANNING AVE .
fir # '• a
•� f Construction:
- Flow EQ /irr
r „t Pump Station III `
-;, .
N
0 200 400 Water Production Enhancement Project
W E 6nommimsonL===J Feet OCSD Plant 2 Wastewater Treatment Site
Figure 2
S
Section 2
Once the piles and concrete pad ha[la been constructed, the steel tank would be
assembled. A crane and welding laborers would be rewired to weld the steel
components of the tank together. Once the tank is welded, the surface would be
prepped for a base coat and finally painted.
While the tank is being assembled, the contractor would be elluipping the pump station
and meter fault with the use of laborers, fork lifts and cranes. The construction
ellipment for the tank, meter Dault, flow di[f:rsion box and pump station would include;
an excall3tor, crane, pile driller, bull doer, backhoe, compactor, dump trucks, concrete
trucks, water truck, man lifts and fork lifts.
2.5 Construction Phasing Plan
The OCWD Water Production Enhancement Project would be implemented in filb
construction phases beginning in August 2020 and concluding in December of 2022.
The seDuence of construction actidties is shown below.
Estimated Construction Dates: August 2020 to December 2021
Construction Phases: 1A, 1 B and 1 C will be constructed separately. 1 D and 1 E would
be constructed concurrently.
Phase 1A: Excaoation, Hauling, Grading for Flow EQ Tank, Pump Station,
Pipeline/Meter Vault
Phase 1 B: Construction of Piles for Flow EQ Tank
Phase 1C: Concrete Pours for Flow EQ Tank Pad
Phase 1 D: Flow EQ Tank Assembly D Coating
Phase 1 E: Installation of pipeline and assembly of eDuipment for Flow EQ pump station
and meter moult
2.6 Construction Equipment
The construction e0uipment and hours of operation are shown in Table 1 and the
construction traffic trips are shown in Table 2.
t� Orange County Water District Water Production Enhancement Project
V Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 2-5
Section 2
Table 1: Flow EQ Tank, Pump Station, & Pipeline/Meter Vault Construction
Equipment Mix
Equipment Equipment Time Total Total HP
Activity Description Quantity (H./Day) s Hours Pining
OCSDFlow EQ Tank,PS,Meter Vault&Pipeline(1A) Bull Dozer 2 6 30 360 250
C nn actor 1 6 10 60 200
Excavator 2 6 20 240 200
Dump Trucks 4 6 4 96 350
Demo Dump Trucks 4 6 14 336 350
Water Trucks 1 8 45 3W 350
0C5D Flow EQ Tank Piles(1B) Drill Ri 1 6 20 120 S00
Backhoe 11 6 20 120 150
Concrete Trucks 1 5 3 IS MO
Dump Trucks 2 5 3 30 350
Water Truck 2 4 25 2W 350
Dan FIow EQ Tank Pad(1Q Crane 1 5 5 25 300
Forklift 2 6 5 W 120
Concrete Trucks 4 5 24 480 MO
OGSD Flow EQTank Assembly&Geatin 11)) Gran 1 6 10 W 300
Fork Df[ 1 4 6 30 220 120
Man lift 51 6 15 450 25
OCSD Flow EQ PS&Meter Vault Equipping(IE) Crane 1 61 10 60 300
Forklift 41 61 30 220 120
Man Lift 1 51 61 IS 450 25
Table 2: Flow EQ Tank, Pump Station, and Pipeline/Meter Vault Worker & Daily
Trip Summary
Daily Total
Haul Haul
OCSD Flow EQTank,Pump Station,and Pipeline/Meter Vault Worker Vendor Trips Trips
IA:Excavation,Hauling,Grading for Flow EQTank,Pump Station,and Pipeline 10 1 32 248
1B:Piles Construction for Flow EQ Tank 10 2 4 12
1C:Flow EQTank Pad Construction 10 2 12 288
11):Flow EQTank Assembly and Coating 5 2
1E:Assembly of Flow EQ Pumps and Meter Vault 5 4
t*�1 Orange County Water District Water Production Enhancement Project
J Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 2-6
Section 2
2.6 Permits and Approvals
The Initial Study/Mitigated Negatilb Declaration prepared for the OCWD Water
Production Enhancement Project would be used as the supporting CEQA enLironmental
documentation for the following approCels and permits.
Agency Approvals/Discretionary Actions
Orange County Water District . Project Approval
• Appro al for Agreements
Construction Contracts
• Agreement with the Orange County
Sanitation District for the
deLelopment, operation and
maintenance of Groundwater
Replenishment System facilities on
Orange County Sanitation District
Plant No.2
Orange County Sanitation District . Project Approval
• Agreement with the Orange County
Water District for the de3slopment,
operation and maintenance of
Groundwater Replenishment
System facilities on Orange County
Sanitation District Plant No.2
State Regional Water Quality Control Board, Approval of amendment to Regional Water
Santa Ana Region Control Board Producer/User Water
Recycling Permit Orange County Water
District Groundwater Replenishment System
IR812008700580
State Water Resources Control Board Stale Relbl7ing Fund Loan
City Huntington Beach Coastal DeiLlopment Permit
t;+, Orange County Water District Water Production Enhancement Project
V Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 2-7
Section 3
SECTION 3.0 ENVIRONMENTAL CHECKLIST EVALUATIONS
The following is the OCWD Endronmental Checklist Form that was prepared for the Water
Production Enhancement Project. The Envfonmental Checklist Form is consistent with
Envronmental Checklist form prolded in Appendix G of the CEQA Guidelines.
Project Title: Orange County Water District Water Enhancement Project
Lead Agency Name and Address: Orange County Water District
18700 Ward Street
Fountain Valley, CA 92708
Project Contact: Daniel Bott
Location: 22212 Brookhurst Street Huntington Beach, California
Environmental Determination On the basis of this initial evaluation, I find that:
a0 ❑ The Water Production Enhancement Project could not haES a significant effect on the an 0ronment
and a NEGATIVE DECLARATION will be prepared.
b0 X Although the Water Production Enhancement Project could hale a significant effect on the
enUronment,there will not be a significant effect in this case because reUsions to the project haEL
been made by or agreed to by the applicant. A MITIGATED NEGATIVE DECLARATION will be
prepared.
c0 ❑ The Water Production Enhancement Project may hale a significant effect on the en0ronment and
an ENVIRONMENTAL IMPACT REPORT is recuired.
d0 ❑ Although the Water Production Enhancement Project could hale a significant effect on the
enUronment, because all potentially significant effects ®blare been analyCad adeUtately in an
earlier EIR 1EIR No. CLpursuant to applicable standards and lb-haLB been amided or mitigated
pursuant to that earlier EIR, including re0sions or mitigation measures that are imposed upon the
project,nothing further is reDlired.
e0 ❑ Pursuant to Section 15164 of the CEQA Guidelines, an EIR EIR No. 01has been prepared earlier
and only minor technical changes or additions are necessary to make the predous EIR adeaate
and these changes do not raise important new issues about the significant effects on the
enUronment. An ADDENDUM to the EIR shall be prepared.
f ❑ Pursuant to Section 15162 of the CEQA Guidelines,an EIR [EIR No. DEhas been prepared earlier;
howelar,subseUaent proposed changes in the project and/or new information of substantial
importance will cause one or more significant effects no preGously discussed. A SUBSEQUENT
EIR shall be prepared.
Signature Date
Printed Name: Daniel Bott
tom, Orange County Water District Water Production Enhancement Project
V Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 3-1
Section 3
Less Than
Significant
Potentially with Less Than
Significant Mitigation Significant No
V. Issues o Supporting Information Sources Impact Incorporated Impact Impact
I. Aesthetics—Would the project:
all Hale a substantial adCerse effect on a scenic ❑ ❑ ❑ N
UstaC
bo Damage scenic resources, including but not ❑ ❑ ❑ N
limited to,trees, rock outpourings and historic
buildings within a state highwayo
co Substantially degrade the existing ❑sual character ❑ N ❑ ❑
or Duality of the site and its surroundings❑
do Create a new source of substantial light or glare ❑ N ❑ ❑
which would ad Cersely affect day or nighttime
dews in the area❑
It. AGRICULTURAL AND FOREST RESOURCES: In determining whether impacts to agricultural resources are
significant endronmental effects, lead agencies may refer to the California Agricultural Land EEaluation and Site
Assessment Model prepared by the California Department of ConserDution as an optional model to use in
assessing impacts on agricultural farmland. In determining whether impacts to forest resources, including
timerberland, are significant enf7ronmental effects, lead agencies may refer to information compiled by the
California Department of Forestry and Fire Protection regarding the states in Centory of forest land, including
the Forest and Range Assessment Project and the Forest Legacy Assessment project; and forest carbon
measurement methodology prooded in Forest Protocols adopted by the California Air Resources Board.Would
the project:
all Con Eart Prime Farmland, UnlQle Farmland or ❑ ❑ ❑ N
Farmland of Statewide Importance ElFarmlandoto
nonCagricultural used IThe Farmland Mapping
and Monitoring Program in the California
Resources Agency, Department of ConserLation,
maintains detailed maps of these and other
categories of farmland.❑
bD Conflict with existing Doling for agricultural use or ❑ ❑ ❑ N
a Williamson Contracto
co Conflict with existing Coning for,or cause re[oning ❑ ❑ ❑ N
of,forest land ®s defined in Public Resources
Code section 12220Cgq timberland [as defined by
Public Resources Code section 4526q or
timberland Coned Timberland Production [as
defined by GoEarnment Code section 51104[gEll
do Result in the loss of forest land or conEbrsion of ❑ ❑ ❑ N
forest land to non[forest use❑
ell In oll a other changes in the existing endronment ❑ ❑ ❑ N
which, due to their location or nature, could
indilldually or cumulatiEbly result in loss of
Farmland,to non®gricultuml use or conibmion of
r Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 3-2
Section 3
Less Than
Significant
Potentially with Less Than
Significant Mitigation Significant No
V. Issues ❑Supporting Information Sources Impact Incorporated Impact Impact
forest land to non[brest use❑
III. Air Quality- Where aD3ilable, the significance criteria established by the applicable air Duality management or
pollution control district may be relied upon to make the following determinations. Would the project:
a❑ Conflict with or obstruct implementation of ❑ ❑ ❑
applicable Air Quality Attainment Plan or
Congestion Management Plan
b❑ Violate any stationary source air Duality standard ❑ ® ❑ ❑
or contribute to an existing or proposed air Duality
Uolation❑
co Result in a cumulatively considerable net increase ❑ ❑ ® ❑
of any criteria pollutant for which the project
region is non®ttainment under an applicable
federal or state ambient air uality standard
[ncluding releasing emissions which exceed
DuantitatiCe thresholds for o.-one precursors®
d❑ Expose sensiti[B receptors to substantial pollutant ❑ ❑ ® ❑
concentrations❑
eo Create objectionable odors affecting a substantial ❑ ❑ ® ❑
number of people❑
IV. Biological Resources ❑Would the project:
a❑ Have a substantial adEarse impact, either directly ❑ ❑ ❑
or through habitat modifications, on any species
identified as a candidate, sensitive or special
status species in local or regional plans, policies
or regulations or by the California Department of
Fish and Game or U.S. Fish and Wildlife
SerDCeSv
b❑ Have a substantial adEarse impact on any riparian ❑ ❑ ❑
habitat or natural community identified in local or
regional plans, policies, and regulations or by the
California Department of fish and Game or U.S.
Fish and Wildlife SerdCe❑
co Adversely impact federally protected wetlands as ❑ ❑ ❑
defined by Section 404 of the Clean water Act
[Including, but not limited to, marsh, Larnal pool,
coastal,etc.Dhrough direct remoEbl,filling
hydrological interruption, or other meansv
d❑ Interfere substantially with the mo[Bment of any ❑ ❑ ❑
native resident or migratory fish or wildlife species
or with established native resident or migratory
wildlife corridors, or impede the use of native
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 33
Section 3
Less Than
Significant
Potentially with Less Than
Significant Mitigation Significant No
V. Issues O Supporting Information Sources Impact Incorporated Impact Impact
wildlife nursery sites0
e0 Conflict with any local policies or ordinances ❑ ❑ ❑
protecting biological resources, such as tree
preservation policy or ordinance0
fO Conflict with the pmJsions of an adopted Habitat ❑ ❑ ❑
Conserlhtion Plan, Natural Community
Conservation Plan, or other approved local
regional or state habitat conserlation plane
V. Cultural Resources 0 Would the project:
aO Cause a substantial adverse change in the ❑ ® ❑ ❑
significance of a historical resource as defined in
Section 15064.50
bo Cause a substantial ad[Prse change in the ❑ ® ❑ ❑
significance of a uniLue archaeological resource
pursuant to define Section 15064.50
cO Directly or indirectly disturb or destroy a uniEue ❑ ❑ ❑
paleontogical resource or site0
d0 Disturb any human remains, including those ❑ ® ❑ ❑
interred outside of formal cemeteries❑
VI. Geology and Soils 0 Would the project:
a0 Expose people or structures to potential ❑ ❑ ❑ ❑
substantial ad[arse effects, including the risk of
loss, injury, or death in�oldng:
1. Rupture of a known earth Disks fault, as ❑ ❑ ® ❑
delineated on the most recent on the most
recent AlE)uistEPriolo Earth Disks Fault
Zoning map issued by the State Geologist
for the area or based on other substantial
e0dence of a known fault❑
2. Strong seismic ground shaking❑ ❑ ® ❑ ❑
3. SeismicTelated ground failure, including ❑ ® ❑ ❑
IidefactionL
4. Landslides I ❑ ❑ ❑
1:0 Would the project result in substantial soil ❑ ❑ ® ❑
erosion or the loss of topsoil❑
cO Be located on a geologic unit or soil that is ❑ ® ❑ ❑
unstable, or that would become unstable as
result of the project, and potentially result in ono
orlbff site landslide, lateral spreading,
r Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 3.4
Section 3
Less Than
Significant
Potentially with Less Than
Significant Mitigation Significant No
V. Issues ❑Supporting Information Sources Impact Incorporated Impact Impact
subsidence, lidefaction or collapse❑
d❑ Be located on expansi Ce soil, as defined in table ❑ ® ❑ ❑
1811IS of the uniform Building Code creating
substantial risks to life or property0
so Ham soils incapable of adeDiately supporting ❑ ❑ ❑
the use of septic tanks or alternali-L waste water
disposal systems where sewers are not available
for the disposal of waste water
VIL GREENHOUSE GAS EMISSIONS ❑ Would the projectO
a❑ Generate greenhouse gas emissions,either ❑ ❑ ® ❑
directly or indirectly,that may halt a significant
impact on the enilronmento
b❑ Conflict with an applicable plan, policy or ❑ ❑ N ❑
regulation adopted for the purpose of reducing
the emissions of greenhouse gases❑
Vill. HAZARDOUS AND HAZARDOUS MATERIALS ❑Would the project:
a❑ Create a significant haLard to the public or the ❑ N ❑ ❑
endronment through the routine transport, use or
disposal of hal]3rdous materials❑
b❑ Create a significant havard to the public or the ❑ N ❑ ❑
endronment through reasonably foreseeable
upset and accident conditions in�[Jng the
release of haEardOUs materials into the
en17ronmentO
co Emit havardous emissions or handle havardous ❑ ® ❑ ❑
or acutely haEardous materials, substance or
waste within one1luarter mile of an existing or
proposed school❑
d❑ Be located on a site which is located on a list of ❑ ❑ ❑ X
havardous materials sites compiled pursuant to
Go[Ernment Code Section 659662.5 and,as a
result,would it create a significant he and to the
public or the endronmento
e❑ For a project located within an airport land use ❑ ❑ ❑ N
plan or where such a plan has not been adopted,
within two miles where of a public airport or
public use airport,would the project result in a
safety hard for people residing or working in
the project area❑
fo For a project within the ❑cinity of a private ❑ ❑ ❑ N
airstrip, would the project result in a safety
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 35
Section 3
Less Than
Significant
Potentially with Less Than
Significant Mitigation Significant No
V. Issues o Supporting Information Sources Impact Incorporated Impact Impact
halbrd for people residing or working in the
project area❑
go Impair implementation of or physically interfere ❑ ❑ ❑
with an adopted emergency response plan or
emergency eLacuation plan
ho Expose people or structures to a significant risk ❑ ❑ ❑
of loss, injury or death in[b❑ng wild land fires,
including where wild lands are adjacent to
urbaniCed areas or where residences are
intermixed with wild lands❑
VDL HYDROLOGY AND WATER QUALITY o Would the project:
a❑ Violate any water Duality standards or waste ❑ ® ❑ ❑
discharge reouirementso
bo Substantially deplete groundwater supplies or ❑ ❑ ❑
interfere substantially with groundwater recharge
such that there would be a net deficit in adifer
Colume or a lowering of the local groundwater
table leEbl re.g., the production rate of pre
existing nearby wells would drop to a Is el which
would not support existing land uses or planned
uses for which permits haJB been granted-
co Substantially alter the existing drainage pattern ❑ ® ❑ ❑
of the site or area, including through the
alteration of the course of stream or ricer, in a
manner which would result in substantial erosion
or siltation on or offaiteo
do Substantially alter the existing drainage pattern ❑ ® ❑ ❑
of the site or area, including through the
alteration of the course of a stream or ri Cer,or
substantially increase the rate or amount of
surface runoff in a manner which would result in
Flooding orl off site
eo Create or contribute runoff water which would ❑ ® ❑ ❑
exceed the capacity of existing or planned
stormwater drainage systems or pro0de
substantial additional sources of polluted runoffo
to Otherwise substantially degrade water Dualityo ❑ ® ❑ ❑
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEOA-Plus Federal Consultation Review 3-6
Section 3
Less Than
Significant
Potentially with Less Than
Significant Mitigation Significant No
V. Issues o Supporting Information Sources Impact Incorporated Impact Impact
go Place housing within a 1001year flood hard ❑ ❑ ❑ N
area as mapped on a federal Flood Halard
Boundary or Flood Insurance Rate Map or other
flood havard delineation map❑
ho Place within a 100gear Flood halard area ❑ ❑ ❑ N
structures which would impede or redirect flood
floWSE
io Expose people or structures to a significant risk ❑ ❑ ❑ N
of loss, injury, or death in 3Ndng flooding,
including flooding as a result of the failure of a
leEbe or dam❑
V Inundation by seiche,tsunami,or mudflowo ❑ ❑ ❑
X. LAND USE AND PLANNING o Would the project:
all Physically dude an established community❑ ❑ ❑ ❑ N
bo Conflict with any applicable land use plan, ❑ ❑ ❑ N
policy,or regulation of an agency with
jurisdiction oEbr the project Ohcluding, but not
limited to the general plan, specific plan, local
coastal program, or Coning ordinance adopted
for the purpose of avoiding or mitigating an
enl7ronmental effecto
co Conflict with any applicable habitat conservation ❑ ❑ ❑ N
plan or natural community conserCation plan❑
A. MINERAL RESOURCES—Would the project:
a❑ Result in the loss of availability of a known ❑ ❑ ❑ N
mineral resource that would be of Ealue to the
region and the residents of the state❑
bo Result in the loss of alailability of a locallyo ❑ ❑ ❑ N
important mineral resource recovery site
delineated on a local general plan, specific plan,
or other land use plan
XII. NOISE ❑Would the project result in:
so Exposure of persons to or generation of noise ❑ ® ❑ ❑
leELS in excess of standards established in the
local general plan or noise ordinance, or
applicable standards of other agencies❑
bo Exposure of persons to or generation of ❑ ❑ N ❑
excessive groundbome ❑bration or
groundborne noise lelblso
co A substantial permanent increase in ambient ❑ N ❑ ❑
noise levels in the project ❑cinity above IeEbIS
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 3-7
Section 3
Less Than
Significant
Potentially with Less Than
Significant Mitigation Significant No
V. Issues 0 Supporting Information Sources Impact Incorporated Impact Impact
existing without the project0
d0 A substantial temporary or periodic increase in ❑ ® ❑ ❑
ambient noise lelals in the project Ocinity abo[B
Weis existing without project0
e0 For a project located within an airport land use ❑ ❑ ❑
plan or where such a plan has not been
adopted,within two miles of a public airport or
public use airport,would the project expose
people residing or working in the project area to
excessiDs noise le>31s-i
fC For a project within the Elcinity of a pri ate ❑ ❑ ❑
airstrip,would the project expose people
residing or working in the project area to
excessive noise Ie�alS7
XIII. POPULATION AND HOUSING 0 Would the project:
a0 Induce substantial population growth in an area, ❑ ❑ ❑
either directly mor example, by proposing new
homes and business0or indirectly [for example,
through extension of roads or other
infrastructure®
b0 Displace substantial numbers of existing ❑ ❑ ❑
housing, necessitating the construction of
replacement housing elsewhere0
c0 Displace substantial numbers of people, ❑ ❑ ❑
necessitating the construction of replacement
housing elsewhere0
XIV. PUBLIC SERVICES
ao Would the project result in substantial adDarse ❑ ❑ ® ❑
physical impacts associated with the prodsion
of new or physically altered govemmental
facilities, need for new or physically altered
govemmental facilities,the construction of
which could cause significant en Oronmental
impacts, in order to maintain acceptable serilce
rations, response times or other performance
object!ves for any of the public serdce:
Fire protection0 ❑ ❑ ❑ ❑
Police protection0 ❑ ❑ ❑ ❑
Schools0 ❑ ❑ ❑ ❑
Parks0 ❑ ❑ ❑ ❑
Other public facilities0 ❑ ❑ ❑ ❑
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 3-8
Section 3
Less Than
Significant
Potentially with Less Than
Significant Mitigation Significant No
V. Issues 0 Supporting Information Sources Impact Incorporated Impact Impact
Xv. RECREATION
a❑ Would the project increase the use of existing ❑ ❑ ❑ N
neighborhood and regional parks or other
recreational facilities such that substantial
physical deterioration of the facility would occur
or be accelerated❑
b0 Does the project include recreational facilities or ❑ ❑ ❑
reDuire the construction or expansion of
recreational facilities which might have an
ad Lame physical effect on the endronment0
XVI. TRANSPORTATIONITRAFFIC Would the project:
a❑ Conflict with an applicable plan, ordinance or ❑ ❑ N ❑
policy establishing measures of effectiveness
for the performance of the circulation system,
taking into account all modes of transportation
including mass transit and non Tnotorived traDM
and releEent components of the circulation
system, including but not limited to
intersections, streets, highways and freeways,
pedestrian and bicycle paths, and mass transit0
b0 Conflict with an applicable congestion ❑ ❑ N ❑
management program, including but limited to
level of serl7ce standards and tfaEbl demand
measures, or other standards established by the
county congestion management agency for
designated roads or highways❑
co Result in a change in air traffic patterns, ❑ ❑ ❑ N
including either an increase in traffic levels or a
change in location that results in substantial
safety risks0
d❑ Substantially increase havards to a design ❑ ❑ N ❑
feature ®.g. sharp curJas or dangerous
intemections0or incompatible uses Ea.g.farm
eaipmentm
e0 Result in inadeDuate emergency access❑ ❑ ❑ N ❑
fv Conflict with adopted policies, plans, or ❑ ❑ N ❑
programs regarding public transit, bicycle, or
pedestrian facilities,or otherwise decrease the
performance or safety of such facilities❑
XVII. UTILITIES AND SERVICE SYSTEMS—Would the project:
a0 Exceed wastewater treatment rellirements of ❑ ❑ N ❑
r Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 3-9
Section 3
Less Than
Significant
Potentially with Less Than
Significant Mitigation Significant No
V. Issues 0 Supporting Information Sources Impact Incorporated Impact Impact
the applicable Regional Water Quality Control
Board❑
b0 ReDllre or result in the construction of new ❑ ❑ ❑
water or wastewater treatment facilities or
expansion of existing facilities, the construction
of which could cause significant endronmental
effects❑
CO ReOulre or result in the construction of new ❑ ❑ ❑
storm water drainage facilities or expansion of
existing facilities,the construction of which
could cause significant endronmental effects❑
d0 Are sufficient water supplies aCailable to serve ❑ ❑ ❑
the project from existing entitlements and
resources or are new or expanded entitlements
needed❑
eo Result in the determination by the wastewater ❑ ❑ ❑
treatment prodder which serves or may seroa
the project that it has ade:uate capacity to
serve the projects projected demand in addition
to the prodder®existing commitments❑
fC Is the project serDad by a landfill with sufficient ❑ ❑ ® ❑
permitted capacity to accommodate the
projects sold waste disposal needs❑
g0 Comply with federal, state and local statutes ❑ ❑ ® ❑
and regulations related to solid wasteE
XVIII. MANDATORY FINDINGS OF SIGNIFICANCE—
a0 Does the project haEa the potential to degrade ❑ ® ❑ ❑
the Duality of the endronment, substantially
reduce the habitat of a fish or wildlife species,
cause a fish or wildlife population to drop below
selfsustaining Weis,threaten to eliminate a
plant or animal community, reduce the number
or restrict the range of a rare or endangered
plant or animal or eliminate important examples
of the major periods of Califomia history or
prehistory❑
b0 Does the project haEb impacts that are ❑ ® ❑ ❑
indi ddually limited but cumulatiJBly
considerableo aCumulati Dslyconsiderableo
means that the incremental effects of a project
are considerable when dewed in connection
with the effects of past projects, effects of other
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 3-10
Section 3
Less Than
Significant
Potentially with Less Than
Significant Mitigation Significant No
V. Issues ❑Supporting Information Sources Impact Incorporated Impact Impact
cuff ant projects and the effects of probable
future pmjects0
co Does the project haDa endronmental effects ❑ ® ❑ ❑
which will cause substantial adEbrse effects on
human beings, either directly or indirectlyo
Note:Authority cited: Sections 21083, 21083.05, Public Resources Code. Reference: Section 65088.4
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 3-11
Section 4
SECTION 4.0 ENVIRONMENTAL ANALYSIS
The following analysis responds to the endronmental issues listed on the OCWD CEQA
Checklist Form. The analysis identifies the IeCel of anticipated impact and where
needed includes the incorporation of mitigation measures to reduce potentially
significant impacts to the endronment to a less than significant le[el.
4.1 Aesthetics
Existing Setting
The OCSD Plant No. 2 Site is located within the southeast industrial area of the City of
Huntington Beach. The OCSD Plant No. 2 Site is surrounded by the Santa Ana Ricer
Trail to the east, Talbert Park to the northeast, Brookhurst Street and single family
residential uses to the west, multiple family residential uses to the north and the Talbert
Marsh to the south. OCSD Plant No. 2 Site is currently deCeloped with numerous
structures that Lary in height, mass and function. The tallest onsite structure would be
the surge tower at a height of 86 feet, located at the southwestern end of the site. Other
notably si[ed structures include the existing sludge storage silos at approximately 50
feet in height and trickling filters at a height of 40 feet.
The OCSD Plant No. 2 Site is situated within urbaniCed area and is impacted from a
Dariety lighting sources from the surrounding the area. The lighting from these
surrounding sources generally diminishes the Duality of the nighttime sky. The OCSD
Plant No. 2 Site has controlled onsite security lighting which has been designed to
minim!D3 spillioD gr light and glare impacts to the surrounding area.
Sensible dsual receptors near the OCSD Plant No. 2 Site include; residential uses
located west of Brookhurst Street, trail users along the Santa Ana Ricer Trail and the
Talbert Marsh Trail, along Pacific Coast Highway and Talbert Regional Park.
The area west of Brookhurst Street between Bushard ACenue and Hamilton ACenue
consists predominately of single family homes, many of which are two stories. As shown
in Figure 3, existing Dews of the OCSD Plant No. 2 Site from along Brookhurst Street
are dsually screened by an existing 81toot block wall and a row of towering eucalyptus
trees. The height of the wall and eucalyptus trees screens both close and distant Dews
into Plant No. 2.
The Santa Ana Ricer Trail extends along the eastern boundary of the OSCD Plant No. 2
Site. A shown in Figures 4 and 5 along the Santa Ana Riser Trail there are intermittent
dews of the OCSD Plant No. 2 Site. The dews are partially obstructed by existing
landscaping and topography.
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 4-1
Existing view of OCSD Plant No. 2 Wastewater Treatment Site
Brookhurst St& Baybreeze Dr
3
q�
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9
3
° Existing view of OCSD Plant No. 2 Wastewater Treatment Site
Brookhurst St & Banning St
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N Water Production Enhancement Project
Study Area
W E Existing Views
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Figure 3
a
i Flow EQ Tank
Site
.t{.,
Existing view from Santa Ana River Trail
Flow EQ Tank Site
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e
N Water Production Enhancement Project
Study Area Views from
W 4..• E Santa Ana River Trail
Figure 4
8
Flow EQ Tank _
Site
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Existing view from Santa Ana River Trail
r
Construction Lay Down Area
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N Water Production Enhancement Project
Study Area Views from
W t"; Ill Santa Ana River Trail
r
Figure 5
s
Section 4
The Talbert Marsh Trail is located along the southern boundary OCSD Plant No. 2. As
shown in Figure 6, along the Talbert Marsh Trail is there is an existing landscaped wall
that proildes a ❑sual barrier between the trail and Plant No. 2.
Pacific Coast Highway is located south of OCSD Plant No. 2. As shown in Figure 11,
from along Pacific Coast Highway are sweeping dews of the Santa Ana Ricer and of
Plant No. 2. The dominant 11sual structure on Plant No. 2 would be the 861toot surge
towers.
OCerlooking from the bluffs near Talbert Regional Park are distant dews of the Pacific
Ocean, Banning Ranch Wetlands, oil drilling operations and Carious structures located
OCSD Plant No. 2. As shown in Figure 7, the long distance dews are partially
obstructed by topography, trees and dense Cegetation.
Regulatory Framework
State
State Scenic Highways Program
The Scenic Highway Program was created in 1963 by the California legislature and was
established to protect scenic highway corridors from changes that would diminish the
aesthetic [alue of adjacent lands. The segment of Pacific Coast Highway that extends
near OCSD Plant No. 2 is not officially designated as State Scenic Highway, but is
designated as eligible for the Scenic Highways Program.
California Coastal Act
The California Coastal Act defines the coastal Cone and establishes land use controsl
for the designated mne. The California Coastal Act; 11 osets specific uses, including
restoration, in which wetlands may be permitted in the coastal mne; [20proddes for
additional redew and appro0als for proposed actions located within designated
sensitiCe coastal areas; and CBOreDjires cities or counties located within the coastal
Cone to prepare a Local Coastal Program. The California Coastal Act has also
identified and reouires the protection of important scenic and ❑sual Dualities of the
coastal areas. All of OCSD Plant No.2 is located within the Coastal Zone.
Regional/Local
County of Orange General Plan
The Orange County Master Plan of Scenic Highways designates the segment of Pacific
Coast Highway near OCSD Plant No.2 as a County Scenic Highway and as a View
scape Corridor.
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 45
Existing view of study area from Pacific Coast Highway
s
m
i
Existing view from Talbert Marsh Trail
d
H Water Production Enhancement Project
Study Area Views from
W - . E PCH &Talbert Marsh
u13
Figure 6
S
A
Flow EQ Tank Site
Existing view of study area from Talbert Park
19
Flow EQ Tank
Trickling Filters Site
z
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N Water Production Enhancement Project
Study Area Views from
yr 2�9 IIITalbert Park
r
Figure 7
s
Section 4
City of Huntington Beach General Plan Coastal Element
The purpose of the Coastal Element is to meet the reDuirements of the Coastal Act and
guide ci is decisions regarding growth, deCelopment, enhancement and preserCation of
the City 8 Coastal Zone and its resources. The Coastal Element identifies the segment
of Pacific Coast Highway near Plant No. 2 as a Major Urban Scenic Corridor and
Landscape Corridor. The Coastal Element further identifies dsual resources within the
coastal Eone which includes; Huntington State Beach, Pacific Ocean, Talbert Marsh,
and the Santa Ana Ricer.
City of Newport Beach Local Coastal Program
Although the study area is not located in the City of Newport Beach, it is located in
proximity to the City of Newport Beach% city limit. The City of Newport Beach is
presently in the process of preparing an Implementation Plan for the Citycs Coastal Land
Study Area and as identified Pacific Coast Highway as a Coastal View Road.
A: Would the project have a substantial adverse effect on a scenic vista?
Less than Significant Impact: Within the Ucinity of the study area scenic resource
public [Jews are prodded from the Santa Ana Ricer Trail, Talbert Marsh Trail, Talbert
Park and Pacific Coast Highway. Additionally, within the study area there are seDaral
priDAe residential uses that haDa dews of Plant No.2 along Brookhurst Street. There
would be the potential that the construction and operation of the proposed project could
encroach into the dew shed of nearby scenic resources. To help measure potential
dew shed impacts to surrounding scenic resources, a dew shed analysis was prepared
where the proposed project would be implemented. Ground and structure elelations
were identified in Plant No. 2 and along the Santa Ana Rimer Trail, Pacific Coast
Highways, the Hamilton Avenue Bridge entrance to Talbert Park and along Brookhurst
Street and were dsually modeled based on the dews of a six foot tall person.
Santa Ana River Trail
The Santa Ana Ricer Trail extends along the eastern boundary of OCSD Plant No 2. As
shown in Figure 8, the proposed Flow eCuali-ation tank and pump station would be
within the dew shed of trail users along the Santa Ana Ricer Trail approximately 2,000
feet north and south of the location where the structures would be constructed.
Presently, along most of the Santa Ana Ricer Trail are existing dews of the OCSD Plant
No. 2 structures. The dsual presence of the proposed flow ellualiDation tank and pump
station structure would not obstruct dews of the Pacific Ocean or the Banning Ranch
Wetlands. Views along the Santa Ana Ricer Trail into Plant No. 2 would not be
substantially different from current dews and would not hace an adcerse impact on any
scenic dstas. Potential dew impacts along the Santa Ana Rilbr Trail would be less than
significant.
r Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 4-8
tom„ r
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Project Viewsheds
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Section 4
Talbert Marsh Trail
As shown in Figure 6, along the Talbert Marsh Trail is there is an existing landscaped
wall that proddes a dsual barrier between the trail and Plant No. 2. The existing
landscaped wall would also dsually screen the proposed flow a ualiCation tank and
pump station structure. Existing scenic dews from the Talbert Marsh Trail would not
change from the current condition. Potential dew impacts would be less than significant.
Talbert Regional Park
Talbert Regional Park is located northeast of OCSD Plant No. 2. The park proddes
distant sweeping dews towards the Pacific Ocean. Presently from Talbert Park are
distant dews of OCSD Plant No. 2 structures, the most dewable being the 86loot
surge towers. As shown in Figure 9, a portion of the flow ellualiDation tank would be
within distant dews from Talbert Regional Park. Because the elelation of Talbert Park
is considerable higher than the eleDation of Plant No.2, the presence of the flow
eDuali0ation tank would not interfere with existing distant dews of the Pacific Ocean and
surrounding area. Existing dews from Talbert Park would not substantially change from
the current conditions. Potential dew impacts would be less than significant.
Pacific Coast Highway
Pacific Coast Highway [PCH is located approximately I mile south from the OCSD
Plant No. 2 Site. Situated between Pacific Coast Highway and Plant No. 2 is the Talbert
Wetlands which proddes an open space dsual buffer for motorist and bicyclist along
PCH. As shown in Figure 10, the presence of the proposed flow enlaliration tank and
pump station structure would not encroach into the dew shed along the Pacific Coast
Highway. Existing dews from Pacific Coast Highway would not change from the current
condition. Potential dew impacts would be less than significant.
Views from Brookhurst Street
Presently, dews of Plant No. 2 along Brookhurst Street are screened by perimeter block
wall and row of eucalyptus trees. As shown in Figure 11, the row of eucalyptus would
also dsually screen the proposed flow ellualilation tank and pump station structure.
Existing dews from Brookhurst Street would not change from the current condition.
Potential dew impacts would be less than significant.
B. Would the project damage scenic resources, including but limited to, trees,
rock outpourings, and historic buildings within a State Highway?
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 4-10
3 .
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Section 4
Less than Significant Impact: According to the California Department of
Transportation Scenic Highways Program, the closest State Scenic Highway to the
OCSD Plant No. 2 Site would be Pacific Coast Highway. The proposed flow
eDialillation tank and pump station structure would located approximately 4,200 feet
from Pacific Coast Highway and would be ❑sually screened by seCeral existing
structures located in the foreground. As shown in Figure 10, with the implementation of
the proposed project existing dews along Pacific Coast Highway would not change from
their current condition. Potential impacts to scenic resources along a State Highway
would be less than significant. No mitigation measures are reCuired.
C. Would the project substantially degrade the existing visual character or quality
of the site and its surrounding?
Less than Significant Impact: The proposed eolalill3tion tank and pump station
structure would be similar in scale and mass compared to seleral other existing
structures located on Plant No. 2 and would be isually compatible. The presence of the
flow eE)jaliCation tank and pump station structure would not substantially degrade the
existing dsual character of the study area and potential aesthetic impacts would be less
than significant. No mitigation measures are reolired.
D. Would the project create a new source of substantial light or glare which would
adversely affect day or nighttime views in the area.
Less than Significant Impact: Implementation of the proposed project would not
inlbl lB the construction of any new structures that would permanently introduce
substantial amounts of new sources of light and glare into the study area. Similar to the
existing buildings on OCSD Plant No. 2 Site, the proposed new structures would haDa
some low Cottage outdoor security lighting. HoweCer the outdoor lighting would be
confined to the immediate area and would not spill oCer into adjacent areas. With the
implementation Mitigation Measures All and A[2 potential light and glare impacts
associated with the operation of the proposed project would be less than significant.
Construction operations for the proposed project would occur during the day. Therefore,
no nighttime construction lighting would be reouired. Some glare impacts could occur
from construction eCuipment during the day. HoweEbr, the impacts would be confined to
the study area and would not haCe any significant offsite light and glare impacts.
Mitigation Measure
A-1: All onsite lighting shall be directed away from adjacent residential, business uses
and away from the Santa Ana Ricer right®f[Way.
A-2: During operation of the project the onsite lighting creates a light or glare issues for
sensitiEe receptor properties, OCWD will implement correcti[B measures to resolCe the
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEgA-Plus Federal Consultation Review 4-14
Section 4
issue. Such correcti[J0 measures may include prodding additional shielding on light
fixtures, relocating lighting fixtures and reducing the intensity of lighting.
4.2 Agricultural Resources/Forest Resources
A. Would the project convert Prime Farmland, Unique Farmland or Farmland of
Statewide Importance to non-agriculture uses?
No impact. According to the State of California Farmland Mapping and Monitoring
Program, the OCSD Plant No. 2 Site does not contain any Prime Farmland, UniDte
Farmland, or Farmland of Statewide Importance. Therefore, no ad[:erse impacts to
Prime Farmland, UniD1e Farmland, or Farmland of Statewide Importance would occur
from the implementation of the proposed project. No mitigation measures are reDlired.
B. Would the project be in conflict with existing zoning for agriculture use or a
Williamson Contract?
No Impact. According to the City of Huntington Beach Zoning Code, the OCSD Plant
No. 2 site is not [tined for agriculture uses. Additionally, the City® General Plan does
not identify that there are any existing Williamson Contracts on the property. Therefore,
implementation of the proposed project will not be in conflict with any existing
agriculture Coning. No mitigation measures are reDtired.
C. Would the project be in conflict with existing zoning for, or cause rezoning of
forest land or timberland.
No Impact. According to the City of Huntington Beach Zoning Code, the OCSD Plant
No. 2 Site is not coned for forest land or timberland. Therefore, implementation of the
proposed project would not cause change of [cone of existing forest or timberland to
other land uses. No mitigation measures are reD/ired.
D. Would the project result in the loss of forest land or conversion of forest land
to non-forest use?
No Impact: Presently, the OCSD Plant No. 2 Site does not contain forest lands.
Therefore, the implementation of the proposed project would not convert existing forest
land to noniforest land. No mitigation measures are re Mired.
E. Would the project involve other changes in the existing environment which,
due to their location or nature, could result in conversion of Farmland to non-
agriculture use or conversion of forest land to non-forest use?
No Impact. The study area is not located on forest land. Therefore, the implementation
of the proposed project will not directly or indirectly result in the loss of any forest land
or result in the convlarsion forest lands to noniforest lands. Additionally, the
implementation of the proposed project would not convBrt existing farmlands within the
study area to nonvagriculture land uses. No mitigation measures are reouired.
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEgA-Plus Federal Consultation Review 4-15
Section 4
4.3 Air Quality
The following analysis is based on an Air Quality and Greenhouse Gas Report prepared
for the Water Production Enhancement Project by Endronmental Science Associates, in
August of 2016. The Air Quality and Greenhouse Gas Report is presented in Appendix
A.
Setting
The study area is located in the City of Huntington Beach, southeast of the corner of
Baybree[13 Drib and Brookhurst Street. Huntington Beach is located within the South
Coast Air Basin [SCABQ which is under the jurisdiction of the South Coast Air Quality
Management District [SCAQMDD The SCAB is a 6,60009[luareirnile coastal plain
bounded by the Pacific Ocean to the southwest and the San Gabriel, San Bernardino,
and San [Jacinto Mountains to the north and east. The SCAB includes the nonidesert
portions of Los Angeles, RiDarside, and San Bernardino Counties, and all of Orange
County. The topography and climate of southern California combine to make the SCAB
an area of high air pollution potential. The SCAB is a coastal plain with connecting
broad Galleys and low hills, bounded by the Pacific Ocean to the west and high
mountains around the rest of the perimeter. The general region lies in the semi[]
permanent highgoressure Cone of the eastern Pacific, resulting in a mild climate
tempered by cool sea breeds with light allerage wind speeds. The usually mild
climatological pattern is disrupted occasionally by periods of extremely hot weather,
winter storms, or Santa Ana winds. During the summer months, a warm air mass
frelluently descends o[er the cool, moist marine layer produced by the interaction
between the ocean® surface and the lowest layer of the atmosphere. The warm upper
layer forms a cap oDbr the cool marine layer and inhibits the pollutants in the marine
layer from dispersing upward. In addition, light winds during the summer further limit
orntilation. Furthermore, sunlight triggers the photochemical reactions that produce
omne.
Ambient Air Quality Standards
Regulation of air pollution is achieEbd through both federal and state ambient air Duality
standards and emission limits for indiddual sources of air pollutants. As reDuired by the
Federal Clean Air Act [CAAQ the U.S. Endronmental Protection Agency m1SEPADhas
identified criteria pollutants and has established National Ambient Air Quality Standards
INAAQSoto protect public health and welfare. NAAQS hale been established for o[bne
CO3Q carbon monoxide ICOQ nitrogen dioxide LN02Q sulfur dioxide [S02Q particulate
matter I>PM10 and PM2.54 and lead [PbD These pollutants are called Mriteria Dair
pollutants because standards hale been established for each of them to meet specific
public health and welfare criteria.
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The NAAQS establish the IeCel for an air pollutant abo11q which detrimental effects to
public health or welfare may result. The NAAQS are defined as the maximum
acceptable concentrations that, depending on the pollutant, may not be eoualed or
exceeded more than once per year or in some cases as a percentile of obserilations.
California has generally adopted more stringent ambient air Duality standards for the
criteria air pollutants [de., California Ambient Air Quality Standards [CAAQSUand has
adopted air Duality standards for some pollutants for which there is no corresponding
national standard, such as sulfates, hydrogen sulfide, dnyl chloride, and risibility❑
reducing particles.
SCAQMD maintains monitoring stations within district boundaries that monitor air Eluality
and compliance with associated ambient standards. The study area is located in the
North Orange County Coastal Air Monitoring Subregion. Currently, the nearest
monitoring station to the study area is the Costa Mesa D MesaVerde Drioa Station 12850
Mesa Verde Dr East, Costa Mesa, CAD This station monitors ambient concentrations of
omne, NO2, CO, and S02, but does not monitor PM2.5 or PM10. The nearest monitoring
station that monitors ambient concentrations of PM2.5 and PM10 is the Anaheim station
located at 1630 W. Pampas Lane. Historical data of ambient clone, NO2, CO, SO2,
PM10 and PM2.5 concentrations from these monitoring stations for the most recent three
years [2012 1-2014Eare shown in Table 3.
Both CARB and USEPA use this type of monitoring data to designate areas according
to their attainment status for criteria air pollutants. The purpose of these designations is
to identify the areas with air Duality problems and thereby initiate planning efforts for
improCement. The three basic designation categories are nonattainment, attainment,
and unclassified. Unclassified is used in an area that cannot be classified on the basis
of aCailable information as meeting or not meeting the standards. In addition, the
California designations include a subcategory of nonattainment®ransitional, which is
g0an to nonattainment areas that are progressing and nearing attainment. The current
attainment status for the SCAB is prodded in Table 4.
Table 3: Study Area Air Quality Data Summary (2012-2014)
Pollutant Monitoring Data by Year
Standards 2012 2013 2014
Owne-Costa Nbsa
Highest 1 HourAlLrage LppmE 0.090 0.095 0.096
Days oibr State Standard 0.09 ppm 2 1 1
Highest 6 Hour AEerage [ppm❑ 0.076 0.063 0.079
Days o[br National Standard 0.075 ppm 1 0 4
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Days oar State Standard 0.070 ppm 1 2 6
Carbon Nbnoxide—Costa Ntsa
Highest 8 Hour Alarage lopm❑ 1.7 2 1.9
Days olbr National Standard 9.0 ppm 0 0 0
Days olbr State Standard 9.0 ppm 0 0 0
Nitrogen Dioxide—Costa Ntsa
Highest 1 Hour ACerage [ppm❑ 0.0744 0.0757 0.061
Days over National Standard 0.100 ppm 0 0 0
Days over State Standard 0.18 ppm 0 0 0
Annual A:13rage [PpmC 0.0104 0.0116 0.011
Days olar National Standard 0.053 ppm 0 0 0
Days o[Er State Standard 0.030 ppm 0 0 0
Sulfur Dioxide—Costa Ntsa
Highest 24 Hour Albrage [ppm❑ 0.0062 0.0042 0.009
Days oar State Standard 0.04 ppm 0 0 0
Particulate Nhtter(PNSo)—Anaheim
Highest 24 Hour Alemge gtg/m3[4 48 77 85
Days oCer National Standard 150 µg/m3 0 0 0
[rneasured6
Days o1br,State Standard 50 µg/ms 0 1 2
Imeasured6
Annual AEsrage qtg/m30? 20 µg/m3 22.4 25.4 26.8
Particulate Natter(PM.$)—Anaheinn
Highest 24 Hour ACerage 4,g/m30? 50.1 37.8 56.2
Days over National Standard 35 µg/m3 4 1 6
irneasured�
Annual ACerage [pg/m3[4 12 µg/ms 10.81 10.1 10.3
NOTES'.
ppm We per mllllom Vglm°n micrograms per cutdc meter.
00 Insufficient data to ilable to determine Me>lue.
a Generally,slate standards and national standards are not to be exceeded more then once per year.
b Concentrations and aC mgea represent federal statistics.Stale and federal statistics may differ because of different sampling methods.
c Measurements are usually collected eery six days.Days oum Me standard represent the measured number of days that the standard has
been exceeded.
SOURCE:SCAOMD 2014,2013a,2012.
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Table 4: South Coast Air Basin Attainment Status
Attainment Status
Pollutant California Standards Federal Standards
O[une Extreme Nonattainment Se[efe Nonattainment
CO Attainment Unclassfied/Attainment
NOz Attainment Unclassfied/Attainment
SOz Attainment Attainment
PMIe Nonattainment Attainment
PMz.s Nonattainment Nonattainment
Lead Attainment Nonattainment
Sensitive Receptors
Sensitiliq receptors are indidduals who are considered more sensitise to air pollutants
than others. The reasons for greater than aDorage sensitidty could include preexisting
health problems, proximity to emissions sources, or duration of exposure to air
pollutants. Schools, hospitals, and con[alescent homes are considered to be relati113ly
sensitille to poor air ntality because children, elderly people, and the infirm are more
susceptible to respiratory distress and other air Dualitylbelated health problems than the
general public. Residential areas are considered sensitille to poor air Duality because
people usually stay home for extended periods of time, with associated greater
exposure to ambient air Duality. Recreational uses are also considered sensiti[e due to
the greater exposure to ambient air I]/ality conditions because rigorous exercise
associated with recreation places a high demand on the human respiratory system.
Currently, the sensitiDa uses located in the study area ❑cinity include residential uses
located directly west of Brookhurst Street from the OCSD Plant No. 2. The closest
residence is located approximately 260 feet 176 metersOfrom the construction area.
Regulatory Setting
Federal
The principal air Duality regulatory mechanism at the federal leLel is the CAA and in
particular, the 1990 amendments to the CAA and the NAAOS that it establishes. These
standards identify the maximum ambient [backgroundDconcentration le[Lis of criteria
pollutants that are considered to be safe, with an adeDuate margin of safety, to protect
public health and welfare. As discussed predously, the criteria pollutants include oCbne,
CO, NO2 [Which is a form of NOxlJ SO2 [Which is a form of SOxq PM10, PM2.5, and lead.
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The CAA also rewires each state to prepare an air Eluality control plan, referred to as a
state implementation plan ESIPD The CAA Amendments of 1990 ECAAAoadded
reouirements for states with nonattainment areas to rellse their SIPS to incorporate
additional control measures to reduce air pollution. The SIP is modified periodically to
reflect the latest emissions inLisntories, planning documents, and rules and regulations
of the air basins, as reported by their jurisdictional agencies. USEPA is responsible for
ret)ewing all SIPS to determine whether they conform to the mandates of the CAA and
its amendments, and to determine whether implementing the SIPS would achieCe air
Duality goals.
The USEPA also has regulatory and enforcement jurisdiction oCer emission sources
beyond state waters [outer continental shelf17 and those that are under the exclusiDP
authority of the Federal goEernment, such as aircraft, IocomotiEbs, and interstate
trucking. USEPAS primary role at the state IeDBI is to oCersee the state air Duality
programs. USEPA sets federal D ahicle and stationary source emissions standards and
proddes research and guidance in air pollution programs.
General Conformity Rule
The General Conformity Rule 140 CFR Part 930reDuires that federal agencies
demonstrate that federal actions conform with the applicable State Implementation Plan
[SIPDin order to ensure that federal acti-ities do not hamper local efforts to control air
pollution. The EPA general conformity rule applies to federal actions occurring in
nonattainment or maintenance areas when the total direct and indirect emissions of
nonattainment pollutants [or their precursorsoexceed specified thresholds. The de
minimis emission thresholds are based on the attainment status of each air basin. Since
the proposed project is located in an air basin that is designated attainment for all
federal criteria pollutants, it is not subject to the General Conformity emissions
thresholds.
State
California Air Resources Board (CARB)
CARB, a department of the California Endronmental Protection Agency [Cal/EPAQ
oDgrsees air Eliality planning and control throughout California by administering the SIP.
Its primary responsibility lies in ensuring implementation of the 1989 amendments to the
CCAA, responding to the federal CAA reEluirements, and regulating emissions from
motor Dohicles sold in California. It also sets fuel specifications to further reduce
DBhicular emissions.
The amendments to the CCAA establish CAAQS, and a legal mandate to achieCe these
standards by the earliest practical date. These standards apply to the same criteria
pollutants as the federal CAA, and also include sulfates, risibility reducing particulates,
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hydrogen sulfide and ❑nyl chloride. They are also generally more stringent than the
federal standards.
CARB is also responsible for regulations pertaining to TACs. The Air Toxics [Hot Spots[]
Information and Assessment Act was enacted in 1987 as a means to establish a formal
air toxics emission in[lontory risk D antification program. Assembly Bill 1AB112588, as
amended, establishes a process that relluires stationary sources to report the type and
Duantities of certain substances their facilities routinely release.
California Green Building Standard Code
In 11anuary 2010, the State of California adopted the 2010 California Green Building
Standards Code ICALGreengwhich became effectiCe in [January 2011. Building off of
the initial 2008 California Green Building Code, the 2010 CAL-Green Code represents a
more stringent building code that reDtires, at a minimum, that new buildings and
renollations in California meet certain sustainability and ecological standards. The 2010
CAL-Green Code has mandatory Green Building prodsions for all new residential
buildings that are three stories or fewer Jhcluding hotels and motels0and all new non❑
residential buildings of any siCe that are not additions to existing buildings.
Regional
South Coast Air Quality Management District (SCAQMD)
Criteria Air Pollutants
SCAQMD attains and maintains air Duality conditions in the SCAB through a
comprehensID3 program of planning, regulation, enforcement, technical innovation, and
promotion of the understanding of air Duality issues. The clean air strategy of SCAQMD
includes preparation of plans for attainment of ambient air Duality standards, adoption
and enforcement of rules and regulations concerning sources of air pollution, and
issuance of permits for stationary sources of air pollution. SCAQMD also inspects
stationary sources of air pollution and responds to citiCen complaints; monitors ambient
air Duality and meteorological conditions; and implements programs and regulations
reDuired by the CAA, CAAA, and CCAA.
Air Quality Management Plan
SCAQMD and the Southern California Association of GoCernments [SCAGOare
responsible for preparing the air Duality management plan EAQMPQ which addresses
federal and state CAA reDuirements. The AQMP details goals, policies, and programs
for improdng air Duality in the SCAB.
The 2012 AQMP was adopted by the SCAQMD GoElarning Board on December 12,
2012. The purpose of the 2012 AQMP for the SCAB is to set forth a comprehensiCe and
integrated program that would lead the region into compliance with the federal 241hour
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PM2.5 air olality standard, and to prodde an update to the SCABrs commitment towards
meeting the federal 8lhour clone standards ISCAQMD, 2013b0 The AQMP would also
sere to satisfy recent USEPA rel]lirements for a new attainment demonstration of the
reloked 1 dour olone standard, as well as a lohicle miles traDAed A/MTDemissions
offset demonstration.) Specifically, the AQMP would serCe as the official SIP submittal
for the federal 2006 241hour PM2.5 standard, for which USEPA has established a due
date of December 14, 2012.2 In addition, the AQMP updates specific new control
measures and commitments for emissions reductions to implement the attainment
strategy for the 8Ehour olone SIP. The 2012 AQMP sets forth programs which reolire
integrated planning efforts and the cooperation of all lelols of golornment: local,
regional, state, and federal. Currently, SCAQMD staff has already begun initiating an
early del elopment process for the next AQMP.
SCAQMD Rules and Regulations
All projects are subject to SCAQMD rules and regulations in effect at the time of
construction. Specific rules applicable to the construction anticipated under the
proposed project would include the following:
Rule 401: Visible Emissions A person shall not discharge into the atmosphere from
any single source of emission whatsoelkr any air contaminant for a period or periods
aggregating more than three minutes in any 1 hour that is as dark or darker in shade as
that designated No. 1 on the Ringelmann Chart, as published by the United States
Bureau of Mines.
Rule 402: Nuisance A person shall not discharge from any source whatsoelor such
Dfantities of air contaminants or other material that cause injury, detriment, nuisance, or
annoyance to any considerable number of persons or to the public, or that endanger the
comfort, repose, health, or safety of any such persons or the public, or that cause, or
haCe a natural tendency to cause, injury or damage to business or property. The
prodsions of this rule do not apply to odors emanating from agricultural operations
necessary for the growing of crops or the raising of fowl or animals.
Rule 403: Fugitive Dust This rule is intended to reduce the amount of particulate
matter entrained in the ambient air as a result of anthropogenic [human[madeofugitiEs
dust sources by reUfiring actions to prelont, reduce, or mitigate fugitilo dust emissions.
1 Although the federal 1-hour ozone standard was revoked in 2005,the USEPA has proposed m require anew 1-how ozone
attainment demonstration in the South Coast extreme ozone nonattainment area as a result of a recent court decision.
Although USEPA has replaced the 1-how ozone standard with a more health protective 8-hour standard,the CAA anti-
backsliding provisions require that California have approved plans for attaining the 1-how standard.
2 Although the 2012 AQMP was approved by the SCAQMD Board on December 7,2012,the plan did not get submitted in the
USEPA by December 14,2012 as it first required approval from CARB.The 2012 AQMP was subsequently approved by
CARS on January 25,2013,and w of February 13,2013 the plan has been submitted by CARS m the USEPA.
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Section 4
Rule 403 applies to any actidty or human[made condition capable of generating fugitile
dust.
Rule 1113: Architectural Coatings No person shall apply or solicit the application of
any architectural coating within the SCAQMD with VOC content in excess of the [blues
specified in a table incorporated in the Rule.
Significant Impact Threshold
The OCWD and the City of Huntington Beach hale not delbloped specific air nlality
thresholds for air iluality impacts. Howeler, as stated in Appendix G of the CEQA
Guidelines, the significance criteria established by the applicable air Duality management
or air pollution control district may be relied upon to make the abole determinations. As
such, the significance thresholds and analysis methodologies in SCAQMD® CEQA Air
Quality Handbook are used in elaluating project impacts. SCAQMD has established daily
mass thresholds for regional pollutant emissions, which are shown in Table 5.
Aside from regional air ntality impacts, projects in the SCAB are also rewired to
analy[t: local air illality impacts. As discussed predously, SCAQMD has deleloped
LSTs that represent the maximum emissions from a project that are not expected to
cause or contribute to an exceedance of the most stringent applicable federal or state
ambient air Duality standards, and thus would not cause or contribute to localiled air
Duality impacts. LSTs are deleloped based on the ambient concentrations of that
pollutant for each of the 38 source receptor areas ISRAsoin the SCAB. The locali[Ed
thresholds, which are found in the mass rate looklup tables in SCAQMD® Final
Localized Significance Threshold Methodology document, were de[Eloped for use on
projects that are less than or equal to fife acres in SKIS and are only applicable to the
following criteria pollutants: NOx, CO, PM10, and PM2.5• The construction and
operational LSTs for a one[acre site in SRA 18 LNorth Costal Orange CountyQ which is
where the Project site is located, are shown in Table 6.
It should be noted that with regards to NOx emissions, the two principal species of NOx
are NO and NO2, with the [gist majority 195 percentoof the NOx emissions being
comprised of NO. Howeler, because adcerse health effects are associated with NO2,
and not NO the analysis of IocaliDad air Duality impacts associated with NOx emissions
is focused on NO2 le[t?ls. For combustion sources, SCAQMD assumes that the
con Darsion of NO to NO2 is complete at a distance of 5,000 meters from the source.
Table 5: SCAQMD Regional Air Quality Significance Thresholds
Pollutant Mass Daily Thresholds (Ibslday)
Construction Operations
Oxides of Nitrogen INOxD 100 55
Reacti[B Organic Gases IROG❑ 75 55
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Respirable Particulate Matter IPM,,D 150 150
Fine Particulate Matter 11PM2.50 55 55
Oxides of Sulfur[SOxo 150 150
Carbon Monoxide [COD 550 550
Table 6: SCAQMD Localized Significance Thresholds
Pollutant Monitored Within SRA 18— One-Acre Site
North Coastal Orange County
Allowable emissions(pounds/day)as a function
of receptor distance (feet)from site boundary
25(m) 50(m)T100(m) 200(m) 500(m)
Construction Thresholds
Nitrogen Oxides INOxd 92 93 108 140 219
Carbon Monoxide ECO❑ 647 738 1,090 2,096 6,841
Respirable Particulate Matter[ffM100 4 13 27 54 135
Fine Particulate Matter I)PM2 s11 3 5 9 22 76
Operational Thresholds
Nitrogen Oxides INOxd 92 93 108 140 219
Carbon Monoxide [COo 647 738 1,090 2,096 6,841
Respirable Particulate Matter IIPM150 1 4 7 13 33
Fine Particulate Matter PM2 so 1 1 1 2 1 3 1 6 19
a
The locali®d Mmsholds listed for Nos in this fade take into consideration the gradual con�sreion of NO to NO2.The analysis of
locall�ed it amlily Impacts associated with NOx emissions focuses on NO¢le21s as May are associated vdt adrarse heart elfects.
SOURCE: SCAOMD,2003 Re Ised 2009�,
A. Would the project be in conflict with or obstruct implementation of the
applicable air quality plan or congestion management plan?
Less than Significant Impact: The study area is located within the SCAB, which is
under the jurisdiction of the SCAQMD. SCAQMD® 2012 AQMP is the applicable air
olality plan for the study area. Projects that are consistent with the regional population,
housing, and employment forecasts identified by SCAG are considered to be consistent
with the AQMP growth projections, since the forecast assumptions by SCAG forms the
basis of the land use and transportation control portions of the AQMP. Additionally,
because SCAG® regional growth forecasts are based upon, among other things, land
uses designated in general plans, a project that is consistent with the land use
designated in a general plan would also be consistent with the SCAG® regional forecast
projections, and thus also with the AQMP growth projections.
The proposed project implements a temporary water storage tank to support the
expansion of the GWRS but would not substantially increase the employment growth
anticipated within the 2012 AQMP. Nor would the proposed project result in the creation
of new housing or potential residential growth. Because the land use would not change,
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and has been in operation since before the creation of the 2012 AQMP, the proposed
project would not change the regional growth forecasts as identified in the local General
Plan or those of the 2012 AQMP. Therefore, the proposed project would not conflict
with, or obstruct, implementation of the AQMP, and this impact would be less than
significant.
B. Would the project violate any air quality standard or contribute substantially to
an existing or projected air quality violation?
Construction
Less than Significant Impact: Construction actidties associated with the proposed
project would generate pollutant emissions from the following construction actidties: 11❑
site preparation: [2oconstruction workers traEbling to and from work site; 3-deliEbry
and hauling of construction supplies to, and debris from, the work site; ADfuel
combustion by on[site construction el7uipment; 15Dtank and building construction and
the application of architectural coatings. These construction actidties would temporarily
create emissions of dust, fumes, eolipment exhaust, and other air contaminants. The
amount of emissions generated on a daily basis would Lary, depending on the intensity
and types of construction actidties occurring simultaneously.
Table 7 summari[es the modeled peak daily emissions of criteria air pollutants and
oame precursors associated with the proposed project for each indiddual phase as well
as for oDsHaps where construction of different phases would occur at the same time.
For the projects construction, CCWD prodded the full inDantory of the enjipment that
would be used during the peak day for each of the construction phase. As shown in
Table 7, the maximum daily construction emissions generated by the proposed project®
worst[case construction scenario would not exceed SCAQMD® daily significance
threshold for any criteria pollutant and therefore would result in less than significant
impacts. No mitigation is reDAred.
Table 7: Proposed Regional Construction Emissions
Construction Activities Estimated Maximum Daily Emissions(lbslday)
ROG I NOx I CO 1SOz 1 PMtr T PM2,6
Indil7dual Phase Emissions
1A 4.66 63.38 28.25 0.13 8.35 4.63
1 B 1.52 17.88 11.34 0.04 0.90 0.63
1 C 0.90 11.15 10.44 0.02 0.73 0.46
1 D 59.65 19.79 21.85 0.03 0.94 1.56
1 E 1.22 16.03 17.49 0.03 0.74 1.35
Phase Overlap Emissions
1 D, 1 E 60.88 1 35.82 1 39.34 1 0.06 1 1.68 2.91
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Maximum Daily Emissions
Maximum Emissions 60.88 63.38 39.34 0.13 8.35 4.63
Regional Significance Threshold 75 100 550 150 150 55
Significant lmpact0 No No I No No I No No
Source:ESA,2015.
Operation
Less than Significant Impact: Implementation of the proposed project would result in
longfterm regional emissions of criteria air pollutants and clone precursors associated
with the operation of the new tank, pump station, and pipeline. As shown in Table 8, the
proposed project would result in long Nrm regional emissions of criteria air pollutants
and o[bne precursors that are below SCAQMD® applicable thresholds. Therefore, the
proposed projects operational emissions would not result in or substantially contribute
to emissions concentrations that exceed the NAAQS and CAAQS. No mitigation
measures are rewired.
Table 8: Operation Emissions
Emissions Source Estimated Emissions (lbslday)
ROG NOx CO S02 PM10 PM2,1
Total Operational 0.0359 0.0179 0.0879 3.5e[4 0.0258 7.11e3
Emissions
Regional Significance 55 55 550 150 100 55
Threshold
Significant Impact0 No No No No No No
C. Would the project result in cumulatively considerable net increase of any
criteria pollutant for which the project region is non-attainment under an
applicable federal or state ambient air quality standard?
Less than Significant Impact: The study area is located within the SCAB, which is
considered the cumulatiL-e study area for air wality. Because the SCAB is currently
classified as a state nonattainment area for omne, PM10, and PM2.5, cumulatiDa
deCelopment consisting of the proposed project along with other reasonably foreseeable
future projects in the SCAB as a whole could ❑olate an air uality standard or contribute
to an existing or projected air Duality ❑olation. HoweCer, based on SCAQMD19
cumulatID3 air Duality impact methodology, SCAQMD recommends that if an indiddual
project results in air emissions of criteria pollutants [ROG, CO, NOx, SOx, PM10, and
PM2.0hat exceed the SCAQMD® recommended daily thresholds for projectispecific
impacts, then it would also result in a cumulatilbly considerable net increase of these
criteria pollutants for which the proposed project region is in non®ttainment under an
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applicable federal or state ambient air Duality standard. As shown in Table 7, the
proposed projects construction emissions would not exceed SCAQMDs daily
thresholds. Thus, because the proposed projects construction[period impact would be
less than significant, the proposed project would not result in a significant cumulatilb
impact, when considered with other past, present and reasonably foreseeable projects.
In addition, the operational emissions associated with the proposed project would also
not exceed the SCAQMDs thresholds of significance for any of the criteria pollutants.
Furthermore, the proposed project would also be consistent with SCAQMDs AQMP.
Thus, the proposed project would not conflict with SCAQMDs air quality planning efforts
for nonattainment pollutants and would not lead to a cumulatiCely considerable net
increase in nonattainment pollutants during operations. ODrrall, the proposed projects
construction and operational emissions contribution to cumulatiQb air quality impacts
would be less than significant. No mitigation measures are required.
D. Would the project expose sensitive receptors to substantial pollutant
concentrations?
Less than Significant Impact: The daily onsite construction emissions generated by
the proposed project were egaluated against SCAQMDs LSTs for a one[acre site to
determine whether the emissions would cause or contribute to ad[brse IocaliCed air
quality impacts.3 The nearest sensitive receptors to the study area are the residential
neighborhoods located across Brookhurst Street to the west. The nearest residential
buildings are located o[]3r 50 meters away from where the construction actidties would
occur. Since the mass rate look1hp tables prodded by SCAQMD only proDdes LSTs at
receptor distances of 25, 50, 100, 200, and 500 meters, the LSTs for a receptor
distance of 50 meters are used to eEsluate the potential locali[ed air Duality impacts
associated with the Projects peak day construction emissions. Table 9 identifies the
daily unmitigated, localiEbd onsite emissions that are estimated to occur during the
proposed projects worst[base construction scenarios based on receptor distance and
phase. As shown in Table 9, the daily unmitigated emissions generated onsite by the
proposed projects worst[base construction scenario would not exceed the applicable
SCAQMD LST for any criteria pollutants. Because the proposed projects worst[base
construction emissions would not exceed SCAQMDs applicable LSTs, the proposed
project would be less than significant for IocaliCed construction impacts. No mitigation
measures are required.
3 According to SCAQMD's LST methodology,LSTs are only applicable to the m-site construction emissions that are
generated by a project and do not apply to emissions generated offsite such as mobile emissions on roadways from worker,
vendor,and haul truck trips.
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Table 9: Localized Daily Construction Emissions
Construction Phase Estimated Maximum Daily On-Site Emissions (lbs/day)
NoxT c0 I PM"' I PM:.s'
50 meters to receptor
Max Indiddual Phase 35.68 21.41 5.63 3.66
1D, 1E o1briap 35.34 38.24 1.52 2.86
Localized Significance Threshold' 93 738 13 1 5
Significant Impacto No No No I No
Localized Operational Air Quality Impacts — Criteria Air Pollutants
During project operations, the daily amount of localised pollutant emissions generated
onsite by the proposed project would not be substantial. The proposed project would not
result in a net increase in onlaite operational emissions as there are no localiied criteria
pollutant emissions associated with electrical or water consumption, solid waste or
wastewater generation, or consumer product use. All criteria pollutant emissions are
associated with mobile sources or consumer products IROGsowhich are not considered
in the LST analysis. Therefore, the proposed project would result in no impacts with
respect to operational LSTs, and no mitigation is reDuired.
Localized Construction Air Quality Impacts—TACs
Less than Significant Impact: The proposed project construction would result in short❑
term emissions of diesel PM, a TAC. Diesel PM poses a carcinogenic health risk that is
measured using an exposure period of 70 years. The exhaust of off[toad heafy[luty
diesel eolipment would emit diesel PM during demolition, site preparation e.g.,
clearingq site grading and excaCation; paring; installation of utilities, materials transport
and handling; building construction; and other miscellaneous actidties. SCAQMD has
not adopted a methodology for analydng such impacts and has not recommended that
health risk assessments be completed for construction[related emissions of TACs.
The dose to which receptors are exposed is the primary factor used to determine health
risk Gle., the potential exposure to TACs to be compared to applicable standardsLi Dose
is a function of the concentration of a substance or substances in the endronment and
the duration of exposure to the substance. Dose is positiCely correlated with time,
meaning that a longer exposure period would result in a higher exposure IeCel for the
maximally exposed indiddual. Thus, the risks estimated for a maximally exposed
indiddual are higher if a fixed exposure occurs o1br a longer period of time. According
to the Office of Endronmental Health Halard Assessment OEHHAQ Carcinogenic
health risk assessments, which determine the exposure of sensitise receptors to TAC
emissions, should be based on a 701year exposure period; howeler, such assessments
should be limited to the period or duration of actidties associated with the proposed
Project. The construction period for the proposed project would be much less than the
? Orange County Water District Water Production Enhancement Project
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701year period used for risk determination 11.25 years[] Because offlitoad heaBilduty
diesel eouipment would be used only for short time periods, project construction would
not expose sensitiEb receptors to substantial emissions of TACs. This impact would be
less than significant.
Project Operations —TACs
Typical sources of acutely and chronically haElardous TACs include industrial
manufacturing processes, automotiL-is repair facilities, and dry cleaning facilities. The
proposed project would not include any of these potential sources, although minimal
emissions may result from the use of consumer products. The operation of the
proposed project would not expose surrounding sensiti[L receptors to substantial
pollutant or TAC emissions.
E. Would the project create objectionable odors affecting a substantial number of
people?
Less than Significant Impact: During construction of the proposed project, exhaust
from ellipment and actidties associated with the application of architectural coatings
and other interior and exterior finishes may produce discernible odors typical of most
construction sites. Such odors would be a temporary source of nuisance to adjacent
uses, but would not affect a substantial number of people. As odors associated with
proposed project construction would be temporary and intermittent in nature, the odors
would not be considered to be a significant endronmental impact. Therefore, impacts
associated with objectionable odors would be less than significant.
Land uses that are associated with odor complaints typically include agricultural uses,
wastewater treatment plants, food processing plants, chemical plants, composting,
refineries, landfills, dairies, and fiberglass molding. The proposed project would be
incorporating a flow en alimtion storage tank at OCSDIs Plant E2 to facilitate the
expansion of the OCWD groundwater recharge facility. While the new tank would store
water processed at the OCSD® wastewater treatment plant, it would not increase the
throughput of the wastewater treatment plant. Therefore, because the proposed project
would not increase the throughput of a land use type that is associated with nuisance
odors, and there ha Ea been no odor complaints within the last two decade, this impact
would be less than significant. No mitigation measures are re[]uired.
4.4 Biological Resources
The following Analysis is based on a Biological Assessment prepared for the Water
Production Enhancement Project by the Orange County Water District Natural
Resources Department in Dine of 2016. The Biological Assessment is presented in
Appendix B
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Biological Setting
The OCSD Plant No.2 Site is located within USGS Newport Beach Quadrangle at
Township 6 South, Range 10 West, and Section 20. The site is deCeloped with
wastewater treatment structures, offices, and paced parking areas and roadways. A
row of eucalyptus trees extends along western boundary of Plant No. 2 and scattering
of natiCe landscaping prodded along the Santa Ana Ricer Trail boarders Plant No. 2 to
the east. A site surley of the study area did not identify any sensiti le biological
resources on Plant No. 2. Within close dcinity to Plant No.2 are two biological
resources; the Talbert Marsh and California Least Tern Colony.
Talbert Marsh is a tidal marsh that has been restored to full tidal action. The water
within Talbert Marsh is seawater from the ocean inlet located south of the marsh
property that fluctuates in height up to 8 feet from tidal flows. Talbert Marsh proddes
habitat for both migratory and resident bird species.
South of Pacific Coast Highway is the location the California Least Tern Natural
PreserDa Area. The California Least Tern Natural PreserCe Area was first established
under the Huntington State Beach General DeCelopment Plan in 1976. It was originally
dedicated on 2.5 acres and was fenced off with a cyclone fence [a heaEylduty, chain[]
link fence topped with barbed wiredto pre Cent predators from harassing the birds. OCer
the years, the California least tern Cs nesting area has expanded beyond the fenced
area, State Parks has erected additional picket fencing to protect the birds. Currently,
the cyclone fence area c000rs approximately 8.9 acres and the picket fence [front yard
area is 3.8 acres. California State Parks protects the nesting area by limiting access,
conducting trash remoCal, grooming the sand periodically, and conducting predator
management.
Sensitive Vegetation Communities
The proposed project would be constructed on lands that haD3 been paled or are in a
disturbed condition. There were no sensitiCe 1:eIgetation communities obserled at the
OCSD Plant No. 2 Site where the proposed construction actidties would occur.
Special Status Plant Species
To determine the potential for special status plant species to be present within the study
area, a database search with the United States Fish and Wildlife information and
Planning Database and the California Department Fish and Wildlife CCDFWLJNatural
DiDarsity Database was conducted. A listing of special status plant species with
potential to occur within the Newport Beach USGS Quadrangle is shown in Table 10.
Subseduent to the database search, OCWD conducted a surCey of the study area to
determine the potential for the species to present within the study area. The
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determination on the potential for the special status plant species to occur within the
study area was based on the following criteria:
• Present: Species was obserlad within the study area within the last year.
• High: The study area supports suitable habitat and the species has been
obserCed within the last year.
• Moderate: The study area supports suitable and the species has not been
obserlled within last two years.
• Low: The study area lacks suitable habitat for the species.
Table 10: Special Status Plant Species
Species Federal State CNPS General Potential for
Habitat/Recent Occurrence Study
Occurrence Area
Chaparral sand[Verbena NL NL 1B.1 Coast Scrub Low
(Abronia Villosa var. audta) Chaparral. Species presumed
extirpated
Aphanisma NL NL 1B.2 Coastal Scrub, Low
(Aphanisma blitoides) Coastal Bluff Scrub, Study Area lacks
Coastal Dunes suitable habitat
Ventura Marsh Milk0tetch E NL Marshes, Swamps, Low
[Astnagalus pycnostachy Coastal Dunes, Study Area lacks
[ar. Lanosissimus Coastal Scrub suitable habitat
Coulter Saltsbush NL NL 1B.2 Coastal Scrub, Low
(Atriplex coulted) Coastal Bluff Scrub, Study Area lacks
Coastal Dunes suitable habitat
South Coast Saltscale NL NL 1 B.2 Coastal Scrub, Low
Coastal Bluff Scrub Study Area lacks
suitable habitat
Dalldson®Saltscale NL NL 1B.2 Coastal Scrub, Low
(Atriplex serenana var. Coastal Bluff Scrub Study Area lacks
davidsonfi) suitable habitat
Southern Tarplant NL NL 1 B.1 Marshes and Low
(centromadia parryi ssp. swamps Study Area lacks
Australis) suitable habitat
Salt Marsh BirdsEbeak E E 1 B.2 Coastal Salt marsh, Low
(Chloropyron maritimum Coastal Dunes Study Area lacks
ss . Maritimum) suitable habitat
Many Stemmed Dudleya NL NL 1 B.2 Chaparral, Coastal Low
(Dudleya Multicaulis) Scrub Study Area lacks
suitable habitat
San Diego ButtomCelery E E 1 B.1 Vernal pools, Low
Iffryngium aristulatum Ear. Coastal Scrub, Study Area lacks
parishii❑ Valley and Foothill suitable habitat
Grasslands
Los Angeles Sunflower NL NL 1A Marshes and Low
(Helienthus nuttallii ssp. Swamps Study Area lacks
Parishfi) suitable habitat
Coulter®Goldfield NL NL 1 B.1 Coastal Salt Low
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Masthenia glabrata ssp. marshes Study Area lacks
CouRed suitable habitat
Mud name NL NL 2.2 Marshes and Low
(Name stenocarpum) swamps Project area lacks
suitable habitat
Gambels Water Cress E T 1B.1 Marshes and Low
(Nasturtium gambelii) swamps Study Area lacks
suitable habitat
Prostrate Vernal Pool NL NL 1 B.1 Vemal pools, Low
Nallarretia coastal scrub Study Area lacks
Navarrotiaprostrate) suitable habitat
Coast woollyheads NL NL 1B.2 Coastal Dunes Low
(Nemacaulis denudate var. Study Area lacks
denudate) suitable habitat
Estuary Seablite NL NL 1 B.2 Marshes and Low
(Suaeda Esteroa) swamps Study Area lacks
suitable habitat
San Bernardino Aster NL NL 1 B.2 Marshes and Low
(Symphyotdchum swamps, coastal Study Area lacks
defoliatum) scrub suitable habitat
Pau l
EFEndangered
TThreatened
NL1Not Liatetl
State Listing tCel',fwnia Endangered Species Act.CDFG
FPTully Protected
E,Endangered
TThreatenetl
StSeral
ssciSpecial Species of Concern
WLlwatcb List
Ni Listed
California Not Plant Sudety CNPS
1APlants pn isumetl to lnd in CelRomia
to Plants core,threatened,or endangered in California and elsewhere
2Plants rare,threatened,or endangered In California but more common elsewhere
3 Plants aboard which we need more renew
4 Plants of limited tliren brdign
CNPS Threat Rank
t Seriously Endangered
.2 Fairly Endangered
.3 Not Very Endangered
Special Status Wildlife Species
To determine the potential for special status wildlife species to be present within the
study area, a database search with the United States Fish and Wildlife Serdce
m1SFWS0information and Planning Database and the Department of California Fish
and Wildlife Natural DiCersity Database was conducted. A listing of special status plant
species with potential to occur within the Newport Beach USGS Quadrangle is shown in
Table 11. Subseolent to the database search, OCWD conducted a surrey of the study
area to determine the potential for the species to be present within the study area. The
determination on the potential for the special status wildlife species to occur within the
study area was based on the following criteria:
a Present: Species was obserled within the study area within the last year.
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• High: The study area supports suitable habitat and the species has been
obseried within the last year.
• Moderate: The study area supports suitable and the species has not been
obserled within last two years.
• Low: The study area lacks suitable habitat for the species.
Table 11: Special Status Wildlife Species
Species Federal State General Potential Occurrence
NabitatlRecent Study Area
Occurrence
Orange throat NIL SSC Low leLal coastal Low
Whiptail scrub, sandy areas with Study Area lacks
As idosce/is h e hrapatches of scrub suitable habitat
Burrowing owl NIL SSC Open growing low Low
(Athens cunicularia) grasslands Study Area lacks
suitable habitat
San Diego Fairy Shrimp E SSC Vernal pools Low
(Branchinecta Study Area lacks
sandle onensis suitable habitat
Western Snowy Plolbr T SSC Sandy Beaches Low
(Charaddus alexandrines Study Area lacks
nivosus suitable habitat
Southwestern Willow E E Riparian woodlands Low
Flycatcher Study Area lacks
Em idonex trailli extimus suitable habitat
Western Mastiff Bat NIL SSC Roosts in cliffs,tall Low
(Eumops perotis buildings, trees and Study Area lacks
califomicus) I tunnels suitable habitat
Big free Bat NIL SSC Roosts in cliffs,tall Low
(Nyctinomops macrotis) buildings, trees and Study Area lacks
tunnels suitable habitat
Pacific Pocket Mouse E SSC Coastal Plains Low
(perognathus Study Area lacks
Ion imembris acifus) suitable habitat
Coast Horned Lilard NIL SSC Low lands along sandy Low
(Phrynosoma biainviliii) washes with scattered Study Area lacks
brush suitable habitat
Coastal California T SSC Coastal sage scrub Low
Gnatcatcher Study Area lacks
(Polioptila callfomica suitable habitat
californica
Lightl:ooted Clapper Rail E E Salt marshes Low
(Rallus longirostris Study Area lacks
levi es) I suitable habitat
Southern California NIL SSC Coastal Marshes Low
Saltmarsh Shrew Study Area lacks
Sorex orafus suitable habitat
California Least Tern E E Sandy Beaches Low
(Stems antillarum) Study Area lacks
suitable habitat
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Least Bells ❑reo E E Low growing riparian Low
(Vireo bellii pusillus) habitats Study Area lacks
suitable habitat
"Send
Federal EntlanOeretl Species Act
E Endangered
T Threatened
California Endanne red Species ActiCalifornia Department Fish Game
FP Fully Protected
E1Entlangereo
TThreatenetl
515ensiti e
SSC Special species of concern
WC warm List
Critical Habitat
The Federal Endangered Species Act reouires the federal golkrnment to designate
Critical Habitat for any species it lists under the Federal Endangered Species Act.
Critical Habitat is defined as 1 Dspecific areas within the geographical area occupied by
the specie at the time of listing, if they contain physical or biological features essential to
conserDation, and those features may reLUire special management considerations or
protection and 2Dspecific areas outside the geographical area occupied by the species
if the agency determines that the area itself is essential for conserCation. According to
the of USFWS Information, Planning, and ConserCation System Database and the
California Department of Fish and Wildlife Natural DiDersity Database, the study area is
not located on lands that are designated as Critical Habitat.
Waters of the United States
A water body is considered Waters of the U.S. if it is: 11 Etraditional nadgable water
ITNWU [BDwetlands adjacent to a TNW; GBononinadgable tributaries of TNW that haDe
perennial or seasonal Flow of water; and 14Dwetlands that are adjacent to non[hadgable
tributaries of TNW that ham perennial or seasonal flow of water. The nearest Waters of
the U.S. to the study area is the Santa Ana Ri[er. The Federal jurisdiction along the
Santa Ana Ri[]3r extends to the ordinary high water mark and to any adjacent wetland
113getation.
Waters of the State of California
According to the State Water Code, Waters of the State are defined as any surface
water, groundwater or wetlands within the boundary of the state. The nearest Waters of
the State to the study area is the Santa Ana Ri[Br. The State jurisdiction along the
Santa Ana Ri[Br extends to the top of the slope to adjacent wetland 113getation.
Wetland Waters of the United States and State California
Wetland Waters are a subset of jurisdictional Waters of the U.S. and the State.
Generally, wetlands are lands where saturation with water is the dominant factor
determining the nature of soil deCBlopment and the types of plant and animal
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communities Ii[Ing in the soil and on its surface. Wetlands generally include swamps,
freshwater marshes, brackish water and saltwater marshes, bogs, liernal pools,
periodically inundated salt flats, intertidal mudflats, wet meadows, wet pastures, springs
and seeps, portions of lakes, ponds, ri[Prs and streams and all areas which are
periodically or permanently collared by shallow water, or dominated by hydrophilic
Cagetation, or in which the soils are predominantly hydric in nature. Presently, there is
no single definition for wetlands. HoweCer, all resource agencies recogniLL that
wetlands must demonstrate the following three essential elements: d Othe site
periodically supports hydrophytic CPgetation, 12Ethe site contains hydric soil and CSDthe
site periodically contains water or the soil is saturated with water at some time during
the growing season of each year.
Project Impacts
A. Would the project have a substantial adverse impact, either directly or through
habitat modifications, on any species identified as a candidate, sensitive or
special status species in local or regional plans, policies or regulations or by the
California Department of Fish and Game or U.S. Fish and wildlife Services?
Onsite Impacts
No Impact: Based on a reDew of databases from United State Fish and Wildlife Serlice
and California Department of Fish and Wildlife and biological sur[Pys conducted within
the study area, it has been determined that there would be low potential for special
status plant species or special status wildlife species to be present on OCSD Plant No.
2. As shown in Table 10 and Table 11, Plant No. 2 lacks suitable habitat to support
special status plant species or special status wildlife species that were identified in the
database search. Additionally, no indications were found that any special status species
were ear present. Therefore, implementation of the proposed project would not result
in adCPrse impacts to any special status plant species or special status wildlife species.
Offsite Impacts
Less than Significant Impact: Located south of OCSD Plant No. 2 is the Talbert
Marsh and south of Pacific Coast Highway is the California Least Tern Colony. Both of
these biological resources could pro-lde suitable nesting habitat for special status bird
species. The construction operations for the proposed project would be confined to
OCSD Plant No. 2. No construction act!Oties would occur at the Talbert Marsh or at the
California Least Tern Colony. Therefore, no direct impacts to special status plant or
wildlife species would occur.
The construction actidties for the proposed project would in MCP the operation of heaEy
construction eDulpment that could operate during nesting season. If the construction
actidty was to occur in close proximity to nesting birds there would be the potential that
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Section 4
breeding patterns could be disturbed. The United States Fish and Wildlife Serdce as
established a noise impact threshold of 60 dBA to identify potential adverse impacts to
nesting birds. The Talbert Marsh is located approximately 3,300 feet from where the
construction actidties would occur and the California Least Tern Colony is located
approximately 4,200 feet from the construction would occur. Based on the nosiest
piece of construction eLUipment that would be used, the noise estimated Ie0al at the
Talbert Marsh and at the California Least Tern Colony would be below 49 dBA.
Additionally, with the presence of the block wall around Plant No. 2 and the traffic noise
along Pacific Coast Highway, it would be Cery unlikely that construction noise would
herd at either location. Potential indirect noise impacts to special status wildlife species
would be less than significant. No mitigation measures are re0uired.
B. Would the project have a substantial adverse impact on any riparian habitat or
natural community identified in local or regional plans, policies, and regulations
or by the California Department of Fish and Game or U.S. Fish and Wildlife
Service?
No Impact: The location where the proposed flow entaliiation tank and pump station
structure would be constructed is currently paled or in a disturbed condition. A surley
conducted at the location where the flow eEualilation tank and pump station structure
would be constructed did not identify any sensitilb Eegetation communities. Therefore,
implementation of the proposed project would not result in adEOrse impacts to sensiti[E
natural communities. No mitigation measures realired.
C. Would the project have a substantially adverse effect on federally protected
wetlands as defined by Section 404 of the Clean Water Act through direct
removal, filling hydrological interruption, or other means?
No Impact: The location where the proposed project would be constructed is paLbd or
in a disturbed condition. A preliminary site surCey conducted on the study area did not
identify any rewired parameters that define Wetland Waters of the U.S. or State.
Therefore, the implementation of the proposed project would not ad[brsely impact
Wetland Waters of the U.S or State. No mitigation measures reDiired.
D. Would the project interfere substantially with the movement of any native
resident or migratory fish or wildlife species or with established native resident or
migratory wildlife corridors, or impede the use of native wildlife nursery sites?
Less than Significant Impact: The OCSD Plant No. 2 Site is currently improled with
buildings, wastewater treatment facilities, roadways and parking areas. The site does
not contain suitable habitat or prodde linkages to suitable habitat to support wildlife
movement. Along the perimeter of Plant No.2 are a row of eucalyptus trees that could
prodde potential nesting opportunities for migratory birds. Therefore, construction
actidties for the proposed project would not inmlLe the remoEel of any trees. Therefore,
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Section 4
potential direct impacts to nesting migratory birds would be abided. Additionally, sound
attenuation measures would be incorporated into the project to minimi[B noise impacts
in the study area.
The Talbert Marsh is located approximately 3,600 feet from the construction actidties
and the California Least Tern Colony is located approximately 4,500 feet from where the
construction would occur. At the distance the construction noise lelels would be
minimal and would not pose a potential disruption to nesting birds. The implementation
of the proposed project would not result in significant adierse impacts to migratory birds
or result in significant adarse impacts to wildlife moD3ment. No mitigation measures
are rewired.
E. Would the project conflict with any local policies or ordinances protecting
biological resources, such as tree preservation policy or ordinance?
No Impact: The City of Huntington Beach does not ham any local policies or
ordinances that prodde for the protection of management of biological resources that
would apply to the study area. Therefore, implementation of the proposed project would
not be in conflict with local polices or ordinances that prodde for the protection of
biological resources. No mitigation measures are relluired.
F. Would the project be in conflict with the provisions of an adopted Habitat
Conservation Plan, Natural Community Conservation Plan, or other approved
local, regional, or state habitat conservation plan?
No Impact: The OCSD Plant No. 2 Site is not included within adopted Habitat
Conser ation Plan. Therefore, implementation of the proposed project would not be in
conflict with any appro[bd Habitat Management Plan or Natural Community
Conserlation Plan. No mitigation measures are rentired.
4.5 Cultural Resources
The following analysis is based on a Phase 1 Cultural Resources Report prepared for
the GWRS Final Expansion Project by Endronmental Science Associates in August of
2016. The Phase 1 Cultural Resources Report is presented in Appendix C.
Existing Setting
The study area is located in the cities of Huntington Beach and Fountain Valley, Orange
County, in southern California. The topography of Orange County includes a
combination of mountains, hills, flatlands, and shorelines. UrbaniDad Orange County is
predominantly within an alludal plain, semi[anclosed by the Puente and Chino Hills to
the north, the San Coalluin Hills to the south, and the Santiago Foothills and the Santa
Ana Mountains to the east. The Puente and Chino Hills, which identify the northern limit
of the plains, extend for 22 miles and reach a peak height of 7,780 feet. To the east and
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southeast of the plains are the Santa Ana Mountains, which hale. a peak height of
5,691[Beet. The Santa Ana Ricer is located adjacent to and just east of the study area.
Prehistoric Setting
The prehistory of the region has been summariEbd within four major hori[bns or cultural
periods: Early 110,000 to 8,000 before present [B.P.W Millingstone 18,000 to 3,000
B.P.q Intermediate 13,000 to 1,500 BRI. and Late Prehistoric 11,500 B.P to A.D. 176911
LWallace, 1955; Warren, 19680
Early Period(10,000 to 8,000 B.P.)
The southern California coast may halls been settled as early as 10,000 years ago
Tones, 19920 These early inhabitants were likely maritime adapted groups exploiting
shellfish and other marine resources found along the coastline [Dixon, 1999; Erlandson,
1994; Vellanoweth and Altschul, 200211 One site located in Newport Bay, Orange
County [CA[ORAI4odates to approximately 9,500 years B.P. and suggests early
intenslie utiliLation of shellfish, fish, and bird resources EDrOCer at al., 1983; Macko,
19980
Millingstone Period(8,000 to 3,000 B.P.)
The Millingstone Period dates to about 8,000 to 3,000 B.P. The transition from the Early
Period to the Millingstone Period is marked by an increased emphasis on the
processing of seeds and edible plants. The increased utilillation of seeds is elldent by
the high freouencies of handstones [tdnnanosoand milling slabs [metateso Around 5,000
B.P., mortar and pestles appear in the archaeological record. Mortars and pestles
suggest the exploitation of acorns IX/ellanoweth and Altschul, 200211 Millingstone Period
sites in Orange County generally date to between 8,000 and 4,000 B.P. Archaeological
eddence suggests a low, stable population centered around semi[ibermanent residential
bases. These sites are located along coastal marine terraces, near the shoreline, bays,
or estuaries. Satellite camps were used to take adlbntage of seasonally aCailable
resources. Marine resources were supplemented by seeds and small terrestrial
mammals. Later Millingstone Period sites indicate a growing reliance on shellfish
[Cleland et al., 200711
Intermediate Period(3,000 to 1,500 B.P.)
The Intermediate Period dates to between 3,000 to 1,500 B.P. Archaeological sites
indicate a broader economic base, with increased reliance on hunting and marine
resources. An expanded in i entory of milling ellipment is found at sites dated to this
period. Intermediate Period sites are characterised by the rise of the mortar and pestle
and small projectile points [Cleland et al., 20071J The number of Intermediate Period
sites in Orange County declined o[br time, particularly around Newport Bay. Climate
changes and drier conditions led to the congregation of populations near freshwater
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sources. Settlement patterns indicate greater sedentism, with reduced exploitation of
seasonal resources and a lack of satellite camps. Coastal terrace sites are not
reoccupied during this time period. These shifts in settlement and subsistence
strategies led to growing population densities, resource intensification, higher reliance
on labor[ihtensiEb technologies, such as the circular fishhook, and more abundant and
di[Brse hunting eDuipment. Rises in disease and inter4tersonal ❑olence, ❑sible in the
archaeological record, may be due to the increased population densities [Cleland et al.,
2007; Raab at al., 19950
Late Prehistoric Period(1,500 B.P. to A.D. 1769)
The Late Prehistoric Period began around 1,500 B.P. and lasted until Spanish contact in
1769. The Late Prehistoric Period resulted in concentration of larger populations in
settlements and communities, greater utili-ation of the a-ailable food resources, and the
delelopment of regional subcultures [Cleland at al., 2007-. Artifacts from this period
include milling implements, as well as bone and shell tools and ornaments. Newport
Bay and San [banlin Hills, abandoned during the Intermediate Period, were reoccupied
during the Late Prehistoric Period. These settlements were smaller than in the
Intermediate. Village sites were located in areas with a multitude of resources. Small
collector groups moled between a small number of these permanent settlements
[Cleland et al., 20070
Ethnographic Setting
The study area is located at the southern extent of Gabrielino[Tong Da territory, near the
boundary with the ElianeDD, or more properly Acjachemen, to the south. Traditionally,
the boundary between the two is identified as either Aliso Creek or the drainage didde
to the north of the creek, roughly 20 miles south of the study area. Both are included
here.
Gabrielino-Tongva
Prior to European coloni ation, the GabrielinoFTongla, a Takic[speaking group,
occupied a di erse area that included: the watersheds of the Los Angeles, San Gabriel,
and Santa Ana ri ers; the Los Angeles basin; and the islands of San Clemente, San
Nicolas, and Santa Catalina Xroeber, 19251J The Gabrielino-Tonga are reported to
hale been second only to the Chumash in terms of population sire and regional
influence [Bean and Smith, 19780
The GabrielinoJongLa were hunter[gatherers and IiCad in permanent communities
located near the presence of a stable food supply. Community populations generally
ranged from 501100 inhabitants, although larger settlements may hale existed. The
Gabdelino[Tong[13 are estimated to hale had a population numbering around 5,000 in
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the prelbontact period, with many recorded tillages along the drainages mentioned
aboEb and in the Los Angeles basin proper [ troeber, 19250
Beginning with the Spanish Period and the establishment of Mission San Gabriel
ArcDigel, NatiCe Americans throughout the Los Angeles area suffered seCere
depopulation and their traditional culture was radically altered. Nonetheless, Gabrielino❑
TongDa descendants still reside in the greater Los Angeles and Orange County areas
and maintain an actile interest in their heritage.
Juaneno-Acjachemen
The EuaneEb or Acjachemen, also TakicEspeaking, occupied a more restricted area
extending across southern Orange County and northern San Diego County. ELaneEb
territory extended along the Pacific coast from midway between Arroyo San Onofre and
Las Pulgas Canyon in the south to Aliso Creek in the north, and continued east into the
Santa Ana Mountains from Santiago Peak in the northwest to the headwaters of Arroyo
San Mateo in the southeast Ttroeber 1925EJ The ELaneEb were bounded by the
GabrielinoJongEO to the north, and the LuiseEb to the east and south.
The ELaneEbEkcjachemen, like the Gabrielino[Tong Ea, subsisted on small game,
coastal marine resources, and a wide leriety of plant foods such as grass seeds and
acoms. Their houses were conical thatched reed, brush, or bark structures. The
CLaneEb inhabited permanent tillages centered around patrilineal clans, with each
❑Ilage headed by a chief, known as a nu Ttroeber 1925; Sparkman 190811 Seasonal
camps associated with tillages were also used. Each tillage or clan had an associated
territory and hunting, collecting, and fishing areas. Villages were typically located in
proximity to a food or water source, or in defensiEB locations, often near Lalley bottoms,
streams, sheltered co Les or canyons, or coastal strands LBean and Shipek 1978EJ
The ELaneEbEAcjachemen population was estimated to haDa numbered approximately
1,000 at the time of European contact. Beginning with the Spanish Period and the
establishment of Mission San Elan Capistrano, the ELaneEb[Acjachemen suffered
seEbre depopulation and their traditional culture was radically altered. Nonetheless,
descendants still reside in the Orange County area and maintain an acti50 interest in
their heritage.
Historic Setting
The historic setting for the study area is didded into three primary periods: the Spanish
Period LA.D. 1769LI821 q the Mexican Period ®1.D. 1821 L1846Q and the American
Period FA.D. 1846 to present[]
Spanish Period(A.D. 1769-1821)
The first European exploration of Orange County began in 1769 when the Gaspar de
Portola expedition passed through on its way from Mexico to Monterey. A permanent
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Spanish presence was established with the founding of Mission San ❑tan Capistrano in
1776 dioo[lar et al., 20020 The mission was founded to break the long journey from
Mission San Diego to Mission San Gabriel [hear Los Angeles0 A large, ornate church
was constructed at the mission from 1797 to 1806, but was destroyed only six years
later in an earth0uake. The church was not rebuilt.
In an effort to promote Spanish settlement of Alta California, Spain granted seligral
large land concessions from 1784 to 1821. At this time, Spain retained title to the land;
indiddual ownership of lands in Alta California was not granted. The parts of Orange
County that would become the City of Huntington Beach and the City of Fountain Valley
began as a Spanish land concession, known as Rancho Los Nietos. A grant of 300,000
acres was gilbn to Manuel Nieto in 1784 in consideration of his military serdce [City of
Huntington Beach, 2000; Logan, 19900
Mexican Period(A.D. 1821-1846)
In 1821, Mexico won its independence from Spain. Mexico continued to promote
settlement of California with the issuance of land grants. In 1833, Mexico seculariLiad
the missions, reclaiming the majority of mission lands and redistributing them as land
grants. During this time, Rancho Los Nietos was didded into file smaller ranchos. The
area of Huntington Beach became part of Rancho Las Bolsas, a 33,460[acre rancho
granted to Maria Catarina RuiElin 1834 [County of Orange, 20110 Maria was the widow
of lose Antonio Nieto, Manuel Nieto® son.
Many ranchos continued to be used for cattle gradng by settlers during the Mexican
Period. Hides and tallow from cattle became a major export for Californios [Hispanic
Californiansq many of whom became wealthy and prominent members of society.
These Californios led generally easy IiDas, IeaUng the hard work to Caoleros diispanic
cowhandsLand Indian laborers. Californios limos centered primarily around enjoying the
fruits of their labors, throwing parties and feasting on Catholic holidays [Pitt, 1994; Starr,
20070
American Period(A.D. 1846 to present)
Mexico ceded California to the United States as part of the Treaty of Guadalupe
Hildalgo, which ended the Mexican American War 118461184811 The treaty also
recogniDgd right of Mexican citillons to retain ownership of land granted to them by
Spanish or Mexican authorities. Howeller, the claimant was renjired to prole their right
to the land before a patent was giDqn. The process was lengthy and costly, and
generally resulted in the claimant losing at least a portion of their land to attorneys fees
and other costs associated with prodng ownership [Starr, 20070
The Gold Rush d849118550saw the first big influx of American settlers to California.
Most of these settlers were men hoping to strike it rich in the gold fields. The increasing
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population prodded an additional outlet for CaliforniosEcattle [Bancroft, 18900 As
demand increased, the price of beef skyrocketed and Californios reaped the benefits.
The culmination of the Gold Rush, followed by deCastating floods in 1861 and 1862 and
droughts in 1863 and 1864, led to the rapid decline of the cattle industry [Bancroft,
189011 Many Californios lost their lands during this period, and former ranchos were
subserviently dilided and sold for agriculture and residential settlement.
Following the admission of California into the United States in 1850, the region of
modern day Orange County was originally part of Los Angeles County. Orange County
was established in 1889, with the City of Santa Ana as County Seat FArmor, 1921 D
History of the Study Area
The study area was once part of a 300,000[bcre Spanish land grant, Rancho Los
Nietos, a part of which became Rancho Las Bolsas during the Mexican Period. Abel
Stearns later acrvtired the land for ranching and cultilation of barley. During the land
boom of the 1880s, the area was subdilided for agricultural and residential
delalopment [County of Orange, 2011; Milkolich, 19860
Predously called Shell Beach and later Pacific City, the town changed its name to
Huntington Beach in 1904 when Henry E. Huntington extended Pacific Electric Railway
serdce to the little community [Carlberg and Epting, 2009; Milkodch, 1986D DiscoCery
of oil in the 1920s led to a population explosion in the town. In one month, the
population of Huntington Beach went from 1,500 to 6,000.
History of OCSD Plant No. 2
In 1921, the cities of Santa Ana and Anaheim agreed to construct a sewer outfall
extending into the Pacific Ocean, thus forming the Orange County Eoint Outfall Sewer
IIOSq and marking the beginning of the OCSD. In 1924, EOS construction was
completed and the first sewage from member cities was discharged into the system.
Three years later, the outfall was extended to a distance of 3,000 feet from shore, and a
new screening plant and pumping station was constructed. In 1941, the first units of the
Primary Treatment Plant, now referred to as Plant No. 1 ❑were constructed. In 1954,
OCSD assumed the duties of DOS and officially commenced operations. OEbr the next
50 years, additional serlices and facilities were constructed at OCSD Plant No. 1. The
portion of the existing facility where the proposed OCSD pipe connection would connect
was constructed within the last 10 years. In 1954, Plant No. 2 was constructed near the
ocean and adjoining Santa Ana Rimer and the second ocean outfall was constructed.
OCSD is currently a public agency that prolldes wastewater collection, treatment, and
disposal serdces for approximately 2.5 million people in central and northwest Orange
County. OCSD is a special district that is goCerned by a Board of Directors consisting of
25 board members appointed from 20 cities, 4 sanitary districts, and one representatilb
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from the Orange County Board of Superdsors. OCSD has two operating facilities
[Plants 1 and 20that treat wastewater from residential, commercial and industrial
sources Eocsd.como
Federal Regulatory Framework
Section 106 of the National Historic Preservation Act
Archaeological resources are protected through the NHPA of 1966, as amended 154
United States Code of Laws EUSCE 300101 et seElq and its implementing regulation,
Protection of Historic Properties E36 CFR Part 8000 the Archaeological and Historic
Preserlation Act of 1974, and the Archaeological Resources Protection Act of 1979.
Prior to implementing an [undertakings—e.g., issuing a federal permit4 Section 106 of
the NHPA reDuires federal agencies to consider the effects of the undertaking on
historic properties and to afford the Addsory Council on Historic PreserEetion and the
State Historic PreserD ation Officer ISHPOE]a reasonable opportunity to comment on any
undertaking that would adD arsely affect properties eligible for listing in the National
Register of Historic Places [National RegisterU As indicated in Section 101[LI[06[➢ADof
the NHPA, properties of traditional religious and cultural importance to a tribe are
eligible for inclusion in the National Register. Under the NHPA, a resource is considered
significant if it meets the National Register listing criteria at 36 CFR 60.4.
National Register of Historic Places
The National Register was established by the NHPA of 1966, as [an authoritat!1b guide
to be used by federal, State, and local golernments, priDate groups and citiEens to
identify the Nation® historic resources and to indicate what properties should be
considered for protection from destruction or impairmentE]136 CFR 60.21J The National
Register recogniElas both historiciperiod and prehistoric archaeological properties that
are significant at the national, state, and local lelels.
To be eligible for listing in the National Register, a resource must be significant in
American history, architecture, archaeology, engineering, or culture. Districts, sites,
buildings, structures, and objects of potential significance must meet one or more of the
following four established criteria [U.S. Department of the Interior, 20020
• Are associated with elents that hale made a significant contribution to the broad
patterns of our history;
• Are associated with the IiEbs of persons significant in our past;
• Embody the distinctioB characteristics of a type, period, or method of construction
or that represent the work of a master, or that possess high artistic [blues, or that
represent a significant and distinguishable entity whose components may lack
indiddual distinction; or,
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• Ham yielded, or maybe likely to yield, information important in prehistory or
history.
Unless the property possesses exceptional significance, it must be at least 50 years old
to be eligible for National Register listing m1.S. Department of the Interior, 20020In
addition to meeting the criteria of significance, a property must haCe integrity. Integrity is
defined as [the ability of a property to conCey its significance0ml.S. Department of the
Interior, 200211The National Register recogniCes seCen Dualities that, in Carious
combinations, define integrity. The seEbn factors that define integrity are location,
design, setting, materials, workmanship, feeling, and association. To retain historic
integrity a property must possess selaral, and usually most, of these selen aspects.
Thus, the retention of the specific aspects of integrity is paramount for a property to
con[A3y its significance.
State Regulatory Framework
California Environmental Quality Act
CEQA is the principal statute go erning envronmental redew of projects occurring in
the state and is codified at Public Resources Code [PRCDSection 21000 at seD CEQA
reDJires lead agencies to determine if a proposed project would halb a significant effect
on the eniiironment, including significant effects on historical or uni-ue archaeological
resources. Under CEQA [Section 21084.1-,]a project that may cause a substantial
ad[erse change in the significance of an historical resource is a project that may hale. a
significant effect on the enilronment. An archaeological resource may lualify as an
[historical resourcellunder CEQA. The CEQA Guidelines Qitle 14 California Code of
Regulations [CCRDSection 15064.5DrecogniD; that an historical resource includes: A❑
a resource listed in, or determined to be eligible by the State Historical Resources
Commission, for listing in the California Register of Historical Resources [California
Register[! [213a resource included in a local register of historical resources, as defined in
PRC Section 5020.1IkDor identified as significant in a historical resource surrey
meeting the reDuirements of PRC Section 5024.1[jgq and Many object, building,
structure, site, area, place, record, or manuscript which a lead agency determines to be
historically significant or significant in the architectural, engineering, scientific,
economic, agricultural, educational, social, political, military, or cultural annals of
California by the lead agency, prodded the lead agency6 determination is supported by
substantial eddence in light of the whole record. The fact that a resource does not meet
the three criteria outlined abolb does not preclude the lead agency from determining
that the resource may be an historical resource as defined in PRC Sections 5020.1 yDor
5024.1.
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Section 4
California Register of Historical Resources
The California Register is ran authoritatiCe listing and guide to be used by State and
local agencies, prillate groups, and citiCens in identifying the existing historical
resources of the State and to indicate which resources deserD3 to be protected, to the
extent prudent and feasible, from Register are based upon National Register criteria
1PRC Section 5024.11110 Certain resources are determined by the statute to be
automatically included in the California Register, including California properties formally
determined eligible for, or listed in, the National Register. To be eligible for the California
Register, a prehistoric or historic1period property must be significant at the local, state,
and/or federal lelel under one or more of the following four criteria:
• Is associated with elents that halt made a significant contribution to the broad
patterns of California® history and cultural heritage;
• Is associated with the lilbs of persons important in our past;
• Embodies the distinctive characteristics of a type, period, region, or method of
construction, or represents the work of an important creatile indiddual, or
possesses high artistic [alues; or
• Has yielded, or may be likely to yield, information important in prehistory or
history.
A resource eligible for the California Register must meet one of the criteria of
significance described abo[D, and retain enough of its historic character or appearance
Gntegrityoto be recognilable as a historical resource and to Conley the reason for its
significance. It is possible that a historic resource may not retain sufficient integrity to
meet the criteria for listing in the National Register, but it may still be eligible for listing in
the California Register.
California Health and Safety Code Section 7050.5
California Health and Safety Code Section 7050.5 reDuire that in the ellant human
remains are discolared, the County Coroner be contacted to determine the nature of
the remains. In the eLlant the remains are determined to be NatiCe American in origin,
the Coroner is reDiired to contact the California NatiCe American Heritage Commission
INAHCDwithin 24 hours to relin[luish jurisdiction.
California Public Resources Code Section 5097.98
California PRC Section 5097.98, as amended by Assembly Bill 2641, proddes
procedures in the eCent human remains of Nati-a American origin are discoCered during
project implementation. PRC Section 5097.98 re-uires that no further disturbances
occur in the immediate dcinity of the discolery, that the discolery is adelluately
protected according to generally accepted cultural and archaeological standards, and
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that further actilities take into account the possibility of multiple burials. PRC Section
5097.98 further reEuires the NAHC, upon notification by a County Coroner, designate
and notify a Most Likely Descendant [BALDoregarding the discoE" of Nati[e American
human remains. Once the MLD has been granted access to the site by the landowner
and inspected the discoDary, the MLD then has 48 hours to prolide recommendations
to the landowner for the treatment of the human remains and any associated graft?
goods.
In the el ent that no descendant is identified, or the descendant fails to make a
recommendation for disposition, or if the land owner rejects the recommendation of the
descendant, the landowner may, with appropriate dignity, reinter the remains and burial
items on the property in a location that will not be subject to further disturbance.
California Public Resources Code Section 21080.3.1
California PRC Section 21080.3.1, as amended by Assembly Bill [ABD52, reDlires lead
agencies to consider the effects of projects on tribal cultural resources and to conduct
consultation with federally and nonifederally recognitgd NatitP American Tribes early in
the ent]ronmental planning process and applies specifically to projects for which a
Notice of Preparation INOPODr a notice of NegatiCe Declaration or Mitigated Negatilb
Declaration IMNDLwill be filed on or after Dily 1, 2015. The goal is to include California
Tribes in determining whether a project may result in a significant impact to tribal
cultural resources that may be undocumented or known only to the Tribe and its
members and specifies that a project that may cause a substantial adD3rse change in
the significance of a tribal cultural resource is a project that may haE S a significant effect
on the enEironment. Tribal cultural resources are defined as [sites, features, places,
cultural landscapes, sacred places, and objects with cultural Elelue to a California NatiD3
American Tribeothat are either included or determined to be eligible for inclusion in the
California Register or included in a local register of historical resources EPRC Section
21074 [a Ell Em
Archival Research
Area of Potential Effects
An Area of Potential Effects EAPEDwas established for the project according to Section
106 of the NHPA in coordination with the OCWD. The APE is shown in Figure 12 and is
defined as:
❑ the geographic area or areas within which an undertaking may directly or
indirectly cause alterations in the character or use of historic properties, if any
such properties exist. The APE is influenced by the scale and nature of an
undertaking and may be different for different kinds of effects caused by the
undertaking 136 Code of Federal Regulations [CFRI BOOA T]
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. ,
OArchaeological Area of Potential Effects
r 1 OCSD Plant No,2
L___
f--t
Contractor
Ln,down Area
His.PC Tan: j
Flaw Tank
I/ I
Construction
Flow EO
m oro.senve / / Control/Meter
I /
/ /
/ C I'll Etion:
Flow O
Pump Station
wo
I /
\\ I
\\
4 \\ 1 [ Z
d / �
y /
/
s 0 2,000
o Feet t
a
N
Water Production Enhancement Project
w E Area of Potential Effects
Figure 12
S
Section 4
The horiDmtal APE encompasses the the Flow EDaalilation Pump Station and Flow
E[]ualilation Control/Meter [about 3.70®cres4 and the area encompassing the pump
station [about 0.28 acre[]The �ertical APE includes the anticipated maximum depth of
ground disturbance of 25 feet below ground surface and the maximum height of the flow
e[]ualiDation tank of 30 feet aboutg ground surface.
South Central Coastal Information Center Records Search
A records search for the APE and a ❑ [Mile radius was conducted on Dane 21, 2016 at
the South Central Coastal Information Center [SCCICq located at California State
UniCersity, Fullerton. The records search included a rellew of all recorded cultural
resources within a ❑ Tnnile radius of the project APE, as well as a redew of cultural
resource reports on file. The Historic Properties Directory was also examined for any
documented historic[period built resources within or adjacent to the project APE. The
results of the SCCIC records search are included in Appendix C.
Previous Cultural Resources Investigations
A total of 61 cultural resources studies hale been conducted within a [] [mile radius of
the project APE. Of the 61 predous studies, file studies included a pedestrian sur[ey of
portions of the APE, and four included archi Cal research for the APE. A complete list of
the 61 studies located within ❑[mile of the project APE is located in Appendix C. Less
than 50 percent of the project APE has been included in predous cultural resources
sur[Bys.
Previously Recorded Cultural Resources
The records search indicated that nine cultural resources h" been predously
recorded within a ❑Gmile radius of the project APE. No cultural resources haDa been
preDously recorded within the project APE. SeD'ral prehistoric sites haCe been
recorded within the search radius along the east bluffs of the Santa Ana Ricer
approximately 2,000 feet east of the project APE.
Historic Map and Aerial Review
Historic maps and aerial photographs were examined in order to prodde historical
information about the APE and to contribute to an assessment of the APES
archaeological sensitidty. ACailable maps include: the 1868 U.S. Surleyor Generals
surrey plat map of Townships 5 and 6 South, Range 10 West the 1895 and 1901 Santa
Ana 1:62,500 topographic Daadrangles; the 1902 Corona 1:125,000 topographic
Duadrangle; and the 1935 Newport Beach 1:31,600 topographic Daadrangles; and 1965
and 1975 Newport Beach 7.51minute topographic Daadrangle. Historic aerial
photographs of the APE from 1938, 1953, 1963, 1972, 1994, 2002, 2003, 2004, 2005,
2009, and 2010 were also examined [historicaerials.com, 2016[]
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The 1868 U.S. SurCeyor General® sura?y plat map shows the APE as being located
within Rancho Las Bolsas. The plat map indicates salt marshes within the current
location of OCSD Plant No. 2. The al ailable historic maps and aerial photographs
indicate that the APE and surrounding area was largely used for agricultural purposes
throughout the 201h century, and did not become urbaniCed until the latter half of the
century. The Santa Ana Rimer is shown confined with artificial IeCees in the 1938 historic
aerial photograph. The OCSD Plant No. 2 is not shown on the 1953 aerial. The OCSD
Plant No. 2 facility is shown on the 1965 Newport Beach 7.51nninute topographic
Djadrangle. Based on a detailed redew of the 1972 and 2016 aerials of the OCSD
Plant No.2, there are structures shown on the 1972 aerial that remain risible on the
2016 aerial photograph.
Native American Outreach — 2016
On [Aine 2, 2016, a SLF search reDiest letter was sent to the NAHC in an effort to
determine whether any sacred sites are listed on SLF for the APE. A response was
prodded on Dine 6, 2016 indicating negatille results for Native American cultural
resources within the project APE. The NAHC recommended outreach to 12 specific
tribal authorities who may want to comment on our search reDrest. A letter to the
NAHCdisted tribal authorities was mailed on [Arne 20, 2016. Phone calls were made to
each of the named tribal members on [Arne 28, 2016. Responses from each tribe is
prodded in Appendix C.
The representatiElas from TongEa Acenstral Terrotorial Tribal Nation,
Gabrieleno/TongEa San Gabriel Band of Mission, Gabrielino TongEa Tribe, Gabrielin
TongEa Nation, and [Ajaneno Band of Mission Indians Acjachemen Nation
recommended that because of the culutuial and spiritual sensitidty of the study area
that the project incorporate NatiE13 American and Archeological Monitoring.
AB 52
In August 2016, OCWD sent letters to two Native American representatiCes who haEb
reDrested to be informed on actidties conducted by the OCWD, under PRC Section
21080.3.1. The OCWD reached out to the Draneoo Band of Mission Indians
Acjachemen Nation and Gabrieleno Band of Mission Indians ❑Kith Nation.
Consultation efforts are currently ongoing.
Geoarchaeological Review
Chris Lockwood, Ph.D., R.P.A., conducted a desktop geoarchaeological redew, of the
project APE and dcinity in order to eCaluate the potential for buried archaeological
resources within the APE. The following section presents the results of Dr. Lockwood®
analysis.
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Geology and Geomorphology
The APE is located in the City of Huntington Beach on the Santa Ana coastal plain in
Orange County, California. It is immediately west of a stretch of the Santa Ana Ricer
that is confined to a flood control channel.
The portion of the APE at OCSD Plant No. 2 is on the distal portion of the alludal fan.
During the late Pleistocene, the portion of the APE at OCSD Plant No. 2 was
approximately 5.5 miles [9.0 km0inland. Historically, the APE consisted largely of salt
marsh, which would ha a been at or just aboCe sea IeDal, and was didded by small
channels. The area was for celery agriculture in historic times. The OCSD Plant No. 2
was initially deleloped for sanitation in 1954, but the parcel, including the APE, was
progressilbly deleloped towards the north oler the next filb decades. The APE is
colered with a palbd surface that is at elelation 314 meters abo e mean sea IelbI
®mslq suggesting the APE contains seleral meters of fill ollorlying the natiD3 salt
marsh deposits. Some of the fill material may haDs originated as dredge spoils from
channelir03tion of the Santa Ana Ri[t:r. Near surface geology the APE is mapped as late
Holocene to latest Pleistocene alludal fan deposits [Morton 2004; Morton and Miller
20060 These deposits consist of grail, sand, and silt transported and deposited by the
Santa Ana Ri[fir. To the south of the APE, the OCSD Plant No. 2 site contains
unconsolidated eolian dune deposits.
soils
Soils within the portion of the APE at OCSD Plant No. 2 are mapped primarily as Bolsa
silt loam INRCS 201611 Boise series soils are deep, somewhat poorly drained soils
deCeloped in mixed alludum parent material on flood plains and basins. The typical soil
pedon consists of a plowed Alborimn [Apl, Ap20deCeloped at the top of relatilaly
unaltered alludal parent material [C1 through C60extending more than 69 inches deep.
The absence of a B[horilon is likely due to the short geological time that has passed
since deposition of the parent material, although agricultural actidty has the potential to
hale disrupted the delelopment of a recognivable 131lorilon as well. The Ahori on in
Bolsa soils ranges from sandy loam to silty clay loam, while the C[loriLon is mainly silt
loam and silty clay loam but may contain thin strata of sandier material 1LJSDA 19970
Significantly, many Bolsa soil pedons contain buried Ahorilons [Jbaleosols0 These
buried Alhorimns represent periods of time in the past during which landform conditions
were relatilaly stable, and during which deposition and erosion were sufficiently
balanced to allow for delelopment and retention of a soil weathering profile. From an
archaeological perspectile, periods of landform stability, such as those signified by
buried Ahori ons, should be correlated with the accumulation and preserlation of
cultural remains. Therefore, Boise soils are considered to halb a high sensitidty for
buried archaeological resources.
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Section 4
Archaeological Potential
Although paled and filled, the portion of the APE at the OCSD Plant No. 2 appears to
retain high sensitidty for buried archeological resources. During the latest Pleistocene
and Holocene, the geomorphic setting of the portion of the APE at the OCSD Plant No.
2 changed from inland to coastal, and rising sea legal resulted in fludal deposition
capable of burying archaeological resources. The portion of the APE at the OCSD Plant
No. 2 was largely salt marsh into the early 20th century, but this is an area that would
ham offered important resources. Owing to its marshy endronment, this area may not
ham been falbred for any substantial occupation, but nonetheless is likely to h" been
❑sited for resource procurement and could contain artifacts associated with those
actidties. Additionally, the saturated conditions offered within this setting may hao�
aided in the preserDition of relatiEbly rare organic artifacts.
Cultural Resources Survey and Results
A cultural resources pedestrian surEEy of the APE was conducted on Lune 16, 2016 by
ArabesDie Said®lbdelwahed to identify the presence of surface archaeological
materials. The OCSD Plant No. 2 consists of existing tanks and waste water treatment
buildings. The locations of the propose flow eLlali[lation tank and flow eMaliCation
control/meter are currently paced and natural ground was not risible. Portions of the
proposed location for the Flow Ewali-ation Pump Station and pipeline connection to the
flow eMaliCation tank are unpaled and were surEayed in regular interCals. No
archaeological or historic built resources were observed within the APE. Potential
historiciperiod buildings/structures were noted at the OCSD Plant No. 2 outside of the
APE.
Project Impacts
A. Would the project cause a substantial adverse change in the significance of a
historical resource as defined in Section 15064.5 of the CEQA Guidelines?
No Impact: One potential historic built resource, OCSD Plant No. 2, was identified as a
result of this study. OCSD Plant No.2 was initially constructed more than 45 years
ago4, although none of the historiciage buildings/structures appear to be within the
APES. The improEBments proposed within OCSD Plant No. 2 are shown in Figure 2.
The proposed construction actidties would haEe no impact on aboEaground builtEl
endronment resources. The actidties would be located in areas where there are no
known historical resources dating from before 1971; where the area is currently only
4 The California OHP recommends including all resources over 45 years of age in the planning process given the lag time
between environmental documentation and project implementation.Generally,resources more than 50 years of age require
evaluation for listing in the National Register and California Register in assess impacts to historic properties under Section
106 of the NHPA and historical resources under CEQA.
5 The project may require creation of a separate architectural APE in order to adequately address direct/indirect effects to historic
builtrescurces.
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graded and paced. The implementation of the Water Enhancement Project would not
adlersely impact any historic or potentially historic resource.
B. Would the project cause a substantial adverse change in the significance of an
archaeological resource pursuant to Section 15064.5 of the CEQA Guidelines?
Less than Significant with Mitigation: As a result of this study, no archaeological
resources were identified within the APE. Hower, based on the results of study, the
project APE should be considered highly sensitiLa for subsurface archaeological
resources. Since the project includes ground[disturbing actidties, there is a potential for
discoDary of subsurface archaeological deposits that could Dalify as historic properties
under Section 106 of the NHPA and/or historical or uniDue archaeological resources
under CEQA. This potential impact to unknown archaeological resources would be
considered significant. Mitigation Measures CR11, CR[2, and CR13 are recommended to
ensure that the project would result in No Historic Properties Affected under Section 106
of the NHPA and less than significant impacts to historical or unill a archaeological
resources under CEQA.
Mitigation Measures
CR-1: Prior to earth modng actidties, a Dlalified archaeologist meeting the Secretary of
the Interiors Professional Qualifications Standards for archaeology [U.S. Department of
the Interior, 2008owill conduct cultural resources sensitidty training for all construction
personnel. Construction personnel shall be informed of the types of cultural resources
that may be encountered, and of the proper procedures to be enacted in the slant of an
inadlartent discollary of archaeological resources or human remains. OCWD will
ensure that construction personnel are made aLailable for and attend the training and
retain documentation demonstrating attendance.
CR-2: Prior to the start of any ground[disturbing actidties, OCWD will retain an
archaeological monitor to obserCe all ground[disturbing actidties. Archaeological
monitoring will be conducted by a monitor familiar with the types of archaeological
resources that could be encountered and shall work under the direct superdsion of the
Dualified archaeologist. Monitoring may be reduced or discontinued by the -ualified
archaeologist, in coordination with OCWD, based on obser[ations of subsurface soil
stratigraphy and/or the presence of older C[horimn deposits. The monitor will be
empowered to halt or redirect ground[disturbing actidties away from the dcinity of a
discoLbry until the qualified archaeologist has eCaluated the disco Cary and determined
appropriate treatment. The monitor will keep daily logs detailing the types of actidties
and soils obser ed, and any discoCeries. After monitoring has been completed, the
Dualified archaeologist shall prepare a monitoring report that details the results of
monitoring. The report shall be submitted to OCWD, SCCIC, and any NatlCe American
groups who reD/est a copy.
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CR-3: In the elent of the discelary of archaeological materials, OCWD or its contractor
shall immediately cease all work actidties in the area [within approximately 100 feetoof
the discoEbry until it can be eEbluated by the oualified archaeologist. Prehistoric
archaeological materials might include obsidian and chert flaked[stone tools le.g.,
projectile points, knifes, scrapers0or toollhnaking debris; culturally darkened soil
midden®containing heat affected rocks, artifacts, or shellfish remains; and stone
milling e0uipment le.g., mortars, pestles, handstones, or milling slabsq and battered
stone tools, such as hammerstones and pitted stones. Historic[Ueriod materials might
include stone or concrete footings and walls; filled wells or prides; and deposits of
metal, glass, and/or ceramic refuse. Construction shall not resume until the Dialified
archaeologist has conferred with OCWD on the significance of the resource. SWRCB
shall be afforded the opportunity to determine whether the discolery reajires
addressing under Section 106 Post[Re lew Discoferies prodsions prodded in 36 CFR
800.13.
If it is determined that the discoCered archaeological resource constitutes a historic
property under Section 106 of the NHPA or a historical resource under CECA,
abidance and preserlbtion in place shall be the preferred manner of mitigation.
PreserEbtion in place maintains the important relationship between artifacts and their
archaeological context and also serlbs to aloid conflict with traditional and religious
lalues of groups who may ascribe meaning to the resource. Preserlation in place may
be accomplished by, but is not limited to, afbidance, incorporating the resource into
open space, capping, or deeding the site into a permanent conserfation easement. In
the eDmt that preserfation in place is demonstrated to be infeasible and data recol ery
through excamtion is the only feasible mitigation afailable, an Archaeological
Resources Treatment Plan that proddes for the adenjate recolery of the scientifically
conseojential information contained in the archaeological resource shall be prepared
and implemented by the Dialified archaeologist in consultation with OCWD. The
appropriate NatiE0 American representatiE0s shall be consulted in determining
treatment for prehistoric or NatiEB American resources to ensure cultural [clues
ascribed to the resource, beyond that which is scientifically important, are considered.
C. Would the project disturb any human remains, including those interred outside
of formal cemeteries?
Less than Significant with Mitigation: NatiDa American respondents indicated
sensibility for archaeological resources in the APE and surrounding area gilen the
proximity to the Santa Ana Ricer corridor. In addition, the geoarchaeological redew
indicates that the portion of the APE within OCSD Plant No. 2 was largely salt marsh
into the early 20th century and would hale offered important resources. Owing to its
marshy endronment, this area may not haDq been fafbred for any substantial
occupation, but nonetheless it is likely to haDq been dsited for resource procurement
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and could contain artifacts associated with those actidties. Additionally, the saturated
conditions offered within this setting could hale aided in the preserlation of relatilely
rare organic artifacts. Mitigation Measures CRA is recommended to ensure that the
project would result in No Historic Properties Affected under Section 106 of the NHPA
and less than significant impacts to historical or uniDue archaeological resources under
CEQA.
Mitigation Measure
CR-4: Prior to issuance of a grading permit and prior to start of any ground[disturbing
actidties, OCWD will retain a NatiDa American monitor to obserCe all ground[ disturbing
actidties. The monitor shall be obtained from a Tribe that is traditionally and culturally
affiliated with the area, according the NAHC list. The monitor shall be empowered to
halt or redirect ground[disturbing actidties away from the Jcinity of a discoCery until the
ilualified archaeologist has eDaluated the disco-ery and determined appropriate
treatment. Monitoring may be reduced or discontinued, in coordination with OCWD and
the nialified archaeologist, based on obserlations of subsurface soil stratigraphy and/or
the presence of older C[horiibn deposits.
D. Would the project directly or indirectly disturb or destroy a unique
paleontogical resource or site?
Less Than Significant Impact with Mitigation: Dr. Samuel A. McLeod, Ph.D., of the
Natural History Museum of Los Angeles County, Vertebrate Paleontology Section,
conducted a thorough search on one 16, 2016 of the paleontology collection records
for the locality and specimen data for the proposed project. No Vrtebrate fossil
localities lie within the project APE; howellar, there are localities nearby from the same
sedimentary units that may occur subsurface in the project APE. The closest L-ertebrate
fossil locality from Quaternary Terrace deposits is LACM 7366, approximately 2.6 miles
west at Huntington Drilb and north of PCH. LACM 7366 produced specimens of marine,
freshwater, and terrestrial specimens including leopark shark, Triakis, threellpined
stickleback, Gasterosteus, garter snake, Thamnophis, desert shrew, Notiosorex, and
most prominently, pocket gopher, Thomomys. A series of fossil localities, LACM 742211
7425, are located a few hundred feet north-northwest of LACM 7366. These localities
produced fossil specimens of mammoth, Mammuthus, bison, Bison, and horse, Equus,
from Alludum or dune deposits. The closest lrtebrate fossil locality from Quaternary
deposits is LACM 6370 located approximately 1.6 miles southeast at the Hoag Hospital
lower campus parcel near the intersection of Superior ACenue and PCH. LACM 6370
produced a specimen of a fossil horse, Equus. Fossil locality LACM 3267 located
approximately 2 miles northeast, near the intersection of 19th Street and Anaheim
ADmue, produced a specimen of a fossil elephant, Proboscidea in Quaternary deposits.
Fossil locality LACM 4219, located approximately 3.3 miles along the Newport Freeway
[State Route 55Lnear Santa Isabel ACenue, produced fossil specimens of turtle,
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Chelonia, and camel, Camelidae. Towards the northern portion of the APE, east of the
Santa Ana Ricer near the top of the mesa bluffs along Adams A[enue, [ertebrate fossil
locality LACM 1339 produced fossil specimens of mammoth, Mammuthus, and camel,
Camelidae, bones from sands approximately 15 feet below the top of the mesa that is
o[edain by shell bearing silts and sands.
The entire APE has surface deposits of younger Quaternary Alludum, denied as fludal
deposits from the Santa Ana Riler to the east of the project APE. No fossil [ertebrate
localities are located nearby these deposits, and they are unlikely to contain significant
Vrtebrate fossils, at least in the uppermost layers. Small hills and bluffs both east and
west of the project APE, howe[er, define the Santa Ana Ricer floodplain drainage and
are mapped as haling exposures of marine Quaternary Terrace deposits. These or
other older Quaternary deposits may occur in the project APE at unknown depth. There
is a low potential to unco[er significant [ertebrate fossil remains during surface grading
or shallow exca[etions in the APE. Howe[er, excaletions that extend down into the
older Quaternary deposits may encounter significant fossil Certebrate specimens. Since
the project includes ground[disturbing actidties, there is a potential for discoCery of
fossils that may be considered significant paleontological resources. This potential
impact to unknown paleontological resources would be considered significant. The
following mitigation measures CR15, CROB and CR17are recommended to ensure that
the project would result in less than significant impacts to unioue paleontological
resources under CEQA.
Mitigation Measures
CR-5: Prior to the start of any ground[disturbing actidties, OCWD shall retain a D alified
paleontologist meeting the Society of Vertebrate Paleontology [SVPDStandards [SVP,
20101J The Dtalified paleontologist shall contribute to any construction worker cultural
resources sensitidty training either in person or ❑a a training module prodded to the
Dlalified archaeologist. The training session shall focus on the recognition of the types
of paleontological resources that could be encountered within the project site and the
procedures to be followed if they are found. The Dualified paleontologist shall also
conduct periodic spot checks in order to ascertain when older deposits are encountered
and where monitoring shall be reDuired.
CR-6: Prior to the start of any ground[disturbing actidties, OCWD shall retain a
paleontological monitor to obser[e all ground[disturbing actidties within older
Quaternary deposits. Paleontological resources monitoring shall be performed by a
D/alified paleontological monitor, or cross Trained archaeological/paleontological
monitor, under the direction of the Dualified paleontologist. The monitor shall hale the
authority to temporarily halt or dil ert work away from exposed fossils in order to reoolbr
the fossil specimens. Monitoring may be reduced or discontinued by the Dlalified
paleontologist, in coordination with OCWD, based on obserDations of subsurface soil
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stratigraphy and/or other factors and if the Elualified paleontologist determines that the
possibility of encountering fossiliferous deposits is low. The monitor shall prepare daily
logs detailing the types of actidties and soils obserLed, and any discoEbries. The
❑ualified paleontologist shall prepare a final monitoring a report to be submitted to
OCWD and filed with the local repository. Any recoEbred significant fossils shall be
curated at an accredited facility with retrie0able storage.
CR-7: If construction or other project personnel discoEbr any potential fossils during
construction, regardless of the depth or presence of a monitor, work in the Elcinity
Ewithin 100 feetoof the find shall cease until the Elualified paleontologist has assessed
the discoEBry and made recommendations as to the appropriate treatment.
4.6 Geology/Soils
Existing Setting
Regional Geology
The study area is located in the Peninsular Ranges Geomorphic PrOdnce. The prodnce
traDarses the southwestern end of California and is bounded by the TransDarse Range
prodnce to the north, the Colorado Desert prodnce to the east, and the Pacific Ocean
to the west. Then topography of the prodnce is characteriCed as alternating northwest
trending ridges and CRlleys with the bedrock geology most closely resembling the Sierra
NeCada with granitic intrusions into®Ider metamorphic rocks. Near surface geologic
units within the study area include wellMorted, fine grained sand and silt, medium to fine
grained sand deposit in the late Holocene by the Santa Ana RiEer, sandy, silty and
clayey organic Erich estuarine deposits and modern sandy wash deposits confined within
the Santa Ana Riler channel.
Local Topography
EleE,ations within the study area range from sea IeEel to 25 feet. Due to minor elemtion
changes across the study area, the slope gradients within the study area are relatilely
flat.
Faulting and Seismicity
There are no actiLe faults tralersing the study are. Howelbr, the study area is located
within a seismic actiEb region and would be susceptible to ground shaking from selbral
actiDa and potentially actile faults in the region, including the Newport Inglewood Fault,
San LbaDuin Hills Fault, Elsinore Fault, Palos Verdes Fault and the San Andreas Fault.
Liquefaction Hazards
According to the California Department of Geologic Surlby Seismic HaDard Zone Map,
the study area is located within an area that would be susceptible to the occurrence of
Il Olefaction.
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Landslide Hazards
According to the California Department of Geologic SurCey Landslide HaCard Map, the
study area is not located within an area that would be susceptible to landslides.
Soils
The predominate soil association within the study area is the Heuneme[Bolsa
Association, a nearly leD31, excessi ely drained fine sand loams located on alludal fans
and floodplains. The soils are characteriled has hating a moderate3o[ligh shrinklawell
potential.
Project Impacts
Al. Would the project expose people or structures to potential substantial
adverse effects, including the risk of loss, injury or death involving rupture of an
unknown earthquake fault, as delineated on the most Alquuist-Priolo Earthquake
Fault Zoning Map?
No Impact: According to the California Geologic SurDey Seismic Hall3rd Zone Map, the
study area is not located within a designated Fault[Rupture Halard Zone. Therefore, the
potential for surface rupture impacts would be unlikely. No mitigation measures are
reDlired.
A2. Would the project expose people or structures to potential substantial
adverse effects, including the risk of loss, injury or death involving strong
seismic ground shaking?
Less Than Significant Impact with Mitigation: The study area is located in a
seismically actiDa region that could be subject to seismic shaking during earthDlakes
generated from seCeral surrounding actiCe faults in the region. An actin fault is one that
has historically produced earthLuakes or shown eUdence of moDament within the past
11,000 years. The closest actin fault would be the Newport Inglewood fault system.
The Newportmnglewood Fault Zone has a probability of approximately 1 percent of
producing an earthquake larger than magnitude 6.7 in the next 30 years IUSGS, 2008D
An earthquake of this magnitude could subject the study area to periodic shaking,
possibly of considerable intensity. The degree of shaking felt would depend on the
distance from the earthquake source and site of earthquake and type of subsurface
material on which the site is situated.
The proposed project would not inCbILb the construction of any habitable buildings that
would pose risk to people during an earthquake. The risk for seismic shaking impacts at
the study area would be similar to other areas in the southern California region. The
proposed project would be designed to meet the Essential Facilities Standards of the
California Uniform Building Code to withstand anticipated ground shaking caused by an
earthquake within an acceptable lelbi of risk. With the implementation of Mitigation
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Measure GE011 the potential risk of seismic shaking impacts resulting in loss, injury or
death would be less than significant.
Mitigation Measure
GEO-1: The OCWD will ensure that all structures for the proposed project are designed
and constructed in compliance with current engineering practices, including the
California Uniform Building Code and all applicable seismic engineering guidelines.
A3. Would the project expose people or structures to potential substantial
adverse effects, including the risk of loss, injury or death involving liquefaction?
Less than Significant Impact with Mitigation: The California Geologic SurCBy
Seismic HaDard Zone Map indicates that the study area lies within a Liquefaction
Hag3rd Zone. The proposed project would be designed and constructed in compliance
with current engineering practices, including the California Uniform Building Code and
all applicable seismic engineering guidelines. With the implementation of Mitigation
Measure GE011 the potential risk of liquefaction impacts resulting in loss, injury or
death would be less than significant.
Mitigation Measure
Mitigation Measure GE011 rewired.
A4. Would the project expose people or structures to potential substantial
adverse effects, including the risk of loss, injury or death involving landslides?
No Impact: The California Geologic Surley HaDard Zone Map indicates that the study
area does not lie within a Landslide HaDard Zone. No mitigation measures are reDuired.
B. Would the project result in substantial soil erosion or the loss of topsoil?
Less than Significant Impact with Mitigation: Erosion can occur by Lbrying
processes and may occur where bare soil is exposed to wind or modng water. The
processes of erosion are generally a function of material type, terrain steepness, rainfall
or irrigation IeCels, and surface water drainage conditions. The exca ation and grading
actidties associated with the proposed project would uncoCer soils which could increase
the potential for erosion impacts to occur. Additionally, construction eDuipment
mobiliCation/demobilig3tion and construction worker traffic could transport soil to streets
and into local and regional drainage systems and wind erosion occurring on unprotected
soils could blow dust particles offsite onto adjacent streets and drainage systems.
The proposed project would disturb and uncoLbr soils in OCSD Plant No. 2, increasing
the potential for erosion impacts. To minimiLb erosion impacts OCWD would file a
Notice of Intent mdOlgwith the State Water Resources Control Board and would prepare
and implement a Storm Water Pollution PreCsntion Plan [SWPPPI]The SWPPP would
contain a map showing the building site, onsite and adjacent roadways, storm water
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collection points and drainage patterns across the site. The SWPPP would also prodde
a list of Best Management Practices rBMPOthat would be used to minimi[B sediment
and wind erosion impacts. With implementation Mitigation Measure GEOCB potential
erosion impacts would be less than significant.
Mitigation Measure
GEO-2: Prior to the start of construction OCWD shall file a Notice of Intent INOIDwith
the State Water Resources Control Board and prepare and implement Storm Water
Pollution PreCention Plan to minimiLb potential erosion impacts.
C. Would the project be located on a geologic unit or soil that is unstable or that
would become unstable as a result of the project and potentially result in on or
off site landslide, lateral spreading, subsidence, liquefaction or collapse?
Liquefaction
Less Than Significant Impact with Mitigation: The California Geologic SurCey
Seismic HaDard Zone Map indicates that the study area lies within a LiDuefaction
Hard Zone. The proposed project would be designed to meet Essential Facilities
Standards of the California Uniform Building Code to withstand potential IiOuefaction
impacts caused by an earthDiake within an acceptable IeCel of risk. With the
implementation of Mitigation Measure GE011 the potential risk of liquefaction impacts
would be less than significant.
Subsidence
Less than Significant Impact: Subsidence is characters ed as a sinking of the ground
surface relatillo to surrounding areas and can generally occur where deep alludal soil
deposits are present in [alley and basin areas. Subsidence could potentially result in
ground fractures that could cause damage to surface improlements. Subsidence is
typically associated with groundwater withdrawal. No subsidence has been
documented in the study area and the proposed project does not inmllla the extraction
of groundwater. Therefore, potential subsidence impacts associated with the proposed
project would be less than significant. No mitigation measures are reDiired.
Landslide
According to the California Department of Geologic SurEay Landslide HaDard Map, the
study area is not located within an area that would be susceptible to landslides. No
mitigation measures are re0uired.
Mitigation Measure
Mitigation Measure GEOd reDuired.
D. Would the project be located on expansive soil, as defined in Table 18-1-B of
the uniform Building Code, creating substantial risks to life or property?
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Less than Significant Impact with Mitigation: ExpansilIg soils are characteriElad as
specific clay materials with the capacity to shrink, swell or otherwise significantly change
mlume due to [Priations in moisture content. Expansi[�e soils could cause excessiEb
cracking and healing of structures with shallow foundations and concrete. The soils
within the study area are characteriDad has haling a moderatellolhigh shrink[swell
potential. All earthwork actidties conducted for the proposed project would be in
compliance with geotechnical reDiirements identified in site specific geotechnical
studies and the California Uniform Building Code. With the implementation of Mitigation
Measure GEOCB potential soil constraints associated with construction of the proposed
project would be less than significant.
Mitigation Measure
GEO3: The OCWD will ensure that all structures for the proposed project are designed
and constructed in compliance with building site specific geotechnical studies and the
California Uniform Building Code.
E. Would the project have soils incapable of adequately supporting the use of
septic tanks or alternative waste disposal systems where sewers are not available
for the disposal of wastewater?
No Impact: The proposed project does not inml119 the construction of septic tanks or
altemati[�e disposal systems. Therefore, the construction and operation of the proposed
project would not result in ad[Erse impacts in regards to the use of septic tanks or
altemati0a disposal systems.
4.7 Greenhouse Gas Emissions
The following analysis is based on the Air Quality and Greenhouse Gas Analysis Report
prepared by Endronmental Science Associates in Jily 2016. The Air Quality and
Greenhouse Gas Analysis Report is presented in its entirety in Appendix A.
Setting
[Global warmingCand Global climate changel3are the terms used to describe the increase
in the a-erage temperature of the earth® near[surface air and oceans since the mid 20th
century and its projected continuation. According to the International Panel on Climate
Change ]PCCEwarming of the climate system is now considered uneniimcal APCC,
20071J Natural processes and human actions ham been identified as the causes of this
warming. The IPCC has concluded that isriations in natural phenomena such as solar
radiation and mlcanoes produced most of the warming from preindustrial times to 1950
and had a small cooling effect afterward. After 1950, increasing GHG concentrations
resulting from human actidty such as fossil fuel burning and deforestation are belieCed to
be responsible for most of the obserced temperature increase. Increases in GHG
concentrations in the earths atmosphere are thought to be the main Cause of human❑
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induced climate change. Certain gases in the atmosphere naturally trap heat by impeding
the exit of solar radiation that is reflected back into space after striking the earth. This is
sometimes referred to as the [greenhouse effectoand the gases that cause it are called
[greenhouse gases.E]Some GHGs occur naturally and are necessary for keeping the
earths surface inhabitable. Howe[Pr, increases in the concentrations of these gases in
the atmosphere during the last 100 years hale decreased the amount of solar radiation
that is reflected back into space, intensifying the natural greenhouse effect and increasing
aCerage global temperatures.
Carbon dioxide [CO24 methane 1CH49 nitrous oxide IN20Q hydrofluorocarbons IHFCsq
perfluorocarbons IPFCs4 and sulfur hexafluoride ISFeDare the principal GHGs. When
concentrations of these gases exceed natural concentrations in the atmosphere, the
greenhouse effect may be intensified. CO2, CH4 and N20 occur naturally, and through
human actidty. Emissions Of CO2 are largely byproducts of fossil fuel combustion,
whereas CH4 results from offigassing6 associated with agricultural practices and
landfills. Other human-generated GHGs include fluorinated gases such as SFCs, PFCs
and SF6, which hale much higher heat-absorption potential than CO2, and are
byproducts of certain industrial processes.
CO2 is the reference gas for climate change because it is the predominant GHG
emitted. The effect that each of the aforementioned gases can hale on global warming
is a combination of the mass of their emissions and their global warming potential
1 GWPD GWP indicates, on a poundmorpound basis, how much a gas contributes to
global warming relatile to how much warming would be caused by the same mass of
CO2. For example, CH4 and N20 are substantially more potent GHGs than CO2, with
GWPs of 21 and 310 times that of CO2, respectilely.
In emissions inCentories, GHG emissions are typically reported in terms of pounds or
metric tons of CO2 eDuiLalents [CO2eu CO2e is calculated as the product of the mass
emitted of a giDan GHG and its specific GWP. While CH4 and N20 hale much higher
GWPs than CO2, CO2 is emitted in such Dastly higher Duantities that it accounts for the
majority of GHG emissions in CO2e, both from residential/commercial deL-elopments
and human actidty in general.
Regulatory Environment
Federal
The federal CAA does not specifically regulate GHG emissions; howe[Pr, the U.S.
Supreme Court has determined that GHGs are pollutants that can be regulated under
the federal CAA. There are currently no federal regulations that set ambient air Duality
standards for GHGs.
6 Off-gassing is defined as the release of chemicals under normal conditions of temperature and pressure.
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State
Executive Order S-3-05
In 2005, in recognition of California® orinerability to the effects of climate change,
Golemor Schwar[Enegger established Executivb Order SC9105, which set forth a series
of target dates by which statewide emissions of GHGs would be progressilbly reduced,
as follows:
• By 2010, reduce GHG emissions to 2000 leCelS;
• By 2020, reduce GHG emissions to 1990 lelels; and
• By 2050, reduce GHG emissions to 80 percent below 1990 IeC2Is.
Assembly Bill 32— California Global Warming Solutions Act
California Assembly Bill 32 EAB 324 the Global Warming Solutions Act of 2006, reDiires
CARB to establish a statewide GHG emissions cap for 2020 based on 1990 emission
le[Lls. AB 32 reEbired CARB to adopt and enforce programs and regulations that
identify and reEuire selected sectors or categories of emitters of GHGs to report and
lerify their statewide GHG emissions. In December 2007 CARB adopted 427 MT CO2e
as the statewide GHG emissions limit eDuil alent to the statewide Ie[BIs for 1990. This is
approximately 28 percent below forecasted 2020 lbusiness[asibsualoemissions of
596 MMT of CO2e, and about 10 percent below a[brage annual GHG emissions during
the period of 2002 through 2004 [GARB, 2009bo
CARB published the Expanded List of Early Action Measures To Reduce Greenhouse
Gas Emissions In California Recommended For Board Consideration in September
2007 [GARB, 200711 CARB adopted nine Early Action Measures for implementation,
including Ship Electrification at Ports, Reduction of High Global[Warming[Potential
Gases in Consumer Products, HeaEy[Duty Vehicle Greenhouse Gas Emission
Reduction [Aerodynamic Efficiencyq Reduction of Perfluorocarbons from
Semiconductor Manufacturing, Improlkd Landfill Gas Capture, Reduction of
Hydrofluorocarbonil34a from Doilt[Yourself Motor Vehicle Serdcing, Sulfur
Hexaflouride Reductions from the Non[Electric Sector, a Tire Inflation Program, and a
Low Carbon Fuel Standard.
As of January 1, 2012, the GHG emissions limits and reduction measures adopted in
2011 by CARB became enforceable. In designing emission reduction measures, CARB
must aim to minimile costs, maximile benefits, improle and modernilb California®
energy infrastructure, maintain electric system reliability, maximile additional
endronmental and economic colbenefits for California, and complement the staters
efforts to improCo air Duality.
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Climate Change Scoping Plan
In December 2006, CARB approCed the AB 32 Scoping Plan outlining the state®
strategy to achielb the 2020 GHG emissions limit [GARB, 2009b0 This Scoping Plan,
deDgloped by CARB in coordination with the Climate Action Team -CAT- proposes a
comprehensile set of actions designed to reduce olerall GHG emissions in California,
improle the enilronment, reduce dependence on oil, diDorsify Califomia[s energy
sources, saDq energy, create new jobs, and enhance public health.
As reDiired by AB 32, the Scoping Plan must be updated at least eDary fife years to
e1hluate the mix of AB 32 policies to ensure that California is on track to meet the
targets set out in the legislation. In October 2013, a draft Update to the initial Scoping
Plan was deCeloped by CARB in collaboration with the California Climate Action Team
tCCAT_ The draft Update builds upon the initial Scoping Plan with new strategies and
expanded measures, and identifies opportunities to leo3rage existing and new funds to
drile GHG emission reductions through strategic planning and targeted program
inl estments. The draft Update to the initial Scoping Plan was presented to CARB®
Board for discussion at its February 20, 2014 meeting. Subsenlently, the first update to
the AB 32 Scoping Plan was approled on May 22, 2014 by CARB.
As part of the proposed update to the Scoping Plan, the emissions reductions reDJired
to meet the 2020 statewide GHG emissions limit were further adjusted. The primary
reason for adjusting the 2020 statewide emissions limit was based on the fact that the
original Scoping Plan relied on the Intergo ernmental Panel on Climate Changers
[tPCCo1996 Second Assessment Report ESARoto assign the global warming potentials
ECWPsoof greenhouse gases. Recently, in accordance the United Nations Framework
ConEention on Climate Change I UNFCCCq international climate agencies hale agreed
to begin using the scientifically updated GWP [clues in the IPCCEs Fourth Assessment
Report EAR4othat was released in 2007. Because CARB has begun to transition to the
use of the AR4 1000year GWPs in its climate change programs, CARB recalculated the
Scoping Plan is 1990 GHG emissions le[EI with the AR4 GWPs. As the recalculation
resulted in 431 MMTCO2e, the 2020 GHG emissions limit established in response to AB
32 is now slightly higher than the 427 MMTCO2e in the initial Scoping Plan. Considering
that the proposed update also adjusted the 2020 BAU forecast of GHG emissions to
509 MMTCO2e, a 15 percent reduction below the estimated BAU Ie0als was determined
to be necessary to return to 1990 IeDals by 2020 LCARB, 2014bLi
Executive Order S-1-07
Executi a Order S11107, which was signed by GoCernor SchwarCenegger in 2007,
proclaims that the transportation sector is the main source of GHG emissions in
California. It establishes a goal to reduce the carbon intensity of transportation fuels
sold in California by at least 10 percent by 2020. As a result of this order, CARB
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approll9d a proposed regulation to implement the low carbon fuel standard ILCFSDon
April 23, 2009, which will reduce GHG emissions from the transportation sector in
California by about 16 MMT in 2020. The LCFS is designed to reduce California®
dependence on petroleum, create a lasting market for clean transportation technology,
and stimulate the production and use of alternatiEP, low[Carbon fuels in California. The
LCFS is designed to prodde a durable framework that uses market mechanisms to spur
the steady introduction of lower carbon fuels. The framework establishes performance
standards that fuel producers and importers must meet each year beginning in 2011.
Senate Bill 375
SB 375, which establishes mechanisms for the deCelopment of regional targets for
reducing passenger Cehicle greenhouse gas emissions, was adopted by the State on
September 30, 2008. On September 23, 2010, California ARB adopted the Cehicular
greenhouse gas emissions reduction targets that had been deleloped in consultation
with the metropolitan planning organisations EMPOsq the targets rewire a 7 to
8 percent reduction by 2020 and between 13 to 16 percent reduction by 2035 for each
MPO. SB 375 recogniCes the importance of achiedng significant greenhouse gas
reductions by working with cities and counties to change land use patterns and improlb
transportation alternatiCes. Through the SB 375 process, MPOs, such as the Southern
California Council of GoEl3mments ISCAGEWill work with local jurisdictions in the
deCelopment of sustainable communities strategies E$CSOdesigned to integrate
deliglopment patterns and the transportation network in a way that reduces greenhouse
gas emissions while meeting housing needs and other regional planning objectiDes.
SCAGEs reduction target for per capita lehicular emissions is 8 percent by 2020 and
13 percent by 2035 [GARB 20100 The MPOs will prepare their first SCS according to
their respect![13 regional transportation plan ERTPoupdate schedule with the SCAG
RTP/SCS adopted on April 4, 2012.
Senate Bill 97
Senate Bill ISBD97, enacted in August 2007, reEuired the Office of Planning and
Research EOPRElto deEElop guidelines for the mitigation of GHG emissions, or the
effects related to releases of GHG emissions. On April 13, 2009, the OPR submitted
proposed amendments to the Natural Resources Agency in accordance with SB 97
regarding analysis and mitigation of GHG emissions. As directed by SB 97, the Natural
Resources Agency adopted Amendments to the CEQA Guidelines for greenhouse gas
emissions on December 30, 2009. On February 16, 2010, the Office of Administrable
Law approCed the Amendments, and filed them with the Secretary of State for inclusion
in the California Code of Regulations. The Amendments became effectilb on March 18,
2010.
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California Green Building Standard Code
In early 2013 the California Building Standards Commission adopted the 2013 California
Building Standards Code that also included the latest 2013 CALGreen Code, which
became effectile on Canuary 1, 2014. The mandatory prodsions of the code are
anticipated to reduce 3 MMT of GHG emissions by 2020, reduce water use by 20
percent or more, and dilert 50 percent of construction waste from landfills. The 2013
California Energy Code [Title 24, Part 6Q which is also part of the CALGreen Code [Title
24, Part 11, Chapter 5.2Q became effectile on fly 1, 2014.
Regional
South Coast Air Quality Management District(SCAQMD)
As a method for determining significance under CEQA, SCAQMD deleloped a draft
tiered flowchart in 2008 for determining significance thresholds for GHGs for industrial
projects where SCAQMD is acting as the lead agency. In December 2008, SCAQMD
adopted a 10,000 MTCO2e/year for industrial facilities, but only with respect to projects
where SCAQMD is the lead agency. SCAQMD has not adopted a threshold for
residential or commercial projects at the time of this writing.
The SCAQMD flowchart uses a tiered approach in which a proposed project is deemed to
hale a less than significant impact related to GHG emissions when any of the following
conditions are met:
• GHG emissions are within GHG budgets in an approlled regional plan;
• Incremental increases in GHG emissions due to the project are below the defined
Significance Screening Lelbls, or Mitigated to Less than the Significance
Screening Lelbl;
• Performance standards are met by incorporating project design features and/or
implementing emission reduction measures; and
• Carbon offsets are made to achiele target significance screening Ielel.
Project Impacts
A. Would the project generate GHG emissions, either directly or indirectly, that
may have a significant impact on the environment?
Less than Significant Impact: The proposed project would generate GHG emissions
from a lariety of sources. First, GHG emissions would be generated during construction
of the proposed project. Once fully operational, the operations would generate GHG
emissions from direct sources such as natural gas consumption and indirect sources
such as electrical and water consumption, solid waste and wastewater generation, and
mobile sources from the one new employee.
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Construction Emissions
Construction related GHG emissions for the proposed project were estimated using the
same assumptions as the air _uality analysis. Total estimated construction Telated GHG
emissions for the proposed project are shown in Table 12. As shown, the proposed
projects total estimated unmitigated GHG emissions during construction would be
approximately 908 MTCO2e. This would ellual to approximately 30 MTCOze per year
after amortil ation Door 30 years per SCAQMD methodology.
Table 12: Estimated Total Construction Related GHG Emissions
Emission Source CO2 CH4 Estimated CO2e
Emissions
Unmitigated Construction Emissions
1 A 543.13 0.03
113 47.71 0.01
1C 118.06 0.00
ID 97.91 0.03
1 E 98.14 0.03
Total 904.94 2.60 907.54 mATo
Annual Construction [Anortiled 30.25(MT/yr)
oDgr 30 years?
NOTES: COiencerbon dioxide eAi-alert;MT rhrebic tons;MT/yr n metric Ions par year.
1 Total Emissions lake into account the global wmming potendal of CH4 wfiich is 25.Therefore the total CH4 emissions will not eNal Me
sum of the Ind1dual phase emissions as shown In the table.
Operational Emissions
The estimated operational GHG emissions resulting from proposed project are shown in
Table 13. Additionally, in accordance with SCAQi recommendation, the project6
amortiCed construction Telated GHG emissions from Table 12 are added to the
operational emissions estimate in order to determine the proposed project6 total annual
GHG emissions. As shown in Table 13, the proposed proji total net annual GHG
emissions would be approximately 39.97 MTCO2e per, which would not exceed
SCAQi proposed screening lelel of 3,000 MTCO2e per year 2020 threshold or the
1,800 MTCO2e per year 2030 threshold. Therefore, the net increase in GHG emissions
resulting from proposed project implementation would be less than significant.
Table 13: Estimated Construction and Operational Related GHG Emissions.
Emission Source Estimated Emissions CO2e(MT/yr)
Construction
Annual Mitigated Construction 30.257
[AmortlEad over 30 years❑
Project Operations
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Area Sources 0.00
Energy Consumption 3.98
Mobile Sources 4.22
Solid Waste 0.35
Water Consumption 1.174
Total(Operational Emissions) 9.72
Total Net Increase in Emissions 39.97
Greater than 3,000 MTCO2e per year[] No
Greater than 1,800 MTCO2e per year[] No
NOTES: CO.eorerMn dioxide eCuirelenq Mr/yr0 W.tons per year;CCperrart.
Source:ESA 2016
B. Would the project be in conflict with an applicable plan, policy or regulation
adopted for the purpose of reducing the emissions of greenhouse gases?
Less than Significant Impact: As discussed below, the proposed project would be consistent
with the CARB Scoping Plan, E01B130115, SB 375 and with the City of Huntington Beach
Energy Action Plan. No mitigation measures are reiyired.
Consistency with AB 32
As discussed under Impact GHG11 abole, the proposed project would not result in
annual GHG emissions exceeding the SCAQMD® 3,000 MTCO2e threshold which was
designed to help the region attain the goals of AB 32. Therefore, the proposed project
would be consistent with the goals of AB 32.
Consistency with EO B-30-15
As discussed under Impact GHG11 abo�e, the proposed project would not result in
annual GHG emissions exceeding 1,800 MTCO2e, or the brightline threshold adjusted
to reduce emissions to 40 percent below 1990 le[Jals by 2030. Therefore, the proposed
project would be consistent with the goals of E0113130115.
Consistency with City of Huntington Beach Energy Action Plan
The City of Huntington Beach Energy Action Plan addresses GHG reductions through
2020, consistent with AB 3219 goal of reducing GHG emissions to 1990 IeDals. As
demonstrated under GHG31 aboCe, the proposed project would not exceed the
SCAQMDIR 3,000 MT brightline threshold deCeloped to help the region attain 1990
GHG emission IeD31s by 2020. Therefore, the proposed project would not interfere with
the City of Huntington Beach Energy Action Plan as the project would not excessilely
increase GHG emissions within the City.
Consistency with SB 375
The key goal of the Sustainable Communities Standard [SCSois to achie[3 GHG
emission reduction targets through integrated land use and transportation strategies.
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The focus of these reductions is on transportation and land use strategies that influence
lehicle traiel. The proposed project would not increase lbhicle traffic within the City or
the region. Therefore, the proposed project would not conflict with the implementation of
SB 375.
4.8 Hazards/Hazardous Materials
Existing Setting
Exposure Hazardous Materials
Title 22 of the California Code of Regulations ICCRQ DiUsion 4.5, Chapter 11, Article 3
classifies halordous materials into the following four categories based on their
properties: toxic Pauses human health effectsq ignitable [has the ability to bumq
corroslEb Pauses selere burns or damage to materialsq and reactile Pauses
explosions or generates toxic gases[] Hazardous materials hale been and are
commonly used in commercial, agricultural and industrial applications as well as in
residential areas to a limited extent. Halardous wastes are halardous materials that no
longer hale practical use, such as substances that hale been discarded, discharged,
spilled, contaminated, or are being stored prior to proper disposal. The health impacts of
halardous materials exposure are based on the frelluency of exposure, the exposure
pathway, and indiDdual susceptibility. The proposed project would be constructed and
operated on the OCSD Plant No. 2 Site. Presently, Plant No. 2 in[bl[Es the handling
and storage of limited amounts halardous materials as part of the treatment system
processes and maintenance actiDties.
Fire Hazard
According to the City of Huntington Beach General Plan the study area is not located in
a high fire haLard lone.
Contaminated Soils
Regulatory databases prodded by federal, State, and local agencies proilde
information of past and present usage, storage and disposal of halardous materials. A
database search of hallardous materials sites was performed to identify potential
contaminated sites in the study area using the online State Water Resources Control
Board l$WRCBDGeoTracker Database and Department of Toxic Substances Control
IDTSCDEndroStor Database. The only reported hazardous site identified on OCSD
Plant No. 2 Site was two closed leaking underground storage tanks. Both sites were
determined to not pose significant risks to human health or the endronment.
Airport Hazards
The Airport Land Use Commission IALUCDof Orange County assists local agencies to
ensure that here are no direct conflicts with land uses, noise or other issues that will
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impact the functionality and safety of airport and heliport operations. The ALUC re[uires
that local jurisdictions general plans and [bning ordinances are consistent with Airport
En[rons Land Use Plans [AELUPISQ which contain noise contours, restrictions for
types of construction and building heights in na[gable air space, as well as
re Duirements impacting the establishment or construction of sensiti[a uses within close
proximity to airports. There are no prilate airport facilities within the [cinity of the study
area. The closest public airport is Cohn Wayne Airport located approximately 5 miles
from the study area.
State Emergency Response Act
The State Emergency Response Act reDuires local jurisdictions establish a Standardilb
Emergency Management System Multi IaCard Functional Plan. Accordingly, the Office
of Emergency Serdces, in coordination with all interested State and local agencies,
jointly establish a standardised emergency management system for use by all
emergency response agencies.
A. Would the project create a significant hazard to the public or the environment
through the routine transport, use or disposal of hazardous materials?
Less than Significant Impact with Mitigation: The OCSD Plant No. 2 Site currently
in[blCes the handling and storage of limited amounts hazardous materials as part of the
treatment system processes and maintenance acti[ties. The implementation of the
proposed project would not substantially increase the handling and storage of
haDardous materials.
The construction operations associated with the proposed project would inmlie the
handling of incidental amounts of halardous materials, such as fuels and oil. The
proposed project would be retired to comply with local, state and federal laws and
regulations regarding the handling and storage of hazardous materials. Additionally,
during construction operations Best Management Practices would be implemented as
part of the implementation of the Storm Water Pollution Pre Cent Plan, that would include
hazardous material spill preCention and management practices. With the
implementation of Mitigation Measure HZ11 potential haDardous material safety impacts
would be less than significant.
Mitigation Measure
HZ-1: Any use of hazardous materials in[blCad with the proposed project must be
conducted in accordance with applicable federal, state and local regulations.
B. Would the project create a significant hazard to the public or environment
through reasonably foreseeable upset and accident conditions involving the
release of hazardous materials into the environment?
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Less than Significant Impact with Mitigation: During construction, limited Dlantities
of halardous materials would be reD/ired to operate eDlipment and Cehicles. To a[bid
the release hallgrdous materials into the endronment, the handling, storage and
transportation of h"rdous materials would be done in compliance local, state and
federal laws and regulations. Additionally, OCSD Plant No. 2 Site has emergency
procedures and e0acuation plans to address the onsite storage and handling of
ha@rdous materials and correctiLb measures in the eCent of the inadCertent release of
ha@rdous materials into the endronment occurs. With the implementation of Mitigation
Measure HZC] the potential impact associated with the accidental release of hazardous
materials into the endronment would be less than significant.
Mitigation Measure
Mitigation Measure HZC] rezuired.
C. Would the project emit hazardous emissions or handle hazardous or acutely
hazardous materials, substance or waste within one-quarter mile of an existing or
proposed school.
Less than Significant Impact with Mitigation: The closest school to the OCSD Plant
2 wastewater treatment facility site would Eder Elementary school located
approximately o mile to the west. The longiteerm operation of the proposed project
would not emit hallardous emissions, or in[bl[o the handling of acutely hallardous
substances. During construction operations incidental amounts of hallgrdous materials
such as oils and fuels will be utiliCed. The handling of these substances would be in
compliance with local, state and federal laws and regulations regarding the
transportation, handling and storage of hazardous substances. The small amounts of
hai erdous materials that would be handled would not expose Eder Elementary School
to ha ardous emission impacts. With the implementation of Mitigation Measure HZd
potential ha[lard emission impacts would be less than significant.
Mitigation Measure
Mitigation Measure HZd rewired.
D. Would the project be located on a site which is included on a list of hazardous
material sites compiled pursuant to Government Code Section 65962.5 and as a
result, would create significant hazard to the public or the environment?
No Impact: There is no known hazardous material sites, pursuant to Gol:ernment Code
Section 65962.5 located on the OCSD Plant No. 2 Site that would create a significant
halard to the public.
E. For a project located within an airport land use plan or where such a plan has
not been adopted, within two miles of a public airport or public use airport, would
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the project the result in a safety hazard for people residing or working within the
project area?
Less than Significant Impact: The closest public airport facility to the project site is
Cohn Wayne Airport. According to the Airport EndronS Land Use Plan for Cohn Wayne
Airport, the OCSD Plant No. 2 Site is not located within a Clear Zone or Accident
Potential Zone. Therefore, implementation of the proposed project would not result in
airport related safety halards to people residing and/or working within the project area.
No mitigation measures are re aired.
F. For a project within the vicinity of a private airstrip, would the project result in
a safety hazard for people residing or working in the project area?
No Impact: There are no pri ate air strips within the Jcinity of the study area. Therefore
no potential safety ha Cards associated with the pri3ate air strip would occur. No
mitigation measures are re uired.
G. Would the project impair implementation of or physically interfere with an
adopted emergency response plan or emergency evacuation plan?
No Impact: The proposed project would be constructed and operated on the OCSD
Plant No. 2 Site. The construction actidties for the proposed project would not re Duire
any offsite road closures that could adCersely interfere with adopted emergency plans or
result in delays to emergency response times. No mitigation measures are reCuired.
H. Would the project expose people or structures to a significant risk of loss,
injury or death involving wild land fires, including where wildlands are adjacent to
urbanized areas or where residences are intermixed with wildlands?
No Impact: According to the City of Huntington Beach General Plan, the OCSD Plant
No. 2 Site is not subject to wild land fire risks. Additionally, the study area is not
adjacent to or intermixed with wild lands. Therefore, implementation of the proposed
project would not expose people or structures to wild land fire risks. No mitigation
measures are reouired.
4.9 Hydrology/WaterQuality
Existing Setting
The study area is located in the lower Santa Ana Ricer Watershed. The Santa Ana
Ricer Watershed is the largest watershed in coastal Southern California, consisting of
oCer 2,800 sillare miles and encompassing parts of RiCerside, San Bernardino and
Orange Counties. The primary surface water body within the study area is the Santa
Ana Ricer. The study area also oCerlies the Orange County Groundwater Basin.
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Santa Ana River
The Santa Ana Ri er is the most prominent hydrologic feature within the watershed.
The Santa Ana Ri or is oar 100 miles in length and has o-er 50 contributing tributaries.
The headwaters for the Santa Ana Ricer are in the San Bernardino Mountains to the
north. The rimer extends westerly through the Santa Ana Valley to the Prado Basin
where it is joined by seD3ral tributaries near Prado Dam. Downstream of Prado Dam,
the Santa Ana RI@r flows through the Santa Ana Mountain Canyon into Orange County
before discharging into the Pacific Ocean. The flows of the Santa Ana Ri[L-r consist of
storm flows and perennial flow [base flowDthat increases in the winter and decreases in
the summer. The base flow of the Santa Ana Ricer consists almost entirely of treated
wastewater discharged from upstream waste water treatment plants. The base flow of
the Santa Ana RiEbr is the primary source of water to recharge the Orange County
Groundwater Basin. Since 1933, OCWD has been dillarting water from the Santa Ana
Ricer for groundwater recharge. Surface water flows of the Santa Ana Ricer are
diDarted into a series of recharge basins to replenish the groundwater basin. Virtually all
of the base flow of the Santa Ana Ricer is captured by OCWD for groundwater recharge
and only a portion of the total storm flow of the Santa Ana Ricer is captured by OCWD
for groundwater recharge. The storm water that is not captured by OCWD is lost to the
ocean.
Orange County Groundwater Basin
The Orange County Groundwater Basin underlies central and northern Orange County
and is bordered by the Santa Ana Mountains to the east, the Pacific Ocean to the west,
the Newportilnglewood Fault to the southwest and Coyote Hills to the north. The basin
is contiguous and directly connected with the Central Basin of Los Angeles County to
the northwest. The basin reaches depths of olar 2,000 feet and is comprised of a
complex series of interconnected sand and graCel deposits. The aE]uifer is didded into
three sections, shallow, principal and deep. Most of the water in the basin is extracted
from the principal aouifer.
Flood Hazards
The OCSD Plant No. 2 Site is located in Flood Zone X. This area is protected from the
onelpercent[annual@hance flood by IeCee, dike, or other structures subject to possible
failure or oDartopping during larger floods.
Seiche, Tsunami and Mudflow Hazards
EarthDiakes can cause flooding due to tsunamis, seiches, or dam failure. Tsunamis are
a potential haCard at this site due to the close proximity of the coast and low election.
According to the City of Huntington Beach General Plan the OCSD Plant No. 2 Site is
classified as a Moderate Tsunami Runmlp Area. Additionally, the study area is located
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within the Prado Dam Inundation Area.
Seiches are earthDiakeOhduced wales in an enclosed or partially enclosed body of
water, which may produce flooding in local areas. The study area is not located near a
body of water that could experience seiches.
Water Quality Regulations
The following is discussion of Federal, State and local water resource programs that
would be applicable to the proposed project.
Federal
Clean Water Act
The objecti les of the Clean Water Act are to restore and maintain the chemical,
physical, and biological integrity of Waters of the United States. The Clean Water Act
establishes basic guidelines for regulating discharges of pollutants into the Waters of
the United States and reDuires states to adopt water Duality standards to protect health,
enhance the Duality of water resources and to deEelop plans and programs to
implement the Act. Below is a discussion of sections of the Clean Water Act that would
be rele[ant to the proposed project.
Clean Water Act Section 303 (d)
Under Section 303 ADof the Clean Water Act, the SWRCB is reDuired to deEelop a list
of impaired water bodies. Each RWQCB is responsible for establishing priority rankings
and deCeloping action plans, referred to as total maximum daily loads QMDI-soto
impro[B water Duality of water bodies included in the 303[ullolist.
Within Orange County, there are two reaches of the Santa Ana RICer. Reach 1 extends
from the Tidal prism to 17" Street in the City of Santa Ana and Reach 2 extends from
171h Street to Prado Dam. Presently, Santa Ana RIEer Reach 2 El7`h Street in Santa Ana
to Prado Damohas been listed as impairment for indicator bacteria. The TMDI_s for the
Santa Ana Riler Reach 2 is reDuired to be prepared before 2025. The Santa Ana RiEer
Reach 1 EPacific Ocean to 17th Street in Santa Anaois not listed as impaired.
State
Porter Cologne California Water Quality Control Act
The Porter Cologne Water Quality Act of 1967 reEluires the SWRCB and the nine
RWQCBs to adopt water Duality criteria for the protection and enhancement of Waters
of the State of California, including both surface waters and groundwater. The SWRCB
sets statewide policy and together with the RWQCB, implements state and federal
water Duality laws and regulations. Each of the nine regional boards adopts a Water
Quality Control Plan. The applicable Water Control Plan for the study area would be the
Santa Ana Region Basin Plan.
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Regional Water Quality Control Board
Beneficial Uses
The Santa Ana Region Basin Plan designates beneficial uses for waters in the Santa
Ana RiEbr watershed and proddes Dtantitative and narrative criteria for a range of
water LUality objectives to certain receidng water bodies in order to protect beneficial
uses. Table 14 describes the beneficial uses established in the Santa Ana Region Basin
Plan.
Table 14: Beneficial Uses
Abbreviation Beneficial Use
GWR Groundwater Recharge waters are used for natural or artificial recharge of groundwater
for purposes that may include, but are not limited to,future extraction, maintaining water
Dlality or halting saltwater intrusion into freshwater avuifers.
REC 1 Water Contact Recreation waters are used for recreational actidties involdng body
contact with water where ingestion of water is reasonably possible.These uses may
include, but are not limited to swimming,wading, water skiing, skin and scuba didng,
surfing,whitewater actidties,fishing and use of natural hot springs.
REC 2 Non[Contact Water Recreation waters are used for recreational actidties in lblEing
proximity to water, but not normally body contact with water where ingestion of water
would be reasonably possible. These uses may include, but are not limited to picnicking,
sunbathing, hiking, beachcombing, camping, boating,tide pool and marine life study,
hunting, sightseeing and aesthetic enjoyment n[conjunction with the abo-e actidties.
WARM Warm waters support warm water ecosystems that may include but are not limited to,
preservation and enhancement of aalatic habitats, vegetation, fish, and wildlife,
including in Cartebrates.
LWARM Limited Warm Freshwater Habitat waters support warm water ecosystems which are
sed:rely limited in dilbmity and abundance.
COLD Cold Freshwater habitat waters support Coldwater ecosystems.
BIOL Preservation of Biological Habitats of Special Significance waters support designated
areas of habitats.
WILD Wildlife Habitat waters support wildlife habitats that may include, but are not limited to the
preservation and enhancement of vegetation and prey species used by waterfowl and
other wildlife.
RARE Rare, Threatened or Endangered Species RAREvwaters support habitats necessary for
the surdEal and successful maintenance of plant or animal species designated under
state or federal law as rare,threatened or endangered.
MUN Municipal and Domestic Supply waters are used for community, military, municipal or
indi ddual water supply systems. These uses may include, but are not limited to drinking
water supply.
AGR Agricultural Supply waters are used for farming, horticulture or ranching. These uses
may include, but are not limited to irrigation,stock watering, and support of vegetation for
range grating.
IND Industrial SerdCe Supply waters are used for industrial actidties that do not depend
primarily on water Diality.These uses may include, but are not limited to mining,cooling
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water supply, hydraulic con[byance, gralbl washing,fire protection and oil well
depressurillition.
PROC Industrial Process Supply waters are used for industrial actidties that depend primarily
on water quality. These uses may include, but are not limited to, process water supply
and all uses of water related to product manufacture or food preparation.
NAV Nallgation waters are used for shipping, traEbl, or other transportation by pride,
commercial or military Cassels.
POW Hydropower Generation waters are used for hydroelectric power generation.
Comm Commercial and Sportlishing waters are used for commercial or recreational collection of
fish or other organisms
EST Uses of water that support estuarine ecosystems including, but not limited to
preserCation or enhancement of estuarine habitats, Cegetation,fish, shell fish or wildlife.
MAR Use of water that support marine ecosystems including, but not limited to, preserCation or
enhancement of marine habitats, -bgetalion such as kelp,fish, shell fish or wildlife.
SPWN Use of water that support high quality aquatic habitats suitable for reproduction and early
delblopment of fish.
SHELL Use of water that support habitats suitable for the collection of flterleeding shellfish for
human consumption, commercial or sports purposes.
As shown in Table 15, the Santa Ana Region Basin Plan establishes the following
beneficial uses for Reach 1 and Reach 2 of the Santa Ana RiCBr and for the Orange
County Groundwater Basin.
Table 15: Beneficial Uses Santa Ana River/Orange County Groundwater Basin
Reach 1 Reach 2 Orange County Groundwater Basin
Recreation 2 Agriculture Municipal Supply Waters
Recreation 1 Groundwater Recharge Agriculture Supply Waters
Recreation 1
Warm Water Habitat Recreation 2 Industrial Process Supply Waters
Wild Water Habitat Warm Water Habitat Industrial Serdce Supply Waters
Wild Water Habitat
Rare Waters
Water Quality Objectives
The Santa Ana Region Basin Plan establishes Water Quality Objectivbs for water
bodies within the study area to ensure the protection of Beneficial Uses. As shown in
Table 16 the Santa Ana Region Basin Plan establishes water quality objectiDas for
Reach 1 and Reach 2 of the Santa Ana Ricer and for the Orange County Groundwater
Basin.
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Table 16: Water Quality Objectives (mg/L)
Reach TDS HARD Na Cl TIN SO4 COD B
Santa Ana Ri[er Reach 1 NL NL NL NL NL NL NL NL
Santa Ana Ricer Reach 2 650d❑ NL NL NL NL NL NL NL
Orange County Groundwater Basin 580 NL NL NL NL NL NL NL
1nrn ira rear,aonog arxage,rvtnla uemd
Regional
OCSD Individual NPDES Permit
Presently, OCSD Plant No. 1 and Plant No. 2 hale a National Pollutant Discharge
Elimination System INPDESOIndiddual Permit for discharges of storm water associated
with their industrial actidties. The Indiddual Permit regulates actidties that may affect
storm water runoff Duality at certain types of industrial facilities, including publicly owned
wastewater treatment plants with design flows greater than 1.0 MGD, such as the
OCSD. Under the Indiddual Permit, facilities which discharge storm water to municipal
sanitary sewer systems instead of to waters of the United States are not reDuired to
obtain a General Constriction Permits or Industrial Permit prodding an onsite storm
water management plan is prepared and implement that contains BMPs to ensure that
construction site surface water runoff and long term surface water runoff is retained
onsite and incorporated into existing wastewater treatment processes.
Project Impacts
A. Would the project violate Regional Water Quality Control Board Water Quality
standards or waste discharge standards?
Recycled Water Requirements
No Impact: The proposed project would increase the amount wastewater flows to the
OCWD GWRS, where it would be ad Danced treated to drinking water standards. The
GWRS water would be used to replenish the Orange County Groundwater Basin. The
use of GWRS recycled water for groundwater replenishment is permitted under
RWQCB Order R[812004[0002 and subseDuent amendment R8C200810058. These two
permits specify water recycling reDuirements for the GWRS. The GWRS water
produced by the additional wastewater flows from OCSD Plant No. 2 Site would be
subject to the same permit conditions. Compliance with RWQCB permit re Duirements
would ensure that the use of GWRS water to replenish the Orange County Groundwater
Basin would not dolate RWQCB recycled water Duality standards.
Beneficial Uses
No Impact: All of the recycled water produced from the proposed project would be used
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to replenish the Orange County Groundwater Basin. The recycled water would be used
for Municipal Water Supply, Agriculture, Industrial and Industrial Processes beneficial
uses. The implementation of the proposed project would not be in conflict with beneficial
uses identified in the Santa Ana Region Basin Plan.
Water Quality Objectives
No Impact: The GWRS RWQCB permit reDuires that the GWRS recycled water meet
all water Luality objectiCes in the Santa Ana Region Basin Plan. Therefore, the use of
GWRS water to replenish the Orange County Groundwater Basin would not be in
conflict with water Duality objectiCes identified in the Santa Ana Region Basin Plan.
Section 303 (d) Impaired Water Bodies
No Impact: Reach 2 of the Santa Ana Ricer has been listed as impairment for indicator
bacteria. The wastewater flows from the OCSD Plant No. 2 Site would be highly treated
and disinfected for bacterial as part of the OCWD GWRS water treatment process. The
implementation of the proposed project would not introduce elelated lellgls of bacteria
and would not further impair any Section 303 Id listed water body.
B. Would the project substantially deplete groundwater supplies or interfere
substantially with groundwater recharge such that there would be a net deficit in
aquifer volume or a lowering of the local groundwater table level?
No Impact: The implementation of the proposed project would generate additional
wastewater supplies for OCWDs GWRS, which would produce an additional 68,000
acre feet of new water supplies to replenish the Orange County Groundwater Basin.
Current State of California® regulations regarding Groundwater Replenishment Reuse
Projects [GRRPsq such as OCWD GWRS, were made final by the California
Department of Public Health and formally adopted in 2014. Immediately thereafter, the
Drinking Water Didsion LDDWOresponsible for deCeloping the GRRP regulations was
transferred from CDPH to the State Water Resources Control Board [ WRCBD The
GRRP regulations reouire a minimum subsurface response retention time RRTDof two
months for Full AdCanced Treatment LFATLprojects, along with pathogen log-remoCal
standards that could re_uire additional subsurface residence time. These RRT
reluirements call for establishing both primary and secondary boundaries lhe., buffer
areasq the primary boundary is the traditional area in which the construction of new
drinking water wells would be restricted, while the secondary boundary is a nine of
potential controlled potable well construction, within which the operation of future new
well could extend otherwise materially affect the primary boundary, thereby rewiring
further study and potential mitigating actidties prior to potable well construction. The
water produced from the proposed project would be conll?yed to existing OCWD
groundwater replenishment basins or facilities at locations that would meet the traEbI
time reDuirement. The operation of the proposed project would increase groundwater
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 4-77
Section 4
supplies and would hale a beneficial impact on the Orange County Groundwater Basin.
No mitigation measures are rehired.
C. Would the project substantially alter the existing drainage pattern of the site or
area, including through the alteration of the course of a stream or river, in a
manner which would result in substantial erosion or siltation on or off site?
Less than Significant impact with Mitigation: ExcaDation and grading actidties
inCblCed with the proposed project would uncoCer soils and potentially expose them to
water and erosion impacts. Additionally construction eDlipment entering and exiting the
work areas could track sediment onto local streets and into local and regional drainage
systems. To minimiCe erosion impacts OCWD would file a Notice of Intent INOldwith
the State Water Resources Control Board and prepare and implement a Storm Water
Pollution PreCention Plan [SWPPPd The SWPPP would contain a map showing the
building site, onsite and adjacent roadways, storm water collection points and drainage
patterns across the site. The SWPPP would also prodde a list of Best Management
Practices 1BMP11that would be used to minimil a sediment and wind erosion impacts.
With implementation Mitigation Measure GEO12 potential erosion impacts would be less
than significant.
Mitigation Measure
Mitigation Measure GEOC2 relhired.
D. Would the project substantially alter the existing drainage pattern of the site or
area, including through the alteration of the course of a stream or river, or
substantially increase the rate or amount of surface runoff in a manner which
would result in flooding on or offsite?
Less than Significant impact: The proposed project would construct 1,200 share feet
of new imperdous surfaces and would replace 31,000 share feet of imperdous on the
OCSD Plant No. 2 Site. The amount of new imperdous surfaces would slightly increase
the existing rates of surface water runoff generated from the Plant No. 2 Site. The
additional surface water runoff generated from the proposed project would be
incorporated into onsite existing drainage systems and would not increase onsite flood
risks or offsite flood risks. To ensure that adelluate drainage facilities would be
alailable, OCWD would implement Mitigation Measure HWQ11, which rehires OCWD
to coordinate with OCSD on the capacity of existing drainage systems and the ability of
those drainage systems to accommodate surface water runoff generated by the
proposed project.
HWQ-1: OCWD will coordinate with OCSD on the capacity of existing drainage systems
to recellb surface water runoff generated from the proposed project and would
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Section 4
participate in any drainage improllaments rewired accommodate the surface water
runoff flows.
E. Would the project create or contribute runoff which would exceed the capacity
of existing or planned storm water drainage systems or provide substantial
additional sources of polluted runoff?
Less than Significant Impact: The construction and operation of the proposed project
would generate short®erm constructions related surface runoff impacts and longterm
surface runoff impacts.
Construction Surface Water Runoff Management
The proposed project construction actidties would disturb approximately 33,200 sn ft.
of area. To minimilb adCerse construction site surface water runoff water Duality
impacts, OCWD would file a Notice of Intent to disturb soils INOldand prepare and
implement a Storm Water Pollution Prellontion Plan 1SWPPP1J The SWPPP would also
provde a list of Best Management Practices IBMPdto retain construction site runoff
onsite for onsite treatment. With implementation Mitigation Measure GEO[2 potential
adilerse surface water runoff water duality impacts would be less than significant.
Long Term Surface Water Runoff Management
The GWRS Final Expansion Project would construct 1,200 sa ft. of new imperdous
surfaces and replace 31,000 so. ft. of existing imperdous surfaces at the OCSD Plant
No. 2 Site. The long term operation surface water runoff flows would be conleyed into
existing drainage systems and incorporated into existing onsite wastewater treatment
processes. By retaining and incorporating the surface water flows into the existing
treatment processes potential long storm surface water runoff water Duality impacts
would be less than significant. To ensure that adeDuate drainage facilities would be
a0ailable, OCWD would implement Mitigation Measure HWQL1, which reDuires OCWD
to coordinate with OCSD on the capacity of existing drainage systems and the ability of
those drainage systems to accommodate surface water runoff generated by the
proposed project.
Mitigation Measures
Mitigation Measure GEO[Y and HWQ[] reduired.
F. Would the project otherwise degrade water quality?
Less than Significant Impact with Mitigation: The use of GWRS recycled water for
ground water replenishment is permitted under RWQCB Order R[S[2004ID02 and
subselluent amendment R[200810058. These two permits specify water recycling
reduirements for the GWRS. Compliance with RWQCB permit retirements would
r Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEgA-Plus Federal Consultation Review 4-79
Section 4
ensure that use of GRWS recycled water for ground water replenishment would not
degrade groundwater water quality.
The long term operation of the proposed project would hale beneficial impacts on
groundwater supplies in Orange County and would support beneficial uses designated
for Reach 2 of the Santa Ana Ri--er and for the Orange County Groundwater Basin.
The project would not result in conflicts in achiedng water quality objectiEbs established
in the Santa Ana Region Basin Plan.
Both construction site surface water runoff and long term surface water runoffs flows
would be retained onsite and incorporated into existing wastewater treatment processes
to amid adlerse water quality impacts.
Mitigation Measures
Mitigation Measure GEOC2 and HWQ11 required.
G. Would the project place housing within a 100-year floodplain, as mapped on a
federal Flood Hazard Boundary or Flood insurance Rate map or other flood
hazard delineation map?
No Impact: The proposed project does not inmlCe construction of residential housing.
Therefore, implementation of the proposed project will not subject any housing to
potential flood risks. No mitigation measures are re uired.
H. Would the project place within a 100-year floodplain structures which impedes
or redirect flows?
No Impact: As shown in Figure 13 the study area is not located within a 1001year flood
plain. Flood improlements along the Santa Ana Riser haDe been designed to prodde
flood control protection up to a 190 year storm eEent. The proposed project would not
construct any structures or conduct any actidties within a 100 year flood area that would
impede or redirect flood flows.
I. Would the project expose people or structures to a significant risk of loss,
injury or death involving flooding, including, flooding as a result of the failure of a
levee or dam?
Less than Significant Impact: The OCSD Plant No. 2 Site is located downstream of
Prado Dam. Improlements implemented at Prado Dam and at SeCen Oaks Dam and
along the Santa Ana Rimer hale been designed to prodde flood control protection up to
a 190 year storm eCent. The proposed project would not inmlLb the construction of any
structures or inmlLJS any facilities that would adCersely impact the flood control capacity
or increase flood risks at Prado Dam or along the Santa Ana Ricer. Therefore, potential
impacts in regards to risk IeCee failure would be less than significant. No mitigation
measures are required.
? Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 4-80
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Figure 13
S
Section 4
J. Could the project site be inundated by a seiche, tsunami, or mudflow7
Less than Significant Impact: The OCSD Plant No. 2 Site is located in a Moderate
Tsunami RunLUp Area. The likelihood that a tsunami would be large enough to inundate
the site would be low and the potential impact for the study area to exposed tsunami
impacts would be less than significant.
The study area and surrounding area does not contain any slopes, hillsides or
mountains that pose the threat for mudflow impacts. Therefore, potential mudflow
impacts would be less than significant. No mitigation measures are reCuired.
4.10 Land Use/Planning
Existing Setting
Existing Land Uses
The OCSD No. 2 Plant Site is currently del-eloped with wastewater treatment facilities,
administratilb buildings, parking areas onsite roadways. Plant No. 2 Site is situated
within the urbanilbd endronment and surrounded by the Santa Ana Ricer to the east,
Brookhourst Street and residential uses to the west and north and the Talbert Marsh to
the south. The study area is predominantly build out.
Relevant Planning Programs
The following are rele[bnt planning programs that would apply to the proposed project.
City of Huntington Beach General Plan
The City of Huntington Beach General Plan designates the OCSD Plant No. 2 Site
Public. The Public designation allows go[brnmental administratile and related facilities,
such as public utilities, schools, public parking lots and infrastructure.
City of Huntington Beach General Plan Coastal Element
The OCSD Plant No. 2 Site is located within Coastal Zone and subject to the California
Coastal Act. The California Coastal Act is implemented by the City of Huntington Beach
General Plan Coastal Element. The Coastal Element includes a land use plan and
policies to guide land use decisions within the coastal Cone. The OCSD Plant No. 2
Site is located in Zone 5, which extends from Beach BouleCard to the Santa Ana RI@r.
The Coastal Element designates OCSD Plant No. 2 4G[Edison Plant. Permitted uses
include public uses and open space conser[btion. Any delblopment actidty occurring in
the Coastal Zone would be re uired to obtain a Coastal Delblopment Permit approlbd
by the City of Huntington Beach.
City of Huntington Beach Zoning Code
The portion of the OCSD Plant No. 2 Site where the proposed project would be
constructed is coned IG [Industrial GeneraloThe Industrial General [bring designation
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allows for full range of manufacturing, industrial processing, resource and energy
production, general serdces and distribution land uses and establishes a maximum
height restriction of 40 feet.
A. Would the project physically divide an established community?
Less than Significant Impact with Mitigation: The long term operation of the
proposed project would be compatible with existing uses on the OCSD Plant No. 2 Site.
All construction actidties would occur on Plant No. 2 and would not physically impact
any offsite existing residential communities, businesses or industries within the study
area. Potential long term land use impacts to established communities within the study
area would be less than significant. To minimiLb construction impacts to surrounding
land uses within the study area, OCWD would coordinate with the public on upcoming
construction actidties. With the implementation of Mitigation Measure 1-1.111 potential
construction impacts to existing land uses would be less than significant.
Mitigation Measure
LU-1: OCWD will prodde residents and business owners with notifications of upcoming
construction actidties.
B. Would the project be in conflict with any applicable land use plan, policy or
regulation of an agency with jurisdiction over the project adopted for the purpose
of avoiding or mitigating an environmental effect?
Less than Significant Impact with Mitigation: The City of Huntington Beach General
Plan land Use Element designates the OCSD Plant No. 2 Site Public. According to
General Plan public utilities are a permitted land use under the Public land use
category. The proposed flow eoualilation tank and pump station impro[Ements would
be consistent with the Public land use designation in that the proposed improEaments
would be an expansion of the existing public utility uses occurring on the OCSD Plant
No. 2 Site.
The City of Huntington Beach Coastal Element designates the OCSD Plant No. 2 Site
4G[Edison Plant and identifies public uses and open space conserEation as permitted
land uses, subject to approial of a Coastal Delalopment Permit. The proposed flow
eo lalilation tank and pump station improlaments would be consistent with the Coastal
Element in that the proposed impro�aments would be a continuation of existing public
uses occurring on the site. The proposed project with appro Dal of Coastal De[elopment
Permit would not be in conflict with the City of Huntington Beach General Plan Coastal
Element.
The northern portion of the OCSD Plant No. 2 Site where the flow ellualiiation tank and
pump station would be constructed is coned Industrial General. The Industrial General
inning designation allows for full range of manufacturing, industrial processing,
OOrange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 4-83
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resource and energy production land uses. The proposed flow en/aliiation tank and
pump station improDDments would be consistent with the Industrial General Zoning
District in that the proposed improDDments would be an expansion of the existing
industrial land uses occurring on the site. The Industrial General Zoning District
establishes a maximum height of 40 feet. The tallest structure proposed would be flow
eDualilation tank at a height of 30 feet. The proposed project would not be in conflict
with the City of Huntington Beach Zoning Code.
Mitigation Measure
LU-2: Prior to construction of the Flow EDualiDation Tank OCWD will obtain approlal of
Coastal DeCelopment Permit from the City of Huntington Beach.
C. Would the project be in conflict with any applicable habitat conservation plan
or natural community conservation plan?
No Impact: The OCSD Plant No. 2 Site is situated within an urban setting. There are no
habitat management plans or natural community conserCetion plans established on the
site. Therefore, implementation of the proposed project would not be in conflict with any
habitat conserlation plan or natural community conserlation plan.
4.11 Mineral Resources
Would the project result in the loss of availability of a known mineral resource
that would be of value to the region and the residents of the state?
No Impact: According to the City of Huntington Beach General Plan, the OCSD Plant
No. 2 Site is not identified has containing mineral resources of regional significance.
Additionally, the Plant No. 2 Site is currently not used for mineral extraction. Therefore,
no impacts on regional minerals or minerals of state importance would occur.
B. Would the project result in the loss of availability of a locally important mineral
resource recovery site delineated on a local general plan, specific plan or other
land use?
No Impact: According to the City of Huntington Beach General Plan, the OCSD Plant
No. 2 Site is not identified has containing mineral resources of regional significance.
Additionally, the Plant No. 2 Site is currently not used for mineral extraction. Therefore,
no impacts on regional minerals or minerals of regional importance would occur.
4.12 Noise
Existing Setting
Noise is defined as unwanted sound. Sound becomes unwanted when it creates a
nuisance that interferes with normal actidties, or when it causes physical harm and
adiarsely affects human health. The standard unit of measurement of the loudness of
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sound is the decibel ABo The lero point on the dB scale is based on the lowest sound
lelel that a healthy, unimpaired human ear can detect. Changes of 3 d6 or fewer are
only perceptible in laboratory endronments. An increase of 10 dB represents a 101Bold
increase in acoustic energy, while 20 dB is 100 times more intense, and 30 dB is 1,000
times more intense. Each 101dB increase in sound lelel is perceiled as approximately
a doubling of loudness.
Numerous methods hale been deleloped to measure sound o1br a period of time,
including: Elluilalent Sound Lelel dLeoQ Community Noise En/ilalent Lelel [CNELQ
Day/Night Alerage Sound Lelel [Ldeoand Maximum Noise elent 1 Lmaxo Noise lelel can
lery pending on the noise source and duration. Below is description of the units of
measure used in this analysis to describe the noise endronment.
• Le,Time lariations in noise exposure are typically expressed as a statistical
description of the sound pressure IeCeI that is exceeded oDar some fraction of a
gilen obserCation period [called L.00 For example, the noise IeLals exceeded on
10 percent of readings is called Lte, the median L50th percentile Oreading is called
Leo, etc.
• CNEL: Because community receptors are more sensitise to unwanted noise
intrusion during the eFening and at night, state law ren/ires that, for planning
purposes, an artificial dB increment penalty be added to ❑llet[Nme noise lelels in
a 241hour noise descriptor called CNEL.
• Ldn:Another commonly used method is the day/night aCerage lelel or Lde.
• Ldn is a measure of the 241hour alerage noise IsILI at a gilen location. It was
adopted by the U.S. EnUronmental Protection Agency IEPADfor deLBloping
criteria for the e0aluation of community noise exposure.
• Lmaz: The maximum noise lelbl recorded during a noise slant is typically
expressed as Lm..
Effects of Noise
Physical damage to human hearing begins at prolonged exposure to noise lelels higher
than 85 dBA. Extended periods of noise exposure abole 90 dBA could result in
permanent hearing damage. When the noise IelaI reaches 120 dBA, a ticking sensation
occurs in the human ear elen with short[term exposure. This Ie�eI of noise is called the
threshold of feeling. As the sound reaches 140 dBA, the tickling sensation is replaced
by the feeling of pain in the ear. This is called the threshold of pain. A sound IelbI of 190
dBA will rupture the eardrum and permanently the inner ear. Table 17 summari[Bs
typical noise sources, lelels, and responses.
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Table 17: Noise Levels and Human Response
Noise Source Noise Level dBA Response
Library 30 Very Mist
Refrigerator humming 40 Quiet
Quiet office 50 Quiet
Normal conEbmation 60 Intrusi e
Vacuum cleaner 70 Telephone use difficult
Freight train at 50 feet 80 Interferes with con Ebmation
Hea yi duty truck at 50 feet 90 Annoying
Eet takeoff at 2,000 feet 100 Very annoying; hearing damage at sustained
exposure IeEels
UnmuHled motorcycle 110 Maximum local effect; physical discomfort
Eat takeoff at 200 feet 120 Regular exposure o1br one minute risks
permanent hearing loss
Shotgun firing 130 Pain threshold
Carrier jet operation 140 Harmfully loud
Source:Me1011e C.Brand,aM R.Dale Belend.lB]0.
Ground Absorption
The sound drop off rate is highly dependent on the conditions of the land between the
noise source and recei0ar. To account for this grounduaffect attenuation CsbsorptionQ
two types of site conditions are commonly used in noise models, so%site and hardlite
conditions. Soft[site conditions account for the sound propagation loss oDar natural
surfaces such as normal earth and ground Eegetation. For point sources, a droplbff
rate of 7.5 dBA/for each doubling of distance from the point source is typically obserlbd
o1br soft ground with landscaping, as compared with a 6.0 dBA/for each doubling of
distance o er hard ground such as asphalt, concrete, stone and Eery hard packed earth
Noise Barrier Attenuation
For a noise barrier to work, it must be high enough and long enough to block the dew of
the noise source. A noise barrier is most effectIDD when placed close to the noise
source or receID3r. A noise barrier can achiel e a 5 dBA noise lell3l reduction when it is
tall enough to break the linelbfisight and greater heights increase the noise reduction.
When the noise barrier is a berm instead of a wall, the noise attenuation can be
increased by another 3 dBA.
Applicable Noise Standards
Federal Occupational Safety and Health Administration
The adilorse impact of noise was officially recogniEed by the federal goilomment in the
Noise Control Act of 1972. The most relemnt federal agency to the GWRS Final
Expansion Project would be Occupational Safety and Health Administration EOSHAQ
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which limits noise exposure of workers to 90 dB Leo or less oler eight hours or 105 dB
Leo or less oler one hour.
Local Noise Regulations
The local noise regulations that are applicable to the GWRS Final Expansion Project
would be the City of Huntington Beach Noise Ordinance.
City of Huntington Beach Noise Ordinance
Chapter 8.40 of the City of Huntington Beach Municipal Code contains the City® Noise
Ordinance. Table 18 identifies the exterior noise standards established in the City of
Huntington Beach Noise Ordinance.
Table 18: City of Huntington Beach Exterior Noise Standards
Noise Zone Noise Level Time Period
All Residential Properties 55 dBA 7:00 a.m.to 10:00 p.m.
50 dBA 10: 00 p.m. to 7:00 a.m.
All Professional Office/Public Institution Properties 55 dBA Anytime
All Commercial Properties Except Professional Office 60 dBA Anytime
All Industrial Properties 70 dBA Anytime
The abole allowed noise lelel standards shall not be exceeded:
1. For a cumulatile period of more than 30 minutes in any hour;
2. Plus file db[Aofor a cumulatile period of more than 15 minutes in any hour;
3. Plus 10 db[Aofor a cumulatile period of more than file minutes in any hour;
4. Plus 15 dbEADfor a cure i[E period of more than one minute in any hour; or
5. Plus 20 db[Aofor any period of time.
6. In the Slant the ambient noise le[BI exceeds any of the first four noise limit
categories aboDa, the curl period applicable to said category shall be
increased to reflect said ambient noise leDal. In the eDant the ambient noise leDal
exceeds the fifth noise limit category, the maximum allowable noise lelel under
said category shall be increased to reflect the maximum ambient noise lelel.
E237917/79❑
Table 19 identifies the interior noise standards established in the City of Huntington
Beach.
Table 19: City of Huntington Beach Interior Noise Standards
Noise Zone Noise Level Time Period
All Residential Properties 55 dBA 7:00 a.m.to 10:00 p.m.
45 dBA 1 10: 00 p.m.to 7:00 a.m.
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All Professional Office/Public Institution 55 dBA Anytime
Properties
All Commercial Properties Except 55 dBA Anytime
Professional Office
All Industrial Properties 55 dBA Anytime
The abo[o allowed noise le[oI standards shall not be exceeded:
1. The noise standard for a cumulati[o period of more than fi[o minutes in any hour:
2. The noise standards plus fiEa db[AOfor a cumulati[e period of more than one
minute in any hour.
3. The noise standard plus 10 db[Aofor any period of time.
4. In the eCent the ambient noise IeCel exceeds either of the first two noise limit
categories abolb, the cumulatilb period applicable to said category shall be
increased to reflect said ambient noise IeDal. In the eCent the ambient noise leCel
exceeds the third noise IeCel, the maximum allowable noise IeD31 under said
category shall be increased to reflect the maximum ambient noise IeDal.
5. Each of the noise limits specified abole shall be reduced by fiEla dbEAOfor impact
or predominant tone noises, or for noises consisting of speech or music.
6. In the e[ont that the noise source and the affected property are within different
noise [ones, the noise standards of the affected property shall apply. E237917/79❑
Special Provisions
Construction Noise
According to Section 8.40.090[dDof the City of Huntington Beach Noise Ordinance,
noise sources associated with construction, repair, remodeling, or grading of any real
property are exempt from the City Noise Ordinance, prodded said actidties do not take
place between the hours of 8:00 P.M. and 7:00 A.M. on weekdays or Saturdays, or at
any time on Sunday or a federal holiday.
Schools, Hospitals, Churches
It is unlawful for any person to create any noise which causes the noise le[oI at any
school, hospital or church while the same is in use to exceed the noise limits as
specified for the assigned noise [one in which the school, hospital or church is located,
or which noise lel of unreasonably interferes with the use of such institutions or which
unreasonably disturbs or annoys patients in the hospital, prodded conspicuous signs
are displayed in three separate locations within oneitenth of a mile of the institution
indicating the presence of a school, church or hospital.
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Existing Noise Levels
The OCSD Plant No. 2 Site is bordered by the Santa Ana RI@r to the east, the Talbert
Marsh and Pacific Coast Highway to the south, and Brookhurst Street to the west. The
study area ambient noise endronment is predominately influenced traffic noise along
Brookhurst Street. Onsite noise[generating sources within OCSD Plant No. 2 include;
engine/motor noise, mechanical esuipment lincluding large fans and trunkline
scrubbersq paging systems and truck traffic entering and leafing the plant.
The closest sensible receptors are single family residential land uses located west of
Brookhurst Street and multiplelfamily residential to the north of the Plant No. 2 property.
An existing block wall prodded along Plant No. 2 helps to reduce noise leLbls within the
study area. Ambient noise measurements were conducted at two locations,
representing the nearby land uses in the dcinity of the project site to establish
conserlbtiCe ambient noise IeCels. The measurement locations along with existing
delblopment and the proposed construction acti-ities are shown on Figure 4. Long®erm
124[hourOmeasurements were conducted at locations R1 and R2. Ambient sound
measurements were conducted on Wednesday, [lily 13, 2016, to characteri[IB the
existing noise endronment in the project dcinity.
• Measurement Location R1: represents the existing noise endronment of single❑
family residential uses west of the project site along Brookhurst Street.
• Measurement Location R2: represents the existing noise endronment of multi El
family residential uses north of the project site along Brookhurst Street.
As shown in Table 20, the existing ambient daytime noise leligls ranged from 66 dBA to
69 dBA, Lei, at R1 and from 68 dBA to 70 dBA, Leo at R2. The existing ambient
nighttime noise lelbis ranged from 56 dBA to 67 dBA, Leo at R1 and from 58 dBA to 66
dBA, Le,at R2.
Table 20: Existing Ambient Noise Levels
Existing Land Daytime Daytime Nighttime Nighttime 24-Hour
Use (7 A.M.to 10 P.M.) Average (10 P.m.to 7 A.M.) Average Average,
Hourly L Hourly Hourly L Hourly L. CNEL
R1 -. Singlemamily 66069 67 5667 61 69
Residential
R2 ❑ MulOmamily 68170 69 5"6 62 71
Residential
Project Impacts
A. Would the project expose persons to or generation of noise levels in excess of
standards established in the local general plan or noise ordinance, or applicable
standards of other agencies?
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Operational Noise Impacts
Less than Significant Impact: Once the Water Production Enhancement Project is
operational, noise IeCeIS generated from the study area would mainly occur from the
pump station. The flow eDjaliCation tank would haDa a 41pump, approximately 50011
linear feet of 361nch diameter connection piping with a meter Gault 115I11t x 201 t x 10I11
deep[Iconnected to the operations of the tank. The pump station would be housed in a
301 t x 40I11 x 201A block wall building.
The analysis of the pump station Ifelated noise is based upon reference noise
measurement conducted on [lily 15, 2016 at a pump station located in the OCWD
facility at 18700 Ward Street, Fountain Valley, CA. Pump station2elated noise IeCels
were measured inside of the pump station and outside of the pump station at 5 feet from
a IouEar. Noise Ielbl of 80 dBA was measured inside of the pump station and noise
IeCel of 66 dBA was measured at 5 feet from the IouCer outside of the pump station. The
pump station house with IouCers would prollde approximately 14 dBA noise reduction.
The nearest single[Bamily residential uses west of the study area would be located
approximately 460 feet from the proposed pump station. Based on a noise leLAel source
strength of 66 dBA at a reference distance of 5 feet, and accounting for distance
attenuation Lfninimum 39 dBA insertion lossDand barrier insertion loss by block walls
Tninimum 5 dBA insertion lossq pump station related noise would be reduced to 22 dBA
at the nearest noise sensitilb uses., well below the City of Huntington Beach Daytime
Noise Standard of 55 dBa and Nighttime noise Standard of 50 dBA. Operation of the
Water Production Enhancement Project would not expose persons to, or generate noise
Ie[Lls in excess of standards established in the local general plan or noise ordinance, or
applicable standards of other agencies, Therefore, operational noise impacts would be
less than significant. No mitigation measures are rentired.
Construction Noise Impacts
Less Than Significant Impact: Construction of the proposed project would renlire the
use of heaDy elluipment during the demolition, grading, and excalation actilities at the
project site. During each stage of del:alopment, there would be a different mix of
elluipment. As such, construction actidty noise lelials at and near the project site would
fluctuate depending on the particular type, number, and duration of use of the 11arious
pieces of construction eDuipment. As shown in Table 21, Indiddual pieces of
construction elluipment anticipated during construction could produce maximum noise
lelials of 60 dBA to 83 dBA Lmax at a reference distance of 50 feet from the noise
source. These maximum noise IeCels would occur when e0uipment is operating at full
power.
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Table 21: Construction Equipment Noise levels
Construction Equipment Noise Level at 50 Feet Estimated
(dBA, Lmax) Usage Factor,
°k
Backhoe 69 50
Bull Dollar 82 40
Co m actor, 83 20
Concrete Tmck 75 25
Crane 81 40
Dump Truck 76 20
Drill Rig Truck 76 50
Excalalor 81 40
Forklift' 60 50
Man Lift 68 25
Water Truck 80 10
During construction, the nearest and most notable offsite sensitise receptors that would
be exposed to increased noise le[DIS would be the existing singlelfamily residential
uses located in proximity to the project site. Specifically, the nearest offsite noise
sensitive receptors include the following:
• Single[Bamily residences along Brookhurst Street approximately 260 feet west of
the project site; and
• Multi[family residences along Brookhurst Street approximately 800 feet north of
the project site.
OCer the course of a construction day, the highest noise le[Bls would be generated
when multiple pieces of construction eDuipment are being operated concurrently. The
projects estimated construction noise levels were calculated for a scenario in which all
construction eDuipment was assumed to be operating simultaneously and located at the
construction area nearest to the affected receptors to present a conserCatiCe impact
analysis. The estimated noise lelals at the offsite sensiti a receptors were calculated
using the FHWA[s RCNM, and were based on the concurrent operation of 6 pieces of
elluipment Gle., front end loader, backhoe, dollar, haul truck, drill rig truck, etc.Dwhich is
considered a worst[base elaluation. Table 22 shows the estimated construction noise
levels that would occur at the nearest offsite sensitive uses during a peak day of
construction actidty at the study area.
Table 22: Estimated Construction Noise Levels (dBa)
Existing Land Use Daytime Low Estimated Noise Level Noise Level
Ambient Construction Increase Increase With
Noise level Noise level Without Considering
Considering Shielding (1)
Shielding dBA
SingleTamily Residential 66 65 -1 B
West of Site, Along
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Section 4
Brookhurst Street
Multi[family Residential 68 56 112 117
North of Site Along
Brookumt Street
MV eoeptors are padially shielded from the mnsuvdon site by existing walls,representing a 5 des rttludw In holes Ie215.
As shown in Table 22, the peak day construction noise leuals experienced by the offsite
sensitiLb receptors would range from 56 dBA, Leo at the multilfamily residential uses
located north of the project site to 65 dBA, Leo at the singlelHamily residential uses
located west of the study area. The construction actidty would only occur during the
day. Therefore, the City of Huntington Beach Day Time Noise Standard would be the
releCant noise standard for the construction actidties. The estimated construction noise
le[els would exceed the City of Huntington Beach Day Time Exterior Noise Standard of
55 dBa. The City of Hunting Beach Noise Ordinance exempts construction noise that
occurs between 7:00 A.M. and 8:00 P.M. Monday through Saturday. The construction
operations for the proposed project would occur during the hours of the day when the
construction noise would be exempt under the City of Huntington Beach Noise
Ordinance and therefore the construction noise would not expose persons to or
generate noise IeCels in excess of local noise standards. No mitigation measures are
reouired.
B. Would the project result in a permanent increase in ambient noise levels in the
project vicinity above levels existing without the project?
Less Than Significant Impact: Because of the proximity of the existing offsite
sensiti0a uses to the study area, the projectls operation actidties would not expose
these sensiti0a receptors to increased exterior noise or interior noise lelbls. Based on
the measured noise leels at the nearest offsite sensitiCe receptors to the project site, it
was determined that the pump station elated noise IeCels would not exceed the
nighttime aCerage ambient noise lellbls at the offsite sensitlEb receptors. As such, there
would not be a substantial permanent increase in ambient noise IeCels in the study area
dcinity abo[e IS els existing without the project Potential long term noise impacts would
be less than significant. No mitigation measures are rewired.
C. Would the project result in a substantial temporary or periodic increase in
ambient noise levels in the project vicinity above levels existing without the
project?
Less than Significant Impact: The state CECA Guidelines do not define the lelals at
which increases in ambient noise Ielels are considered [substantial temporary.[]
Howeler, with respect to noise, a change in noise levels of 3 dBA is considered to be a
barely perceiDable difference, while a change in noise le[Bls of 5 dBA is considered to
be a readily perceiDable difference. A change in noise IeCels of 10 dBA is considered to
1*1 Orange County Water District Water Production Enhancement Project
SJ Draft Initial Study/Mitigated Negative Declaration&CEgA-Plus Federal Consultation Review 4A2
Section 4
be doubling of the parcelled loudness. Thus, for the purpose of conducting a
conseriatile analysis, an increase in the noise endronment of 5 dBA or greater at an
off[site sensiti[e receptor during proposed construction actidties would be considered a
significant noise impact with regards to a temporary substantial increase in ambient
noise leials. Based on the measured noise lelals at the nearest offsite sensible
receptors to the work area, shown in Table 22, it was determined that construction noise
levels would not exceed the ambient noise le�els by 5 dBA at the offsite sensitiEb
receptors. Because of existing eleCated noise IeCels occurring within the study area, it
would unlikely that construction noise would be heard by sensiti0a receptors. Potential
short®erm noise impacts from construction actiUties would be less than significant. No
mitigation measures are reDiired.
Off-Site Construction Traffic Noise
DeliCBry truck and haul truck trips would occur throughout the construction period.
Trucks traCeling to and from the work site would be reDuired to tralbl along Brookhurst
Street. An estimated maximum of approximately 10 workerl§ [chicle trips, 1 Candor
truck trip, and 32 haul truck trips would occur per day. The projects truck trips would
generate noise levels of approximately 50 dBA, CNEL at 25 feet distance along
Brookhurst Street. As shown in Table 22, the existing noise leials along Brookhurst
Street ranged from 66 dBA to 68 dBA, CNEL. Noise leials of 50 dBA, CNEL generated
by construction[related traffic would not increase the ambient noise lelels along
Brookhurst Street. Therefore, off[site construction traffic noise impacts would be less
than significant. No mitigation measures are reluired.
D. For a project located within an airport land use plan or where such a plan has
not been adopted, within two miles of a public airport or public use airport, would
the project expose people residing or working in the project area to excessive
noise levels?
Less than Significant Impact: The closest airport to the study area would be Lohn
Wayne Airport located approximately seDan miles from the study area. According to the
Cohn Wayne Airport Land Use Compatibility Plan the study area would not be impacted
by aircraft noise IeCels that would exceed local, state or federal standards. In addition,
the proposed project does not introduce new sensitID3 receptors to the study area.
Based on the fact the site is not impacted with eleCated IeCels of aircraft noise and the
project would not introduce new sensiti Fe receptors to the project area, there will be no
impacts from airport noise associated with the project. No mitigation measures are
renlired.
E. For a project within the vicinity of a private airstrip, would the project expose
people residing or working in the project area to excessive noise levels?
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No Impact: There are no prilate airstrips within the study area. Therefore, the study
area would not be adhrsely impacted from aircraft noise from a prilate air strip.
F. Would the project expose persons to or generation of excessive groundborne
vibration or groundborne noise levels?
Vibration Standards
Less than Significant Impact: California Administrate Code 15000, Title 14 rehires that
all state and local agencies implement the California Endronmental Quality Act [CEQA❑
Guideline, which rehires an exposure analysis of persons to excessil:s groundborne
dbration impacts. Common sources of dbration impacts from construction actilllties
include; blasting, pile[dridng and operation of heaEy earth[modng ehipment. Sensltlh'
receptors for dbration include structures [especially older masonry structures, people
and dbration sensible ehipment.
There are no state dbration standards that would apply to the proposed project.
Hower, the California Department of Transportation® [CaltransdTranspottation and
Construction Vibration Guidance Manual proddes guidelines that can be used as
screening tools for assessing the potential for ad[erse dbration effects related to
structural damage and human perception. The manual is meant to prodde practical
guidance to Caltrans engineers, planners, and consultants who must address dbration
issues associated with the construction, operation, and maintenance of Caltrans
projects. The dbration criteria established by Caltrans for assessing structural damage
and human perception are shown in Table 23 and Table 24.
Table 23: Caltrans Vibration Damage Potential Threshold Criteria
Maximum PPV
Structure Transit Source Continuous Sources
Extremely fragile historic buildings, ruins, 0.12 0.08
ancient monuments
Fragile buildings 0.2 0.1
Historic and some old buildings 0.5 0.25
Older residential structures 0.5 0.3
New residential structures 1.0 0.5
Modern industrial/commercial buildings 2.0 0.5
Source:Celtrens and Federal TransiUwtliodty
Table 24: Caltrans Vibration Annoyance Potential Criteria Maximum PPV
StructurelCondition Transit Source Continuous Sources
Barely perceptible 0.04 0.01
Distinctly perceptible 0.25 0.04
Strongly perceptible 0.9 0.10
Salem 2.0 0.4
Soup:Caltrans and Federal Tramit Mftnly
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Section 4
Existing Groundborne Vibration Levels
Aside from periodic construction work that could occur throughout the City, other
sources of groundborne ❑bration within the study area ❑cinity may include heaDjlduty
Cehicular traCel lb.g., refuse trucks, deliDary trucks, etc.i on local roadways. Truck traffic
at a distance of 50 feet typically generate groundborne (bration Celocity Ielbls of
approximately 63 VdB ®pproximately 0.006 in/sec PPVQ and these IeCels could reach
72 VdB approximately 0.016 in/sec PPVEWhere trucks pass oCer irregularities in the
road surface.7
Construction Vibration
Construction actidties would haEb the potential to generate low le0als of groundborne
❑bration within the study area. The operation of heaEy el]lipment [Le., compactor,
backhoe, dollar, excaDators, haul trucks, etc.owould generate ❑brations that would
propagate though the ground and diminish in intensity with distance from the source. No
highGmpact actidties, such as pile drdng or blasting, would be used during project
construction. The nearest offsite receptors to the project site that could be exposed to
❑bration Ielbls generated from project construction include singlelfamily residential
uses located west of the project site. Groundbome dbrations from construction actidties
Diary rarely reach the Ielbls that can damage structures, but they may be perceilbd in
buildings lbry close to a construction site.
The PPV dbration Ilalocities for seCeral types of construction equipment, along with
their corresponding RMS Ilalocities [in VdBQ that can generate perceptible dbration
IeCeIS are identified in Table 25 and Table 26.
Table 25: Peak Particle Velocity (PPV) of Vibration Impacts
Equipment 25 ft. 50 ft. 60 ft. 75 ft. 100 ft.
Large dolbr 0.089 0.031 0.024 0.017 0.011
Auger Drill 0.089 0.031 0.024 0.017 0.011
Loaded truck 0.076 0.027 0.020 0.015 0.010
lbckhammer 0.035 0.012 0.009 0.007 0.004
Small Doter 0.003 0.001 0.0008 0.0006 0.0004
Table 26: Decibel Notation (VDB) Levels of Vibration Impacts
Equipment IL 25 ft. 50 ft. 60 ft.
Lar a dolbr 87 78 76 73 69
Au er Drill 87 78 76 73 69
Loaded truck 86 77 75 72 68
hekhammer 79 70 68 65 61
Small Doter 58 49 47 44 40
7 FrA,Transit Noise and Vibration Impact Assessment May 2006.
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Section 4
The groundborne dbration leials at offsite sensitila uses compared to Caltransland
FTA dbration damage potential threshold are shown in Table 25 and Table26. The
table shows the estimated construction[related groundborne dbration IeDDIS that could
occur at the nearest offsite structures during construction at the project site and a
comparison to the identified significance threshold. As shown in Table 27, the dbration
Lelocities forecasted to occur at the offsite sensiti Eb receptors could potentially be up to
0.0027 in/sec PPV [or 57 VdBDat the nearest singleilamily residential uses.
Table 27: Groundborne Vibration levels at Offsite Sensitive uses Compared to
Caltrans and FTA Vibration Damage potential threshold
Closest Offsite Distance to Estimated Caltrans FTA Vibration Exceed
Sensitive Uses Work Site PPV Vibration Damage Caltrans'or
in/sec)/VdB Damage Potential FTA Vibration
Potential Threshold, Threshold?
Threshold PPV(inlsec)d (Yes or No)
PPV Inlsec `
Singlerfamily 260 0.0027/57 0.5 0.5 No
residential uses:
West of the project
site along
Brookhurst Street
Under the FTA construction dbration damaged criteria, the existing residential
structures are considered Ireinforce[concrete, steel or timber [no plaster[J With respect
to the dbration sources associated with project construction, it is anticipated that
continuous/freouent intermittent sources of dbration, as defined under CaltransE -,riteria,
would occur from compaction actidties at the project site, although no pile[dridng would
be relluired. As such, the dbration IeCel criteria for continuous/freDuent intermittent
sources are used in this analysis.
Based on the information shown in Table 27, which shows an estimated PPV of 0.0027,
none of the existing offsite residential structures [considered as [thew residential
structuresDand Ifeinforced[concrete, steel or timberounder the Caltransland FTA
construction dbration damage criteria, respectilblydocated to the west of the project
site would be exposed to PPV groundborne dbration IeEels exceeding the FTA and
CaltransED.S inches per second criteria as shown in Tables 25 and Table 26. The
dbration impacts at these residential structures would be less than significant.
With respect to human annoyance, the City of Huntington Beach Noise Element
identifies residential areas as noise[sensiti113 land uses. Currently, these types of
sensitile uses that are located in the project site dcinity include the singleitamily
residential uses that are located to the west of the project site. Under the CaltranS❑
❑bration annoyance potential criteria, Dbration IeE bis exceeding 0.04 inches per second
PPV for continuous/frel]tent intermittent sources would be considered distinctly
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SJ Draft Initial Study/Mitigated Negative Declandion&CEgA-Plus Federal Consultation Review 4A8
Section 4
perceptible. In addition, under the FTA dbration impact criteria for general assessment,
residential receptors are considered to be a Category 2 land use. Land uses under this
FTA category exposed to dbration leials exceeding 80 VdB for infrelluent e[ents would
be considered an impact. As shown in Table 27 the single[family residential receptors
located west of the project site would be exposed to ❑bration leials of 0.0027 in/sec
PPV/57 VdB which is well below the Caltransm.04 in/sec PPV distinctly perceptible
threshold and the FTA® 80 VdB impact threshold. Potential dbration impacts related to
human annoyance would be less than significant. No mitigation measures reLUired.
4.13 Population/Housing
A. Would the project induce substantial population growth in an area, either
directly or indirectly?
No Impact: The proposed project would prodde additional wastewater flows to OCWD
GWRS water treatment facility to produce additional water supplies to help replenish the
Orange County Groundwater Basin. The proposed project would help to meet planned
water supply needs and would reduce the demand for imported water supplies. The
proposed project would not in[blCe the extension of any new infrastructure or prodde
new water supplies to any undeleloped areas that would facilitate new growth. The
proposed project would assist in accommodating planned growth in OCSD and OCWD
serdce area and would not induce more growth than what has been planned for by local
and regional planning agencies.
B. Would the project displace substantial numbers of existing housing,
necessitating the construction of replacement housing elsewhere?
No Impact: The proposed project would be operated and constructed at an existing
wastewater treatment facility. The implementation of the proposed project would not
displace any existing housing. The construction of the proposed project would generate
shortiterm construction job opportunities. The majority of the employment opportunities
would be expected to be filled by the local employed and unemployed labor force and
would not increase population leials that would increase housing demand in the study
area.
C. Would the project displace substantial numbers of people, necessitating the
construction of replacement housing elsewhere?
No Impact: The implementation of the proposed project would not displace any
households or indidduals for any period of time.
4.14 Public Services
A. Would the project result in substantial adverse physical impacts associated
with the provision of new or physically altered governmental facilities, need for
new or physically altered governmental facilities, the construction of which could
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%�,J Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 4-97
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cause significant environmental impacts, in order to maintain acceptable service
ratios, response times or other performance objectives for fire protection police
protection, schools, parks or other public facilities.
Police and Fire Protection Services
No Impact: Police and fire protection serdce is currently prodded to the study area by
the City of Huntington Beach Police Department and the City of Huntington Beach Fire
Department. The construction and operation of the proposed project would not increase
the demand for additional fire protection serdces and police protection serdces beyond
the current Wei of demand within the study area. Additionally the construction of the
proposed project would not rewire any road closures or actidties that would increase
response times to the study area. No ad Darse impacts to fire protection serdces and
police protection serdces would occur.
School Facilities
No Impact: The closest school facilities to OCSD Plant No. 2 would be Cohn Eader
Elementary, Isaac Sowers Middle School and Edison High School. The implementation
of the proposed project would not generate a substantial need for new school facilities.
Any new full time employees that could result from the proposed project are expected to
be minimal. In the el ent new households do relocate into the study area the existing
schools within study area would be expected to meet school facility needs for all grades.
No adlerse impacts to school facilities would occur.
Parks
No Impact: The implementation of the proposed project would not generate a need for
new park facilities. Any new full time employees that could result from the proposed
project are expected to be minimal. In the e[Bnt new households do relocate into the
study area existing park facilities within the study area would be expected to meet
parkland needs. No adCerse impacts to park facilities would occur.
4.15 Recreation
Project Impacts
A. Would the project increase the use of existing neighborhood and regional
parks or other recreational facilities such that substantial physical deterioration
of the facility would occur or be accelerated?
Less than Significant Impact: The proposed project would not generate new
households or a substantial amount of new employees that would increase the use of
existing neighborhood and regional parks within the study area. Additionally, the
construction operations associated with the proposed project would not relt ire
temporary closure of the Santa Ana Moor Trail. During construction operations there
trail users along the Santa Ana Ricer Trail could experience elelated le[t;ls of
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Draft Initial Study/Mitigated Negative Declaration&CEgA-Plus Federal Consultation Review 4-98
Section 4
construction noise. Howeler, the impact would be for a shortiperiod of time and would
only be experienced along segments of the trail that would be near where construction
actidty would be occurring. Potential impacts to existing recreation facilities would be
less than significant
B. Does the project include recreational facilities or require the construction or
expansion of recreational facilities which might have an adverse physical effect
on the environment.
No Impact. The proposed project does not propose new recreation facilities or
proposes to expand existing recreation facilities. Therefore, there will not be any
adverse impacts associated with the construction of new recreation facilities or the
expansion of existing facilities. No mitigation measures are reDiired.
4.16 Transportation/Traffic
Existing Setting
Study Area Circulation System
Regional access to the study area is prodded by the I1405 Freeway da the Brookhurst
Street exits. Primary local access is prodded by Brookhurst Street.
Congestion Management Program
The Orange County Transportation Agency is responsible for the implementation of the
County of Orange Congestion Management Program 1CMP1J The CMP is designed to
reduce traffic congestion and to prodde a mechanism for the coordination of land use
and transportation decisions. When a project generates more than 100 peak trips along
a CMP highway or 51 or more trips through a CMP intersection, the project would be
relluired to prepare a traffic impact study to e[luate the impacts on the CMP highway
and intersection.
Existing Truck Routes
The City of Huntington Beach General Plan Circulation Element identifies the following
study area roadways as designated truck routes.
• Brookhurst Street,
• Pacific Coast Highway
• Hamilton ACenue
Public Transportation
The City of Huntington Beach is ser[Bd by the OCTA bus serdce. Currently, the OCTA
operates 19 bus routes throughout the City, a demand response serdce through the
[Dial A[Ride Liprogram, and two parkland[fide facilities. Most major streets within the
City have bus serdce aLbilable.
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Draft Initial Study/Mitigated Negative Declaration&CEgA-Plus Federal Consultation Review 4-99
Section 4
Bicycle and Pedestrian Facilities
The City of Huntington Beach has an extensiDa trail system that includes pedestrian and
bike trails. Additionally, the County of Orange maintains a coordinated system of trails,
including bikeways, hiking trails throughout Orange County. Within the study area the
most widely used offetreet bike trails would be the Santa Ana Ricer Trail and the
Talbert Marsh Bike Trail. Additionally, along the study area roadways are on[street bike
ways.
Project Impacts
A. Would the project be in conflict with an applicable plan, ordinance or policy
establishing measures of effectiveness for the performance of the circulation
system, taking into account all modes of transportation including mass transit
and non-motorized travel and relevant components of the circulation system,
including but not limited to intersections, streets, highways and freeways,
pedestrians and bicycle paths.
Less than Significant Impact: The implementation of the proposed project would not
increase long term operation trips within the study area where it would reduce the lelel
of serdce of study area intersections and roadway segments. Therefore, no long term
adierse traffic impacts would occur.
The construction operations for the proposed project would generate shortCterm traffic
trips which would include, hauling trips, worker traffic trips, delilbry traffic trips, and
traffic trips. Additionally, construction traffic would be generated from the mobiliEl3tion
and demobiliCetion of construction elllipment. A listing of construction traffic trips
generated by the proposed project is shown in Table 28.
Table 28: Project Construction Traffic Trips
Daily Total
Haul Haul
OCSD Flow EQTank,Pump Station,and Pipeline/Meter Vault Worker Vendor Trips Trips
IA:Excavation,Haulin&Grading for Flow EQTank,Pum Station,and Pipeline 10 1 32 248
18:Piles Construction for Flow EQTank 10 2 4 12
1C:Flow EQTank Pad Construction 10 2 12 288
11):Flow EQTank Assembly and Coating 5 2
1E:Assembly of Flow EQ Pumps and Meter Vault 5 4
The majority of construction traffic trips generated from the proposed project would be
hauling trips. As shown in Table 28 a maximum of 32 hauling trips would occur each
day during Phase 1 when the majority of the excalation and hauling actidties would
occur. The hauling truck trips would occur during nonipeak hours and would not reduce
the le�el of serdoe of any intersection or roadway segment within the study area.
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During the construction operations a maximum of up to 10 worker daily [chicle trips and
2 Eendor [chicle trips could occur during peak traffic periods. This amount of traffic trips
would hale a less than significant impact on the study area circulation system. No
mitigation measures are reD/ired.
B. Would the project be in conflict with an applicable congestion management
program, including, but not limited to level of service standards and travel
demand measures, or other standards and travel demand measures, or other
standards established by County congestion management agency for designated
roads and highways.
Less than Significant Impact: The closest CMP Highway within the study area would
Pacific Coast Highway. Pacific Coast Highway is not a designated truck route.
Therefore, no construction traffic generated from the proposed project would be using
Pacific Coast Highway to access the study area. There is the potential that some
workers could utili a Pacific Coast Highway or other CMP Highways to travel to the
study area. As shown in Table 28 the short term traffic generated from the proposed
project would not exceed 100 peak trips or 51 or more trips through an intersection. No
potential conflicts with the County of Orange Congestion Management Program would
occur.
C. Would the project result in a change in air traffic patterns, including either an
increase in traffic levels or a change in location that results in substantial safety
risks?
No Impact. According to the [John Wayne Airport Land Use Consistency Plan, the
study area is not within a clear [one or accidental potential [one. Implementation of the
proposed project would not increase the le[BI of air traffic within the regional area. The
maximum height of the tallest structure proposed on OSCD Plant No. 2 Site would be
30 feet. There would be no component of the proposed project that would encroach into
naDgable air space causing a change to air traffic patterns. No mitigation measures are
reDiired.
D. Would the project increase hazards to a design feature or incompatible uses or
equipment?
Less than Significant Impact with Mitigation: The construction and operation of the
proposed project would occur on the OCSD Plant No. 2 Site. The proposed project
would not in[ol[o any construction actidties along a public roadway that would increase
traffic hazards.
The proposed project would rewire the moCement of heaDj construction equipment
within the study area during mobiligation and demobiliCation periods. The weight of the
heaEy construction could potentially damage the surfaces of study area roadways. All
heaEy truck traffic generated from the proposed project would be reD/ired to use a
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designated truck route for access to and from the project site. By directing truck traffic to
specifically designated truck routes potential damage to study area roadway surfaces
would be minimised.
During mobiliCation and demobiliCation of heaDj construction a uipment, turning
moCements into the OCSD Plant No. 2 Site could reDuire temporary lane closures. The
lane closure would occur during nonipeak traffic periods and if needed a flag men would
be prodded to safely direct traffic. With the implementation of Mitigation Measure T11,
potential ha[ards associated with the mobilisation and demobiliilation of construction
entipment would be reduced to less than significant.
Mitigation Measure
T-1: OCWD will be responsible for preparing aden/ate detour and access plans to
ensure the safe molement of lehicles and pedestrians during the construction period.
E. Would the project result in inadequate emergency access?
Less than Significant Impact with Mitigation: The construction and operation of the
proposed project would not cause any road closures that would adsErsely impact
emergency access routes and emergency response times to the study area. The project
mobiliDation and demobiliDation of heaDj construction eMipment could result in some
temporary traffic congestion to access the project site. The impact would be short®erm
and if needed flag men would be aCailable to ensure emergency access would be
maintained at all times. With the implementation of Mitigation Measure T11, potential
emergency access impacts would be less than significant.
Mitigation Measure
Mitigation Measure TC1re0uired
F. Would the project be in conflict with adopted policies, plans, or programs
regarding public transit, bicycle, or pedestrian facilities or otherwise decrease the
performance or safety of such facilities?
Less than Significant Impact: The construction and operation of the proposed project
would not renlire the long term closure of public transportation, bicycle or pedestrian
circulation systems. The mobilisation and demobililetion of construction eojipment
could rea/ire the temporary closure of onsite street bike lanes near the OCSD Plant No.
2 entrances. The closure would be limited to the time of the mobililstion and
demobilisation actidty which in most cases would be less than 30 minutes and if
needed flag men would be prodded to safely direct traffic. With the implementation of
Mitigation Measure T11 potential conflicts with public transportation systems would be
less than significant.
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Mitigation Measure
Mitigation Measure TL1 re0uired.
4.17 Utilities/Service Systems
Environmental Setting
The study area is situated within an urbanii:od area and supported by existing utility
serdce systems.
Water Service
The Huntington Beach Public Works Department would be responsible for water serdce
within the study area, including operating and maintaining wells, reserCoirs, imported
water connections, and distribution pipelines.
Wastewater Service
The Orange County Sanitation District proddes wastewater serdce to the study area.
The Sanitation District proddes wastewater serdces to approximately 2.6 million people
within a 479 square mile serdce area in central and northwest Orange County, which
includes 20 cities and four special districts. It operates the third largest wastewater
system on the West Coast and consists of oler 396 miles of sewers and two regional
wastewater treatment plants.
Storm Drainage Systems
The Orange County Flood Control District owns, operates, and maintains the region®
flood control facilities while the City of Huntington Beach is responsible for the operation
Solid Waste Management
The City® Huntington Beach Public Works Department is responsible for weekly
residential and commercial trash collection serdces and contracts with Rainbow
Disposal Company, Inc. All trash collected by the Cityfs refuse serdces are sorted and
processed at a Materials RecoEary Facility. Rainbow Disposal Company operates a
Transfer Station located at 17121 Nichols Street with a design capacity of approximately
2,800 tons per day.
The Orange County Integrated Waste Management Department IOCIWMDoowns and
operates three actin landfills starling the Orange County region. These include the
Frank R. Bowerman Landfill 111002 Bee Canyon Access Road, Irdneq Olinda Alpha
Landfill f1942 N. Valencia A[Bnue, BreaQ and the Prima Deshecha Landfill E32250 La
Pata AEOnue, San ❑tan Capistranoo The Olinda Alpha Landfill and the Prima Deshecha
Landfill are open to the public while the Frank Bowerman Landfill is for commercial use
only. All three landfills are permitted as Class III landfills. Class III landfills accept only
nonLlaCardous municipal solid waste for disposal; no ha[lardous or IiLuid waste can be
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accepted. The daily maximum amounts recalled and remaining capacity for land fill
facility is shown in Table 29.
Table 29: Capacity Orange County Landfills
Landfill Daily Maximum Maximum Capacity Remaining Capacity
(Tons) (Cubic Yards) (Cubic Yards)
Frank Bowennan 11,500 127,000,000 59, 411,872
Olinda Alpha 8,000 76,900,000 38,578,383
Prima Deshecha 4,000 172,900,000 87,384,799
Project Impacts
A. Would the project exceed wastewater treatment requirements of the applicable
Regional Water Quality Control Board?
No Impact. The proposed project would prodde additional wastewater flows to OCWD
GWRS water treatment facility to produce additional water supplies to replenish the
Orange County Groundwater Basin. The treated water generated from the GWRS
would be subject to the permit conditions under RWQCB Order RLBL2004@02, and
subse0uent amendment R82008LD058. Compliance with the permit conditions would
ensure that RWQCB reouirements would not be exceeded. No mitigation measures are
reouired.
B. Would the project require or result in the construction of new water or
wastewater treatment facilities or expansion of existing facilities, the construction
of which could cause significant environmental effects?
No Impact: The proposed project be constructed and operated on OCSD Plant No. 2
Site and would not require the expansion or construction of any off site facilities that
would result in significant impacts to the endronment. No mitigation measures are
reDilred.
C. Would the project require or result in the construction of new storm water
drainage facilities or expansion of existing facilities, the construction of which
could cause significant environmental effects?
No Impact: The proposed project would slightly increase the rate of surface water
runoff on OCSD Plant No. 2. Surface water flows would be conDayed into existing
drainage infrastructure and onsite wastewater treatment processes. No mitigation
measures are reLuired.
D. Are sufficient water supplies available to serve the project from existing
entitlements and resources or new or expanded entitlements needed?
No Impact. The water stored in the flow eDualiFl3tion tanks would be from existing
wastewater flows con[-eyed to the OCSD Plant No. 2 Site. No additional water supply
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entitlements, or expanded water supply entitlements are needed. No mitigation
measures are rewired.
E. Would the project result in the determination by the wastewater treatment
provider which serves or may serve the project that it has adequate capacity to
serve the project's projected demand in addition to the providers existing
commitments.
No Impact: The proposed project would not expand OCSD existing wastewater
demands and would not hala an adDarse impact on the capacity of OCSD treatment
facility or an ad Ebrse impact on the capacity of serdce lines that support the OCSD
facilities. No mitigation measures are rewired.
F. Is the project served by a landfill with sufficient permitted capacity to
accommodate the project solid waste disposal need?
Less than Significant Impact: The long term operation of the proposed project would
not increase the demand for solid waste disposal oCer the current le113l of demand.
Construction operations associated with the proposed project would generate limited
amounts of solid waste. The closest landfill to Plant No. 2 would be the Frank R.
Bowerman Landfill located at 11002 Bee Canyon Access Road in the City of Irdne. The
Frank R. Bowerman Landfill has a remaining capacity of 59,411,872 cubic yards. The
proposed project would comply with federal, state and local statues and regulations
related to solid waste and where possible would recycle discarded construction
materials and other solid waste. The amount of construction related solid waste
generate from proposed project would ha Ea a de minimiEb impact on the capacity of
landfills that would serEa the proposed project. To minimiEb solid waste disposal
demands OCWD would inEbstigate all a0ailable alternati[as, and then select the best
method of solid waste disposal and reduction of solid waste stream. With the
implementation of Mitigation Measure U[1 potential solid waste disposal needs would
be less than significant.
Mitigation Measure
U-1: OCWD will inCestigate all aCailable alternatiCes, and then select the best method of
solid waste disposal and reduction of solid waste stream as rewired in the California
Integrated Waste Management Act prior to the start of construction.
G. Would the project comply with federal, state and local statutes and regulations
related to solid waste?
Less than Significant Impact with Mitigation: Any solid waste generated by the
proposed project would be hauled from the site, diEerted and recycled, in accordance
with the California Integrated Waste Management Act of 1989. If any hamrdous
materials are encountered, the OCWD would coordinate with the City of Huntington
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Beach and the Orange County Health Care Agency® Certified Unified Program Agency
to ensure that all halardous wastes would be disposed of properly in accordance with
local, state and federal laws. No mitigation measures are renlired. With the
implementation of Mitigation Measure U[] potential conflicts with federal, state and local
statutes and regulations related to solid waste would be less than significant.
Mitigation Measure
Mitigation Measure U17 reDuired.
MANDATORY FINDINGS OF SIGNIFICANCE
A. Does the project have the potential to degrade the quality of the environment,
substantially reduce the habitat of fish or wildlife species, cause a fish or wildlife
population to drop below self-sustaining levels, threaten to eliminate a plant or
animal community, reduce the number or restrict the range of a rare or
endangered plant or animal or eliminate important examples of the major periods
of California history or prehistory.
Less than Significant with Mitigation: The construction and operation of the
proposed project would occur on the OCSD Plant No. 2 Site. The location where the
proposed project improDaments would occur is de[bid of sensitiCe habitat, wildlife and
plant species and cultural resources. The proposed project would implement mitigation
measures to aCbid impacts to unknown cultural resources in the unlikely eCent they are
encountered during construction operations. The implementation of the proposed
project would not reduce the habitat of fish or wildlife to self[sustaining lei els and would
not impact any known cultural resources.
B. Does the project have impacts that are individually limited but cumulatively
considerable?
Less than Significant Impact with Mitigation: The proposed project would comply
with local and regional planning programs, applicable codes and ordinances, state and
federal laws and regulations and project mitigation measures. Compliance with the
applicable codes, planning programs and project mitigation measures would reduce the
project® incremental contributions to curei impacts to a less than significant le[bl.
C. Does the project have environmental effects which will cause substantial
adverse effects on human beings, either directly or indirectly?
Less than Significant with Mitigation: The proposed project would not hai b any
substantial ad[erse effects on human beings. The proposed project would comply with
local and regional planning programs, applicable codes and ordinances, state and
federal laws and regulations and project specific mitigation measures to insure that long
term operational actiUties and short®erm construction actidties associated with the
proposed project would not result in direct or indirect adverse impacts to human beings.
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Section 5
SECTION 5.0 CEQA-Plus Federal Consultation Review
5.1 Purpose
The CEQA-Plus Federal Consultation Redew reluirements that hale been established
by the U.S. Endronmental Protection Agency are intended to supplement the CEQA
Guidelines with specific relairements for endronmental documents acceptable to the
State Water Resources Control Board when redewing applications for SRF loans. This
CEQA[Plus Federal Consultation Redew analysis has been prepared to supplement
Initial Study/Mitigated NegatiDa Declaration prepared for the Orange County Water
District Water Production Enhancement Project.
5.2 Federal Endangered Species Act (ESA), Section 7
Does the project involve any direct effects from construction activities, or indirect
effects such as growth inducement that may affect federally listed threatened or
endangered species or their critical habitat that are known, or have a potential, to
occur on-site, in the surrounding area, or in the service area?
ONo. Discuss why the Project will not impact any federally listed special status
species:
The following analysis is based on the Biological Assessment that was prepared for the
Orange County Water District Water Production Enhancement Project by the OCWD
Natural Resources Department in lane of 2016. The Biological Assessment is
presented in its entirety in Appendix C. As part of the Biological Assessment, OCWD
conducted an onsite biological field surCey in lane of 2016 to determine the presence of
Federal Listed plant species and Federal Listed wildlife species. .
The OCSD Plant No.2 Site is located within USGS Newport Beach Quadrangle at
Township 6 South, Range 10 West, and Section 20. The site is deleloped with
wastewater treatment structures, offices, and paEbd parking areas and roadways. A
row of eucalyptus trees extends along western boundary of Plant No. 2 and scattering
of natiCe landscaping prolded along the Santa Ana Ricer Trail boarders Plant No. 2 to
the east. A site surCey of the study area did not identify any sensiti Lb biological
resources on Plant No. 2. Within close ❑cinity to Plant No.2 are two biological
resources; the Talbert Marsh and California Least Tern Colony.
Talbert Marsh is a tidal marsh that has been restored to full tidal action. The water
within Talbert Marsh is seawater from the ocean inlet located south of the marsh
property that fluctuates in height up to 8 feet from tidal flows. Talbert Marsh proddes
habitat for both migratory and resident bird species.
South of Pacific Coast Highway is the location the California Least Tern Natural
Preser[l:Area. The California Least Tern Natural Preseria Area was first established
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OJ Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 5-1
Section 5
under the Huntington State Beach General Del elopment Plan in 1976. It was originally
dedicated on 2.5 acres and was fenced off with a cyclone fence ® heaEylduty, chain❑
link fence topped with barbed wireoto prelant predators from harassing the birds. OLgr
the years, the California least terns nesting area has expanded beyond the fenced
area, State Parks has erected additional picket fencing to protect the birds. Currently,
the cyclone fence area colors approximately 8.9 acres and the picket fence Irontlyard❑
area is 3.8 acres. California State Parks protects the nesting area by limiting access,
conducting trash remoDal, grooming the sand periodically, and conducting predator
management.
Federal Listed Plant Species
To determine the potential for Federal Listed plant species to be present within the
study area, a database search with the United States Fish and Wildlife information and
Planning Database and the California Department Fish and Wildlife ICDFWE]Natural
DiCersity Database was conducted. A listing of Federal Listed plant species with
potential to occur within the Newport Beach USGS Quadrangle is shown in Table 30.
Subseouent to the database search, a surLey of the study area was conducted to
determine the presence of plant species identified in the database searches. The
determination on the potential for the Federal Listed plant species to occur within the
study area was based on the following criteria:
• Present: Species was obserled within the study area within the last year.
• High: The study area supports suitable habitat and the species has been
obseri ad within the last year.
• Moderate: The study area supports suitable and the species has not been
obserFlad within last two years.
• Low: The study area lacks suitable habitat for the species.
Table 30: Federal Listed Plant Species
Species Federal CNPS General Habitat/Recent Potential for
Occurrence Occurrence Study Area
Ventura Marsh Milk I E 113.1 Marshes, Swamps, Coastal Low
[latch Dunes, Coastal Scrub Study Area lacks suitable
[lstragalus habitat
pycnostachy lar.
Lanosissimus
Salt Marsh Birdsdreak E 1 B.2 Coastal Salt marsh, Coastal Low
(Chloropyron maritimum Dunes Study Area lacks suitable
ss . Marttimum) habitat
San Diego Buttons E 1B.1 Vernal pools, Coastal Low
Celery Scrub,Valley and Foothill Study Area lacks suitable
dEryngium aristulalum Grasslands habitat
fir. arishii❑
Gambols Water Cress 1 E 1 113.1 1 Marshes and swamps i Low
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(Nasturtium gambelii) Study Area lacks suitable
habitat
Federal State Listing California Endangered California Nanue Plant SodeN CNPS
E Endangered Soeces Act C0FG 1A&lants presumed extinct in California
T Threatened FP Fully Protected 113 tans rare,mreetened,or endangered in
SSG Specia15peciesof Concern EEndangered California and elsewhere
C.Candidate for Listing TThreatened 2[lama rare,threatened,or endangered in
NLNot Listed SSendua California but more common elsewhere
SSC Special Species of Concern 3®lenls about which ad need more renew
WL Watch List 4roants of limped distribution
NL Not Listed CNPS Threat Rank
.1 Seriously Endangered
.2 Fairly Endangered
.3 Not Very Entertained
Federal Listed Wildlife Species
To determine the potential for Federal Listed wildlife species to be present within the
study area, a database search with the United States Fish and Wildlife Serdce
IUSFWSDinformation and Planning Database and the Department of California Fish
and Wildlife Natural DiLbrsity Database was conducted. A listing of Federal Listed
wildlife species with potential to occur within the Newport Beach USGS Quadrangle is
shown in Table 31. SubseQlent to the database search, OCWD conducted a surlby of
the study area to determine the potential for the Federal Listed wildlife species to be
present within the study area. The determination on the potential for the Federal Listed
wildlife species to occur within the study area was based on the following criteria:
• Present: Species was obserled within the study area within the last year.
• High: The study area supports suitable habitat and the species has been
obserCed within the last year.
• Moderate: The study area supports suitable and the species has not been
obserled within last two years.
• Low: The study area lacks suitable habitat for the species.
Table 31: Federal Listed Wildlife Species
Species Federal General Potential Occurrence
Classification Habitat/Recent Study Area
Occurrence
San Diego Fairy Shrimp E Vernal pools Low
(Branchinecta sandiegonensis) Study Area lacks
suitable habitat
Western Snowy PloEar T Sandy Beaches Low
(Charadrius alexandrines nivosus) Study Area lacks
suitable habitat
Southwestern Willow Flycatcher E Riparian woodlands Low
(Empidonax trai/li extimus) Study Area lacks
suitable habitat
Pacific Pocket Mouse E Coastal Plains Low
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(pemgnathus longimembris Study Area lacks
pacirus) suitable habitat
Coastal California Gnatcatcher T Coastal sage scrub Low
(Poltoptila califomica califomica) Study Area lacks
suitable habitat
Light[Footed Clapper Rail E Salt marshes Low
(Rallus longirostris levipes) Study Area lacks
suitable habitat
California Least Tem E Sandy Beaches Low
(Sterna antillamm) Study Area lacks
suitable habitat
Least Bells 7reo E Low growing riparian Low
(Vireo bel/ii pusillus) habitats Study Area lacks
suitable habitat
Critical Habitat
The Federal Endangered Species Act rehires the federal golernment to designate
Critical Habitat for any species it lists under the Federal Endangered Species Act.
Critical Habitat is defined as 1 Dspecific areas within the geographical area occupied by
the specie at the time of listing, if they contain physical or biological features essential to
conserlation, and those features may relluire special management considerations or
protection and 2Dspecific areas outside the geographical area occupied by the species
if the agency determines that the area itself is essential for conserlation. According to
the of USFWS Information, Planning, and ConserEation System Database and the
California Department of Fish and Wildlife Natural Dillarsity Database, the study area is
not located on lands that are designated as Critical Habitat.
Project Impacts
Onsite Impacts
Less than Significant Impact: Based on a rel lew of databases from United State Fish
and Wildlife Serdce and California Department of Fish and Wildlife and biological
surEeys conducted within the study area, it has been determined that there would be
low potential for special status plant species or special status wildlife species to be
present on OCSD Plant No. 2. As shown in Table 30 and Table 31 Plant No. 2 lacks
suitable habitat to support special status plant species or special status wildlife species
that were identified in the database search. Additionally, no indications were found that
any special status species were elbr present. Therefore, implementation of the
proposed project would not result in adCerse impacts to any special status plant species
or special status wildlife species.
OOrange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 5.4
Section 5
Offsite Impacts
Less than Significant Impact: Located south of OCSD Plant No. 2 is the Talbert
Marsh and south of Pacific Coast Highway is the California Least Tern Colony. Both of
these biological resources could prodde suitable nesting habitat for special status bird
species. The construction operations for the proposed project would be confined to
OCSD Plant No. 2. No construction act!dties would occur at the Talbert Marsh or at the
California Least Tern Colony. Therefore, no direct impacts to special status plant or
wildlife species would occur.
The construction actidties for the proposed project would in mlLj�i the operation of heaEy
construction eDuipment that could operate during nesting season. If the construction
actiUty was to occur in close proximity to nesting birds there would be the potential that
breeding patterns could be disturbed. The United States Fish and Wildlife Serdce as
established a noise impact threshold of 60 dBA to identify potential adCerse impacts to
nesting birds. The Talbert Marsh is located approximately 3,300 feet from where the
construction actidties would occur and the California Least Tern Colony is located
approximately 4,200 feet from the construction would occur. Based on the nosiest
piece of construction elluipment that would be used, the noise estimated leial at the
Talbert Marsh and at the California Least Tern Colony would be below 49 dBA.
Additionally, with the presence of the block wall around Plant No. 2 and the traffic noise
along Pacific Coast Highway, it would be Cery unlikely that construction noise would
herd at either location. Potential indirect noise impacts to special status wildlife species
would be less than significant. No mitigation measures are reDuired.
5.3 Magnuson-Stevens Fishery Conservation and Management Act, Essential
Fish Habitat:
Does the project involve any direct effects from construction activities, or indirect
effects such as growth inducement that may adversely affect essential fish
habitat?
❑X No. Discuss why the project will not impact essential fish habitat:
According to redew of the National Marine Fisheries Serdce Essential Fish Habitat Map
for the Pacific Ocean, there is no essential fish habitat in the surface water bodies near
the study area. Therefore, the construction and operation of the proposed project would
not result in adlbrse impacts to any Essential Fish Habitat.
5.4 National Historic Preservation Act, Section 106
Identify the area of potential effects (APE), including construction, staging areas,
and depth of any excavation. (Note: the APE is three dimensional and includes all
areas that may be affected by the project, including the surface area and
extending below ground to the depth of any project excavations).
OOrange County Water District Water Production Enhancement Project
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Section 5
The following analysis is based on a Phase 1 Cultural Resource Report prepared for the
Water Production Enhancement Project. The Phase 1 Cultural Resources Report is
presented in Appendix C.
Area of Potential Effects
An Area of Potential Effects EAPEowas established for the project according to Section
106 of the NHPA in coordination with the OCWD. The APE is shown in Figure 22 and is
defined as:
❑ the geographic area or areas within which an undertaking may directly or
indirectly cause alterations in the character or use of historic properties, if any
such properties exist. The APE is influenced by the scale and nature of an
undertaking and may be different for different kinds of effects caused by the
undertaking 136 Code of Federal Regulations 11DFREB00.161d®
The horiContal APE encompasses the Flow EDualillition Tank, Pump Station and Flow
ElllallEbtlon Control/Meter ®bout 3.70®cres[]and the area encompassing the pump
station Mbout 0.28 acre[]The Certical APE includes the anticipated maximum depth of
ground disturbance of 25 feet below ground surface and the maximum height of the flow
eoualiDotion tank of 30 feet abo[e ground surface.
South Central Coastal Information Center Records Search
A records search for the APE and a ❑ [mile radius was conducted on one 21, 2016 at
the South Central Coastal Information Center ISCCIC4located at California State
UniCersity, Fullerton. The records search included a redew of all recorded cultural
resources within a ❑ [mile radius of the project APE, as well as a redew of cultural
resource reports on file. The Historic Properties Directory was also examined for any
documented historic[iberiod built resources within or adjacent to the project APE. The
results of the SCCIC records search are included in Appendix C.
Previous Cultural Resources Investigations
A total of 61 cultural resources studies hale been conducted within a o [mile radius of
the project APE. Of the 61 predous studies, file studies included a pedestrian surlay of
portions of the APE, and four included archi lal research for the APE. A complete list of
the 61 studies located within ❑mile of the project APE is located in Appendix C. Less
than 50 percent of the project APE has been included in predous cultural resources
surEbys.
Previously Recorded Cultural Resources
The records search indicated that nine cultural resources ham been predously
recorded within a mile radius of the project APE. No cultural resources haCe been
predously recorded within the project APE. Selbral prehistoric sites haCe been
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Section 5
recorded within the search radius along the east bluffs of the Santa Ana RIDar
approximately 2,000 feet east of the project APE.
Historic Map and Aerial Review
Historic maps and aerial photographs were examined in order to prodde historical
information about the APE and to contribute to an assessment of the APE®
archaeological sensitidty. Atailable maps include: the 1868 U.S. Surveyor Generals
surEey plat map of Townships 5 and 6 South, Range 10 West the 1895 and 1901 Santa
Ana 1:62,500 topographic ruadrangles; the 1902 Corona 1:125,000 topographic
Quadrangle; and the 1935 Newport Beach 1:31,600 topographic Quadrangles; and 1965
and 1975 Newport Beach 7.51ninute topographic Quadrangle. Historic aerial
photographs of the APE from 1938, 1953, 1963, 1972, 1994, 2002, 2003, 2004, 2005,
2009, and 2010 were also examined ibistoricaerials.com, 20160
The 1868 U.S. SurCeyor General® suray plat map shows the APE as being located
within Rancho Las Bolsas. The plat map indicates salt marshes within the current
location of OCSD Plant No. 2. The aailable historic maps and aerial photographs
indicate that the APE and surrounding area was largely used for agricultural purposes
throughout the 201h century, and did not become urbaniCed until the latter half of the
century. The Santa Ana Rimer is shown confined with artificial IeDaes in the 1938 historic
aerial photograph. The OCSD Plant No. 2 is not shown on the 1953 aerial. The OCSD
Plant No. 2 facility is shown on the 1965 Newport Beach 7.5[aninute topographic
ruadrangle. Based on a detailed redew of the 1972 and 2016 aerials of the OCSD
Plant No.2, there are structures shown on the 1972 aerial that remain risible on the
2016 aerial photograph.
Native American Outreach— 2016
On rune 2, 2016, a SLF search reouest letter was sent to the NAHC in an effort to
determine whether any sacred sites are listed on SLF for the APE. A response was
prodded on rune 6, 2016 indicating negatia results for Natile American cultural
resources within the project APE. The NAHC recommended outreach to 12 specific
tribal authorities who may want to comment on our search reruest. A letter to the
NAHC[fisted tribal authorities was mailed on rune 20, 2016. Phone calls were made to
each of the named tribal members on rune 28, 2016. Responses from each tribe is
prodded in Appendix C.
The representatias from Tonga Acenstral Terrotorial Tribal Nation,
Gabrieleno/Tong a San Gabriel Band of Mission, Gabrielino Tonga Tribe, Gabrielin
Tonga Nation, and ruaneno Band of Mission Indians Acjachemen Nation
recommended that because of the culutuial and spiritual sensitidty of the study area
that the project incorporate Natia American and Archeological Monitoring.
fCN Orange County Water District Water Production Enhancement Project
SJ Draft Initial Study/Mitigated Negative Declaration&CEgA-Plus Federal Consultation Review 5-7
Section 5
AB 52
In August 2016, OCWD sent letters to two NatiCe American representatiCes who haDa
reDiested to be informed on actidties conducted by the OCWD, under PRC Section
21080.3.1. The OCWD reached out to the dlanedD Band of Mission Indians
Acjachemen Nation and Gabrieleno Band of Mission Indians d Kith Nation.
Consultation efforts are currently onl�oing.
Santa Ana Ri Cer. To the south of the APE, the OCSD Plant No. 2 site contains
unconsolidated eolian dune deposits.
Archaeological Potential
Although paced and filled, the portion of the APE at the OCSD Plant No. 2 appears to
retain high sensitiity for buried archeological resources. During the latest Pleistocene
and Holocene, the geomorphic setting of the portion of the APE at the OCSD Plant No.
2 changed from inland to coastal, and rising sea IeDal resulted in fludal deposition
capable of burying archaeological resources. The portion of the APE at the OCSD Plant
No. 2 was largely salt marsh into the early 20th century, but this is an area that would
hake offered important resources. Owing to its marshy endronment, this area may not
hake been famred for any substantial occupation, but nonetheless is likely to hale been
dsited for resource procurement and could contain artifacts associated with those
actidties. Additionally, the saturated conditions offered within this setting may haDq
aided in the preseriation of relatiltaly rare organic artifacts.
Cultural Resources Survey and Results
A cultural resources pedestrian Burl by of the APE was conducted on Rine 16, 2016 by
Arabesriue SaidEAbdelwahed to identify the presence of surface archaeological
materials. The OCSD Plant No. 2 consists of existing tanks and waste water treatment
buildings. The locations of the propose flow eRlaliDation tank and flow eRlalilbtion
control/meter are currently paled and natural ground was not risible. Portions of the
proposed location for the Flow EOualiDation Pump Station and pipeline connection to the
flow eRlaliCetion tank are unpaCed and were surDayed in regular inter[-Ols. No
archaeological or historic built resources were obserCed within the APE. Potential
historic[period buildings/structures were noted at the OCSD Plant No. 2 outside of the
APE.
Historic Resources
One potential historic built resource, OCSD Plant No. 2, was identified as a result of this
study. OCSD Plant No.2 was initially constructed more than 45 years ago$, although
g The California GHP recommends including all resources over 45 years of age in the planning process given the lag time
between environmental documentation and project implementation.Generally,resources more than 50 years of age require
QOrange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEgA-Plus Federal Consultation Review 5-8
Section 5
none of the historiciage buildings/structures appear to be within the APES. The
improCements proposed within OCSD Plant No. 2 are shown in Figure 3. The proposed
construction actidties would haEo no impact on aboEeground built[endronment
resources. The actidties would be located in areas where there are no known historical
resources dating from before 1971; where the area is currently only graded and paced.
The implementation of the Water Production Enhancement Project would not adCersely
impact any historic or potentially historic resource.
Archaeological Resources
As a result of this study, no archaeological resources were identified within the APE.
Howelbr, based on the results of study, the project APE should be considered highly
sensitilb for subsurface archaeological resources. Since the project includes ground-
disturbing actidties, there is a potential for disco Eery of subsurface archaeological
deposits that could nlalify as historic properties under Section 106 of the NHPA and/or
historical or uniELe archaeological resources under CEQA. This potential impact to
unknown archaeological resources would be considered significant. Mitigation
Measures CRE1, CR12, and CR13 are recommended to ensure that the project would
result in No Historic Properties Affected under Section 106 of the NHPA and less than
significant impacts to historical or unioue archaeological resources under CEQA.
Mitigation Measures
CR-1: Prior to earth modng actidties, a Dualified archaeologist meeting the Secretary of
the Interiors Professional Qualifications Standards for archaeology [U.S. Department of
the Interior, 200812vill conduct cultural resources sensitidty training for all construction
personnel. Construction personnel shall be informed of the types of cultural resources
that may be encountered, and of the proper procedures to be enacted in the eCent of an
inadDartent discoDary of archaeological resources or human remains. OCWD will
ensure that construction personnel are made aCailable for and attend the training and
retain documentation demonstrating attendance.
CR-2: Prior to the start of any ground[disturbing actidties, OCWD will retain an
archaeological monitor to obserEB all ground[disturbing actidties. Archaeological
monitoring will be conducted by a monitor familiar with the types of archaeological
resources that could be encountered and shall work under the direct superdsion of the
❑ualified archaeologist. Monitoring may be reduced or discontinued by the Dfalified
archaeologist, in coordination with OCWD, based on obserCations of subsurface soil
stratigraphy and/or the presence of older CmloriCbn deposits. The monitor will be
empowered to halt or redirect ground[disturbing actidties away from the ❑cinity of a
evaluation for listing in the National Register and California Register to assess impacts in historic properties under Section
106 of the NHPA and historical resources under CEQA.
9 The project may require creation of a separate architectural APE in order to adequately address directlindirect effects to historic
builtreaowces.
Orange County Water District Water Production Enhancement Project
OO Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 5A
Section 5
disco[ery until the Dtalified archaeologist has eleluated the disco[ery and determined
appropriate treatment. The monitor will keep daily logs detailing the types of actidties
and soils obseried, and any disco Dories. After monitoring has been completed, the
Dlalified archaeologist shall prepare a monitoring report that details the results of
monitoring. The report shall be submitted to OCWD, SCCIC, and any Native American
groups who reouest a copy.
CR-3: In the eCent of the discoCery of archaeological materials, OCWD or its contractor
shall immediately cease all work actidties in the area within approximately 100 feetoof
the discoEary until it can be eEaluated by the Dtalifed archaeologist. Prehistoric
archaeological materials might include obsidian and chart flaked[stone tools [e.g.,
projectile points, kni[es, scrapersoortoolimaking debris; culturally darkened soil
®nidden®containing heat®ffected rocks, artifacts, or shellfish remains; and stone
milling eDiipment [e.g., mortars, pestles, handstones, or milling slabs[]and battered
stone tools, such as hammerstones and pitted stones. HistoricEperiod materials might
include stone or concrete footings and walls; filled wells or prides; and deposits of
metal, glass, and/or ceramic refuse. Construction shall not resume until the Dtalified
archaeologist has conferred with OCWD on the significance of the resource. SWRCB
shall be afforded the opportunity to determine whether the discoCery reFuires
addressing under Section 106 PostLRedew DiscoCeries prodsions proiided in 36 CFR
800.13.
If it is determined that the discoEered archaeological resource constitutes a historic
property under Section 106 of the NHPA or a historical resource under CEQA,
aD/idance and preser[lition in place shall be the preferred manner of mitigation.
PreserDation in place maintains the important relationship between artifacts and their
archaeological context and also serCes to a[Did conflict with traditional and religious
lblues of groups who may ascribe meaning to the resource. Preseroation in place may
be accomplished by, but is not limited to, albidance, incorporating the resource into
open space, capping, or deeding the site into a permanent conserCation easement. In
the eCent that preserlbtion in place is demonstrated to be infeasible and data recoCery
through excalbtion is the only feasible mitigation albilable, an Archaeological
Resources Treatment Plan that proddes for the ade0uate recolbry of the scientifically
conseDtential information contained in the archaeological resource shall be prepared
and implemented by the D/alified archaeologist in consultation with OCWD. The
appropriate NatiEe American representati[es shall be consulted in determining
treatment for prehistoric or NatlDs American resources to ensure cultural EAlues
ascribed to the resource, beyond that which is scientifically important, are considered.
Native American Sacred Remains
Native American respondents indicated sensitidty for archaeological resources in the
APE and surrounding area gilbn the proximity to the Santa Ana Rilbr corridor. In
OOrange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declaration&CEQA-Plus Federal Consultation Review 5-10
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addition, the geoarchaeological redew indicates that the portion of the APE within
OCSD Plant No. 2 was largely salt marsh into the early 20th century and would hale
offered important resources. Owing to its marshy endronment, this area may not hale
been fa[Dred for any substantial occupation, but nonetheless it is likely to haEb been
❑sited for resource procurement and could contain artifacts associated with those
actidties. Additionally, the saturated conditions offered within this setting could haEP
aided in the preserCation of relati[bly rare organic artifacts. Mitigation Measures CRA is
recommended to ensure that the project would result in No Historic Properties Affected
under Section 106 of the NHPA and less than significant impacts to historical or unidue
archaeological resources under CEQA.
Mitigation Measure
CR-4: Prior to issuance of a grading permit and prior to start of any ground[disturbing
actidties, OCWD will retain a NatiDa American monitor to obser0a all ground[disturbing
actidties. The monitor shall be obtained from a Tribe that is traditionally and culturally
affiliated with the area, according the NAHC list. The monitor shall be empowered to
halt or redirect ground[disturbing actidties away from the dcinity of a discoEbry until the
ELalified archaeologist has eaauated the disco[bry and determined appropriate
treatment. Monitoring may be reduced or discontinued, in coordination with OCWD and
the ELalified archaeologist, based on obserEbtions of subsurface soil stratigraphy and/or
the presence of older C[hori[bn deposits.
5.5 Federal Clean Air
Air Basin: South Coast Air Basin
Local Air District: South Coast Air Quality Management District
Is the project subject to a State Implementation Plan (SIP) conformity
determination?
❑x Yes. The project is in a non[attainment area or attainment area subject to
maintenance plans for a federal criteria pollutant. Include information to indicate the
non®ttainment designation [e.g. moderate, serious, seEare, or extremeq if applicable. If
estimated emissions lbelowdare aboEb the federal de minimis leEbls, but the project is
siEbd to meet only the needs of current population projections that are used in the
approved SIP for air duality, then ELantitatiEbly indicate how the proposed capacity
increase was calculated using population projections.
The NEPA air ELality analysis compares the proposed projects impacts with the
Federal thresholds in order to determine if impacts to Clean Air Act pollutants would
exceed federal thresholds. Considering the standards deEbloped for the State of
California are more restrictiEb than the federal thresholds, the analysis detailed aboEb
0Orange County Water District Water Production Enhancement Project
Draft Initial Study/Mitigated Negative Declam ion&CEQA-Plus Federal Consultation Review 5-11
Section 5
for Air Quality and Greenhouse Gasses would serf to prof compliance with the
NEPA analysis.
The SCAQMD is responsible for the deDalopment of the Basin® portion of the State
Implementation Plan [SIPq which is rel7uired under the federal Clean Air Act for areas
that are in nonattainment for criteria pollutants. The project may obtain state funding
and therefore, under the Clean Air Act, the proposed project would be subject to a SIP
conformity determination. This is because the study area is in a seEbre nonattainment
area for 81hour omne, a moderate nonattainment area for PM10 and a maintenance
area for CO and PM10. Table 32 shows the attainment status for each of the criteria air
pollutants. Under the Clean Air Act de minimis lelels for criteria pollutants hale been
established as a screening lel al to determine the potential for a proposed Project to
adlersely impact air emissions. Emissions are compared to these Ielels for the SIP
conformity determination rde minimise If the project is below the de minimis leiels then
the project is determined to be in conformance with the SIP. If a project exceeds the de
minimis leLels then a full conformity analysis must be conducted. 40 CFR 93 a 153
defines de minimis le[Pls, that is, the minimum threshold for which a conformity
determination must be performed, for Darious criteria pollutants in [arious areas.
Table 32: De Mimimis Levels
Pollutant Area Type Tonslyear
Olone VOC or NOx❑ Serious nonattainment 50
Selore nonattainment 25
Extreme nonattainment 10
Other areas outside an clone transport region 100
OCone INOXE Marginal and moderate nonattainment inside an 100
omne transportation region
Maintenance 100
OCone VoC❑ Marginal and moderate nonattainment inside an 50
olone transport region
Maintenance within an ocune transport region 50
Maintenance outside an omne transport region 100
CO, S02, NO2 All nonattainment and maintenance 100
PM10 Serious nonattainment 70
Moderate nonattainment and maintenance 100
PM2.5 All nonattainment and maintenance 100
Source:USEPA,2016a,USEPA 2016b
Project Emissions
As shown in Table 33, omne precursors are below the de minimis thresholds for
construction and operational actidties, and therefore, the project is consistent with the
SIP. Construction emissions show only the maximum emissions for the proposed
0Orange County Water District Water Production Enhancement Project
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Section 5
project in tons per year and are based on the maximum days of construction per
subphase. Because the proposed project emissions are below the de minimis
thresholds, a detailed conformity analysis is not warranted.
Table 33: SIP Conformity Evaluation
Pollutant Federal Nonattainment Threshold of Maximum Operational
Status Rates Significance Construction Emissions
(tons/year) Emissions (tons/year)
(ton )
Omne 101O Non Extreme See 0/OC O NOxo
Aadainment
Carbon Monoxide ECOO Attainment/ N/A 100 0.64 0.0155
Maintenance
Oxides of Nitrogen N/A N/A 10 1.43 3.3eE3
:NOxO
Volatile Organic N/A N/A 10 0.91 6.5eE3
Compounds IVOC❑
Lead EPb❑ Attainment N/A N/A N/A N/A
Particulate matter less Non Moderate 100 0.10 4.62e[3
than 2.5 microns Attainment
IPM2,s®
Particulate matter less Attainment/ N/A 100 OA9 1.27e[3
than 10 microns Maintenance
IPM1o®
Sulfur Dioxide ES02O Attainment N/A N/A 0.00 6.Oe6
Notes:NIA]Nonrappllcable
Soup: ESA 2016;USEPA,2016a,USEPA 2016b
As discussed predously, no growthGhducing delelopment or land use would occur under the
proposed project, and therefore, the project would not conflict with the Citys General Plan.
Therefore the project would be consistent with the AQMP. Additionally, as the annual
emissions from the project would be well below the de minimis thresholds for SIP conformity,
the proposed project is considered to be in conformance with the SIP. No mitigation measures
are reolired.
5.6 Coastal Zone Management Act
Is any portion of the project site located within the coastal zone?
The OCSD Plant No. 2 Site is located within the coastal Ibne and is included within the
City of Huntington Beach Coastal Element. The proposed project would renlire
approDal of a coastal delelopment permit from the City of Huntington Beach. With
approml of coastal deDglopment permit, the proposed project would be consistent with
the City of Huntington Beach Coastal Element.
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5.7 Coastal Barriers Resources Act
Will the project impact or be located within or near the Coastal Barrier Resources
System or its adjacent wetlands, marshes, estuaries, inlets, and near-shore
waters? Note that since there is currently no Coastal Barrier Resources System in
California, projects located in California are not expected to impact the Coastal
Barrier Resources System in other states. If there is a special circumstance in
which the project may impact a Coastal Barrier Resource System, indicate your
reasoning below.
❑x No. The Project will not impact or be located within or near the Coastal Barrier
Resources System or its adjacent wetlands, marshes, estuaries, inlets, and nearishore
waters.
According to the United States Fish and Wildlife Serdce Official Coastal Barrier
Resource System Maps there are not any coastal barriers within or near the study area.
Therefore, the proposed project would not be in conflict with Coastal Barrier Resources
Act.
5.8 Farmland Protection Policy Act
Is any portion of the project located on important farmland?
❑x No. The project will not impact farmland.
The study area is located in a highly urbaniCed area. The study area doesnmcontain
any existing agriculture land uses. According to the California Farmland Mapping and
Monitoring Program, there is no Prime Farmland, Uniale Farmland or Farmland of
Statewide Importance within the study area. The study area is Coned for urbaniCed land
uses and there are no existing Williamson Act Contracts recorded within the study area.
The construction and operation of the proposed project would not impact any important
farmland resources.
5.9 Flood Plain Management
Is any portion of the project located within a 100-year floodplain as depicted on a
floodplain map or otherwise designated by the Federal Emergency Management
Agency?
0 No. Prodde a description of the project location with respect to streams and potential
floodplains:
As shown in Figure 13 the OCSD Plant No. 2 Site is located in Flood Zone X. This area
is protected from the one-Oercent®nnual[3hance flood by IeCee, dike, or other
structures subject to possible failure or oCertopping during larger floods.
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5.10 Migratory Bird Treaty Act
Will the project affect protected migratory birds that are known, or have a
potential, to occur on-site, in the surrounding area, or in the service area?
❑x No. Prodde an explanation below.
The locations where the proposed project would be constructed does hat19 habitat to
support migratory birds. Along the perimeter of Plant No.2 are a row of eucalyptus trees
that could prodde potential nesting opportunities for migratory birds. Construction
actidties for the proposed project would not inmlL]a the remoEsl of any trees. Therefore,
potential direct impacts to nesting migratory birds would be amided. Additionally, sound
attenuation measures would be incorporated into the project to minimiCa noise impacts
in the study area.
There is potential the migratory birds could net at the Talbert marsh or at the California
Least Tern Colony. The Talbert Marsh is located approximately 3,600 feet from the
construction actidties and the California Least Tern Colony is located approximately
4,500 feet from where the construction would occur. At the distance the construction
noise leLels would be minimal and would not pose a potential disruption to nesting
birds. The implementation of the proposed project would not result in significant adCerse
impacts to migratory birds or result in significant adCerse impacts to wildlife moDament.
No mitigation measures are rewired.
The implementation of the proposed project would not result in significant adtbrse
impacts to migratory birds or result in significant adtlarse impacts to wildlife molement.
No mitigation measures are rewired.
5.11 Protection of Wetlands
Does any portion of the project boundaries contain areas that should be
evaluated for wetland delineation or require a permit from the United States Army
Corps of Engineers?
The area where the proposed project improlements would occur is located on lands
that hate been improE]3d with wastewater treatment facilities. To determine the
presence of Wetland Waters, wetland delineation based on the Corps three parameter
approach was conducted in the location where the proposed improCements would
occur. These three parameters include; d othe presence of wetland Eegetation, t20the
presence of wetland hydrology and Xithe presence of hydric soils.
Vegetation: The locations where the proposed project improE13ments would occur does
not contain any wetland Eegetation species that would meet the wetland E19getation
parameter.
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Draft Initial Study/Mitigated Negative Declaration&CEgA-Plus Federal Consultation Review 5-15
Section 5
Hydrology: The only source of water to the study area would be seasonal rainfall. The
ground surface where the construction actidties would occur consists of compacted
soils or concrete that would not saturate with rainfall. The study area would not meet the
wetland hydrology parameter.
Hydric Soils: The study area soils consist of compacted fill material or concrete and
would not meet the hydric soil parameter.
Wetland Waters Determination
The study area lacks the reouired parameters that define Wetland Waters of the U.S. or
State. Therefore, the implementation of the proposed project would not adlersely
impact Wetland Waters of the U.S or State.
5.12 Wild and Scenic Rivers Act
Is any portion of the project located within a wild and scenic river?
❑x No. The project is not located near a wild and scenic ri[Br.
The study area is located in the Santa Ana Ricer Watershed. Within the Santa Ana
Ricer Watershed there are no Wild and Scenic Ricers. Therefore, the construction and
operation of the Water Production Enhancement Project would not result in ad-arse
impacts to any wild and scenic risers.
5.13 Safe Drinking Water Act, Sole Source Aquifer Protection
Is the project located in an area designated by the United States Environmental
Protection Agency, Region 9, as a Sole Source Aquifer?
❑x No. The project is not within the boundaries of a sole source aDuifer.
The closest sole source aDuifer to the study area would be Campo/Cotton Creek ADAfer
in San Diego County. Therefore, the construction and operation of the proposed project
would not result in ad Dame impacts to any sole source a_uifers.
5.14 Environmental Justice
Does the project involve an activity that is likely to be of particular interest to or
have particular impact upon minority, low-income, or indigenous populations, or
tribes?
ONo. Selecting [NoDmeans that this action is not likely to be of any particular interest
to or hale an impact on these populations or tribes. Explain.
The purpose of the proposed project is to prodde additional wastewater flows to OCWD
GWRS wastewater treatment site to produce additional water supplies to replenish the
Orange County Groundwater Basin to ensure that adeDuate amounts of groundwater
are aleilable to Orange County residents including IowGhcome households. By
1*1 Orange County Water District Water Production Enhancement Project
SJ Draft Initial Study/Mitigated Negative Declaration&CEgA-Plus Federal Consultation Review 5-16
Section 5
maintaining aden/ate amounts of groundwater supplies, less water would hale to be
imported into Orange County which is significantly higher in costs and which could hale
a higher economic impact on lower income households. The implementation of the
proposed project would increase groundwater supplies and would result in beneficial
fiscal impacts to Orange County residents including lower income households.
1*1 Orange County Water District Water Production Enhancement Project
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Section 6
SECTION 6.0 REFERENCES
California Department Fish and Game Natural DID3rsity Database, Accessed Dine
2015.
California Department of Transportation Scenic Highways Program Web Site Access,
September 2015.
California Endronmental Quality Act. 2015.
California Endronmental Quality Act, State CEQA Guidelines, 2015.
California Farmland Mapping Monitoring Program, Web Site Access September 2015.
California Geologic SurEby Seismic Hard Zone Map Newport Quadrangle, Accessed
September 2014.
California NatiEb Plant Society InEbntory of Rare and Endangered Plants Database,
Accessed [line 2015.
California Uniform Building Code, 2016
California Water Code, 2014.
City of Huntington Beach, General Plan, Web Access [line 2016
City of Huntington Beach Municipal Code, Web Access, Dine 2016
City of Huntington Beach Zoning code, Web Site Access, [lme 2016
County of Orange Congestion Management Program, Web Site Access Dine 2016
County of Orange Model Water Quality Management Plan, 2011.
County of Orange, 4� term municipal NPDES permit for Areawide Urban Storm Water
Runoff, 2014.
Endronmental Science Associates, Air Quality and Greenhouse Gas emission Report,
August 2016
Endronmental Science Associates, Cultural Resources Report, August 2016
Federal Transit Agency, Noise Associated with Typical construction ED/ipment, 1995.
Federal Transit Agency, Transit Noise and Vibration Assessment, 2006.
Cohn Wayne Airport Endrons Land Use Plan, 2014.
Mel[lIIe C. Branch and R. Dale Beland, Noise LelbIs and Human Response, 1970.
National Water Research Institute Santa Ana Ricer Water Quality and Health Study,
2004.
Orange County Water District Groundwater Management Plan, 2014.
Orange County Water District Water Production Enhancement Project
!:J Draft Initial Study/Mitigated Negative Declaration&CEQAfIUs Federal Consultation Review 6-1
Section 6
Orange County Water District Mounding Impact technical Memorandum, 2010 and
2011.
Regional Water Quality Control Board, Santa Ana Ricer Basin Plan, Canuary 1995.
U.S. Army Corps of Engineers List of Wetland Plants, 2008.
U.S. Army Corps of Engineers Regional Supplement to the Corps of Engineers Wetland
Delineation Manual Arid West Region, September 2008.
Orange County Water District Water Production Enhancement Project
!:J Draft Initial Study/Mitigated Negative Declaration&CEQAfIUs Federal Consultation Review 6-2
Appendix A
Air Quality and Greenhouse Gas Emissions Technical Report
ORANGE COUNTY WATER DISTRICT — WATER
PRODUCTION ENHANCEMENT PROJECT
Air Quality and Greenhouse Gas Emissions Technical Report
Prepared for July 2016
Orange County Water District
r ESA
J
ORANGE COUNTY WATER DISTRICT - WATER
PRODUCTION ENHANCEMENT PROJECT
Air Quality and Greenhouse Gas Emissions Technical Report
Prepared for July 2016
Orange county Water District
r ESA
J
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TABLE OF CONTENTS
Orange County Water District - Water Production Enhancement
Project
Air Quality and Greenhouse Gas Emissions Technical Report
Paae
Tableof Contents....................................................................................................................I
1. Executive Summary.........................................................................................................1
1.1 Introduction.....................................................................................................1
1.2 Project Background,Summary and Construction Phasing..............................2
1.4 Summary of Analysis Results...........................................................................3
1.4.1 Air Quality Impact Summary............................................................................3
1.4.2 GHG Impact Summary.....................................................................................4
1.4.1 NEPA Impact Summary....................................................................................4
2. Environmental Setting.....................................................................................................4
2.1 Climate and Meteorology................................................................................4
2.2 Federal and State Ambient Air Quality Standards...........................................5
2.3 Project Area Air Quality.................................................................................10
2.4 Sensitive Receptors........................................................................................10
2.6 Regulatory Setting.........................................................................................12
3. Climate Change Setting.................................................................................................16
3.1 Background on Greenhouse Gases and Climate Change...............................16
3.2 Greenhouse Gas Emissions Estimates...........................................................17
3.3 Regulatory Environment................................................................................18
4. CEQA Air Quality Impacts and Mitigation Measures.....................................................21
4.1 Methodology.................................................................................................21
4.2 Thresholds of Significance.............................................................................24
4.3 Project Impacts..............................................................................................27
5. CEQA GHG Impacts and Mitigation Measures..............................................................33
5.1 Methodology.................................................................................................33
5.2 Thresholds of Significance.............................................................................34
5.3 Project Impacts..............................................................................................36
6. NEPA Conformity Analysis.............................................................................................39
6.1 Methodology.................................................................................................39
6.2 Thresholds of Significance.............................................................................39
6.3 Project Impacts..............................................................................................40
7. References.....................................................................................................................41
Orange County Wafer Dlalad F Waer Nodudws Enhanmmen/Pmp E /1ENB"/
Nr Guelgy aM GmenMuse Gas EmSsbns Technical Repo Nly 2016
Appendix A: Air Quality and Greenhouse Gas Emissions Assumptions and Calculations
Appendix B: CalEEMod Output
Tables Page
TABLE 1 Ambient Air Quality Standards for Criteria Pollutants............................................7
TABLE 2 Air Quality Data Summary(2012—2014)For Project Area.................................. 11
TABLE 3 South Coast Air Basin Attainment Status............................................................... 12
TABLE 4 SCAQMD Regional Air quality Significance Thresholds......................................26
TABLE 5 SCAQMD Localized Significance Thresholds.......................................................26
TABLE 6 Anticipated Construction Schedule........................................................................28
TABLE 7 Proposed Regional Construction Emissions...........................................................29
TABLES Proposed project Operational Emissions................................................................30
TABLE 9 Proposed Project Unmitigated Localized daily Construction Emissions...............31
TABLE 10 Estimated Total Construction-Related GHG Emissions.........................................37
TABLE I l Estimated Construction and Operational Related GHG Emissions........................38
TABLE 12 De Minimis Emission Levels.................................................................................40
TABLE 13 SIP Conformity Evaluation....................................................................................41
Orange County Waler Dice ict n Water P udwa EManwanent Pmp II EM11f 7
Nr Guellly aM GreenMuse Gas Emasbne Technical Report NIy 2016
Orange County Water District - Water Production
Enhancement Project
Air Quality and Greenhouse Gas Emissions Technical Report
1. Executive Summary
1.1 Introduction
This technical report has been prepared to support the Orange County Water District(OCWD)'s
environmental review process and provide information regarding potential impacts to air quality
and climate change associated with the approval of the Effluent Flow Equalization Tank Project
(Project).The Project develops a secondary effluent flow equalization tank at the Orange County
Sanitation District(OCSD)Plant No.2 in order to receive the maximum water production at the
Groundwater Recharge System(G)ATRS)facility.OCSD's Plant No.2 is a wastewater treatment
facility which has varying influent(and effluent)flows of secondary effluent.During the day,
wastewater flows into OCSD's Plant No.2 can peak above 140 million gallons per day(MGD).
These peak flows cannot be pumped to the GWRS facility due to the limits of the conveyance
facilities,i.e. effluent pump station and pipeline; that deliver the secondary effluent to GWRS.
Therefore, a secondary effluent flow equalization tank has been proposed at OCSD's Plant No.2
to capture these peak flows during the day and store them in the 6-million gallon tank until
nighttime.During low flows at night,the flow equalization tank would drain into the effluent
pump station to supplement the low secondary effluent inflows and allow the GWRS to treat
these peak flows which would have otherwise been discharged to the ocean. This secondary
effluent flow equalization tank is expected to deliver an additional 6,000 acre-feet of secondary
effluent for treatment at the GWRS facility.
This report describes the existing air quality in the Project area, identifies applicable rules and
regulations,and evaluates potential short-and long-term air quality impacts associated with build
out of the Project.Additionally,this report also provides background information on greenhouse
gas(GHG)emissions and evaluates potential impacts associated with the Project's GHG
contributions.Furthermore,where applicable,measures to mitigate or minimize air pollutants and
GHG emissions associated with the Project are included. In addition,as the project is in support
of a CEQA Plus environmental analysis,a general conformity analysis is also included in the
evaluation.
Information used to prepare this analysis was obtained from the City of Huntington Beach
General Plan,City of Huntington Beach Energy Action Plan,and other sources.
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1.2 Project Background, Summary and Construction Phasing
1.2.1 Background
The GWRS is an advanced water treatment facility constructed by the OCWD and the OCSD that
supplements local water supplies by providing reliable,high quality source of treated water to
recharge the Orange County Groundwater Basin and to protect the Orange County Groundwater
Basin from seawater intrusion. The GWRS consists of three major components: an advanced
water purification facility and pumping stations,a major pipeline connecting the treatment
facilities to existing recharge basins and an existing seawater intrusion barrier.
The GWRS has been designed to be implemented in three construction phases.Phase I was
implemented and produced approximately 70,000 acre feet per year(AFY)of new water supplies
from 2008 through 2014. Phase 2 is currently operational and produces approximately 103,000
AFY new water supplies.
The Final EIR/EIS for the GWRS was based upon a full build-out treatment capacity of 120,000
AFY of new water supplies. However,the Final ERI/EIS did not contemplate receiving
wastewater flows from OCSD Plant 2 wastewater treatment facility site.With additional
wastewater flows from Plant 2,the total new water supplies would increase to 128,000 AFY.
1.2.2 Summary
The Water Production Enhancement Project involves three construction activities: 1)construction
of flow equalization tank,2)construction of a pump station,and 3)construction of conveyance
piping and flow meter vault.
A 6-million gallon(MG)flow equalization tank would be constructed at the north end of OCSD
Plant 2.The 6-MG tank would be a circular welded steel tank approximately 200-feet in diameter
and 30-feet tall from existing grade. The flow equalization tank would have a 4-pump(3 duty+ 1
standby)pump deep),approximately 500-linear feet of 36-inch diameter connection piping with a
meter vault(15-ft x 20-ft x 10-ft deep)connected to the operations of the tank.The pump station
would be housed in a 30-ft x 40-ft x 20-ft block wall building.
The site preparation work for the flow equalization tank,pump station,and pipeline/vault would
involve excavating and hauling approximately 1,000 cubic yards(CY)of soil. In addition to dirt
removal,an existing concrete parking lot would need to be demolished for the tank pad.For this
dirt excavation work,four dump trucks would be doing five round trips each over a period of 4
days to haul the dirt off site. For the demo work, Four dump trucks would be doing three round
trips each over a period of 14 days to haul the concrete/asphalt off site.
The flow equalization tank would be constructed on concrete piles.Approximately 30-piles
would be required for supporting the equalization tank. To construct the pilings, 12-inch diameter
holes would be drilled into the ground with an auger drill rig.Approximately 40 CY of dirt from
pile drilling activity would be removed.Once the pile drilling is completed,the rebut support
cages for the piles would be installed into the drilled holes with a crane.Approximately 40 CY of
concrete would be filled into the holes with the rebar and cured. The piles would be supporting a
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2-foot thick concrete pad matching the diameter of the tank. This equates to 2,330 CY of concrete
for the tank pad.The pump station and meter vault would also require approximately 100 CY of
concrete to construct these structural facilities.
Once the piles and concrete pad have been constructed,the steel tank would be assembled.A
crane and welding laborers would be required to weld the steel components of the tank together.
Once the tank is welded,the surface would be prepped for a base coat and finally painted.
While the tank is being assembled,the contractor would be equipping the pump station and meter
vault with the use of laborers,fork lifts and cranes. The construction equipment for the tank,
meter vault,flow diversion box and pump station would include;an excavator,crane,pile driller,
bull dozer,backhoe,compactor, dump trucks,concrete trucks,water truck,man lifts and fork
lifts. The mix of construction equipment and hours of operation for each of the phases,as well as
the daily haul trips and laborer estimates are provided in Appendix A.
1.2.3 Construction Phasing
The OCWD Water Production Enhancement Project would be implemented in five construction
phases beginning in August 2020 and concluding in December of 2022. The sequence of
construction activities is shown below.The sequence of construction activities is summarized
below and detailed in Appendix A.Activities IA, 1B,and 1 C will be constructed separately.
Activities 1D and 1 E will be constructed concurrently.
• 1A: Excavation,Hauling,Grading for Flow EQ Tank,Pump Station,Pipeline/Meter
Vault.
• 113: Construction of Piles for Flow EQ Tank.
• 1C: Concrete Pours for Flow EQ Tank Pad.
• 1D: Flow EQ Tank Assembly&Coating.
• 1E: Installation of pipeline and assembly of equipment for Flow EQ pump station and
meter vault
1.4 Summary of Analysis Results
1.4.1 Air Quality Impact Summary
AQ-1: The proposed Project would not conflict with or obstruct the implementation of the
applicable air quality plan.The Project impacts would be less than significant,and no
mitigation is required.
AQ-2: The proposed Project would not violate existing air quality standard during construction or
operational activities. Project impacts would be less than significant,and no mitigation is
required.
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AQ-3: The proposed Project would not expose sensitive receptors to substantial pollutant
concentrations. Proposed Project impacts would be less than significant,and no mitigation
is required.
AQ-4: The proposed Project would not create objectionable odors affecting a substantial number
of people. This impact is less than significant,and no mitigation is required.
AQ-5: The proposed Project would not result in cumulatively considerable increases in criteria
pollutants during construction or operational activities. Therefore the proposed Project
impacts with respect to cumulatively considerable increases of criteria pollutants would be
less than significant, and no mitigation is required.
1.4.2 GHG Impact Summary
GHG-1: The proposed Project would not generate greenhouse gas emissions,either directly or
indirectly,that would have a significant impact on the environment. The proposed Project
results in less than significant impacts,and no mitigation is required.
GHG-2: The proposed Project would not conflict with an applicable plan,policy,or regulation
adopted for the purposes of reducing GHG emissions.The proposed Project results in less
than significant impacts,and no mitigation is required.
1.4.1 NEPA Impact Summary
NEPA-L The proposed Project would be consistent with the SIP as indicated by emissions being
below the de minimis thresholds and therefore a detailed conformity analysis is not
warranted.No mitigation is required.
2. Environmental Setting
2.1 Climate and Meteorology
The Project site is located in the City of Huntington Beach,southeast of the corner of Baybreeze
Drive and Brookhurst Street and following the Santa Ana River trail south to the Pacific Coast
Highway. Huntington Beach is located within the South Coast Air Basin(SCAB),which is under
the jurisdiction of the South Coast Air Quality Management District(SCAQMD). The SCAB is a
6,600-square-mile coastal plain bounded by the Pacific Ocean to the southwest and the San
Gabriel, San Bernardino, and San Jacinto Mountains to the north and east.The SCAB includes
the non-desert portions of Los Angeles,Riverside, and San Bernardino Counties,and all of
Orange County.
The ambient concentrations of air pollutants are determined by the amount of emissions released
by sources and the atmosphere's ability to transport and dilute such emissions.Natural factors
that affect transport and dilution include terrain,wind,atmospheric stability,and sunlight.
Therefore, existing air quality conditions in the area are determined by such natural factors as
topography,meteorology, and climate, in addition to the meant of emissions released by existing
air pollutant sources.
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Atmospheric conditions such as wind speed,wind direction,and air temperature gradients interact
with the physical features of the landscape to determine the movement and dispersal of air
pollutants.The topography and climate of southern California combine to make the SCAB an
area of high air pollution potential.The SCAB is a coastal plain with connecting broad valleys
and low hills,bounded by the Pacific Ocean to the west and high mountains around the rest of the
perimeter. The general region lies in the semi-permanent high-pressure zone of the eastern
Pacific,resulting in a mild climate tempered by cool sea breezes with light average wind speeds.
The usually mild climatological pattern is disrupted occasionally by periods of extremely hot
weather,winter storms, or Santa Ana winds.During the summer months,a warm air mass
frequently descends over the cool,moist marine layer produced by the interaction between the
ocean's surface and the lowest layer of the atmosphere. The warm upper layer forms a cap over
the cool marine layer and inhibits the pollutants in the marine layer from dispersing upward.In
addition,light winds during the summer further limit ventilation.Furthermore, sunlight triggers
the photochemical reactions that produce ozone.
Based on past climate records from the Western Regional Climate Center(WRCC),the average
annual maximum temperature in the area is 68 degrees Fahrenheit(OF)and the average annual
minimum temperature is 550 F. The average precipitation in the area is about 11 inches annually,
occurring primarily from December through March(WRCC, 2016).
2.2 Federal and State Ambient Air Quality Standards
Ambient Air Quality Standards
Regulation of air pollution is achieved through both federal and state ambient air quality
standards and emission limits for individual sources of air pollutants.As required by the federal
Clean Air Act(CAA),the U.S.Environmental Protection Agency(USEPA)has identified criteria
pollutants and has established National Ambient Air Quality Standards(NAAQS)to protect
public health and welfare.NAAQS have been established for ozone(03),carbon monoxide(CO),
nitrogen dioxide(NOA sulfur dioxide(SOA particulate matter(PM10 and PMrs),and lead(Pb).
These pollutants are called`criteria"air pollutants because standards have been established for
each of them to meet specific public health and welfare criteria.
To protect human health and the environment,the USEPA has set"primary"and"secondary"
maximum ambient limits for each of the criteria pollutants.Primary standards were set to protect
human health,particularly sensitive receptors such as children,the elderly,and individuals
suffering from chronic lung conditions such as asthma and emphysema. Secondary standards
were set to protect the natural environment and prevent damage to animals,crops,vegetation,and
buildings.
Regional and Local
The NAAQS establish the level for an air pollutant above which detrimental effects to public
health or welfare may result.The NAAQS are defined as the maximum acceptable concentrations
that, depending on the pollutant,may not be equaled or exceeded more than once per year or in
some cases as a percentile of observations.California has generally adopted more stringent
ambient air quality standards for the criteria air pollutants(i.e.,California Ambient Air Quality
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Standards [CAAQS])and has adopted air quality standards for some pollutants for which there is
no corresponding national standard,such as sulfates,hydrogen sulfide,vinyl chloride, and
visibility-reducing particles. Both the national and State ambient air quality standards for
pollutants along with their associated health effects and sources are presented in Table 1.
Criteria Air Pollutants
The California Air Resources Board(CARB)and USEPA currently focus on criteria air
pollutants because they are the most prevalent air pollutants known to be injurious to human
health and extensive health-effects criteria documents are available about their effects on human
health and welfare.A general description of these pollutants is provided below.
Ozone
Ozone,the main component of photochemical smog,is primarily a summer and fall pollution
problem.Ozone is not emitted directly into the air,but is formed through a complex series of
chemical reactions involving other compounds that we directly emitted. These directly emitted
pollutants(also known as ozone precursors) include reactive organic gases(ROGs)or volatile
organic compounds(VOCs), and oxides of nitrogen(NOx). While both ROGs and VOCs refer to
compounds of carbon,ROO is a term used by CARB and is identified based on a list of carbon
compounds that exempts carbon compounds determined by CARB to be nonreactive.VOC is a
term used by the USEPA and is identified based on USEPA's separate list of exempted
compounds it identifies as having negligible photochemical reactivity. The time period required
for ozone formation allows the reacting compounds to spread over a large area,producing
regional pollution problems. Ozone concentrations are the cumulative result of regional
development patterns rather than the result of a few significant emission sources.
Once ozone is formed it remains in the atmosphere for one or two days. Ozone is then eliminated
through reaction with chemicals on the leaves of plants,attachment to water droplets as they fall
to earth("rainout),or absorption by water molecules in clouds that later fall to earth with rain
("washout').
Short-term exposure to ozone can irritate the eyes and cause constriction of the airways. In
addition to causing shortness of breath,ozone can aggravate existing respiratory diseases such as
asthma,bronchitis,and emphysema.
Carbon Monoxide
CO,a colorless and odorless gas,is a relatively non-reactive pollutant that is a product of
incomplete combustion and is mostly associated with motor vehicles. When inhaled at high
concentrations,CO combines with hemoglobin in the blood and reduces the oxygen-carrying
capacity of the blood. This results in reduced oxygen reaching the brain,heart and other body
tissues.This condition is especially critical for people with cardiovascular diseases, chronic lung
disease,or anemia. CO measurements and modeling were important in the early 1980s when CO
levels were regularly exceeded throughout California.In more recent yews,CO measurements
and modeling have not been a priority in most California air districts due to the retirement of
older polluting vehicles,lower emissions from new vehicles,and improvements in fuels.
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TABLET
AMBIENT AIR QUALITY STANDARDS FOR CRITERIA POLLUTANTS
Averaging State National Pollutant Health and
Pollutant Time Standard Standard Atmospheric Effects Major Pollutant Sources
Drone 1 hour 0.09 ppm mr High concentrations can directly Formed when ROG and NOx react in
8 boom 0.07 0.0]5 affect lungs,causing irritation. Me presence of sunlight.Major
ppm PPm Longhand exposure may cause sources include on road motor
damage to lung tissue. ehicles,edam a operation,and
commercial I industrial mobile
e uipment.
Carboy ihour 20ppm 35 ppm Clieiffil ass chemical Internal combustion engines,primarily
Manuel 8 home 9.0 9 asphyxiant,carbon monoxide gasollne�owered motor Ounces.Cot ppm ppm Interferes with the transfer of
fresh oxygen to the blood and
dapples;satellite tissues of
oxygen.
Nmogen ihour 0.18 ppm 0.100 ppm Irritating to eyes and respiratory Motor shales,petroleum refining
u0xda Annual 0.030 ppm 0.053 ppm Imct.Colors atmosphere reddish operations,industrial sources,alrcmtt,
(190) Arithmetic Mean brown. ships,and railroads.
SuWr ihour 0.25 ppm 75 ppb limbless upper respiratory tract; Fuel combustion,chemical plants,
news 3hoom min g.5g injurious to lung tissue.Can sulfur recotery plants,and metal
(SO.) firm yellow the leates of plants, processing.
24 hours 0.04 ppm 0.14 ppm destmdi@ to marble,iron,and
Annual min 0.03 m steel.Limits hill and reduces
Arithmetic Mean PP sunlight.
Respirable 2hours SO Val 15041 May irritate ayes and respiratory Dust and fomerproducing industrial
Particulate Annual 20 r'g/m° mr Imd,decreases in lung capacity, and agricultural operations,
After Arithmetic Mean cancer and Increased mortality. combustion,atmosphere
(pi Produces has and limits photochemical reactions,and natural
dslblllty. on Rise si.g.,Wind rated dust and
ocean spraysc
Fine 24 hours min 35 rSlms Increases respiratory disease, Fuel combustion in matar ehicles,
Particulate Annual 121T31ms 12 tghl lung damage,cancer,and a uipment,and industrial sources;
h§tter Arithmetic Mean premature death Red... residential and agricultural burning;
(I'M 5) Isibilay and results In surface Also,formed from photochemical
soiling, reactions of other pollutants,including
NOx,sulfur oxides,and organics.
Lead(Ph) 30 Day Areal 1.5 rglm' Disturbs gastrointestinal system, Present source:lead smelters,battery
Calendar min 1.5h and causes anemia,kidney manufacturing and recycling facilities.
Quarter ghss disease,and neuromuscular and Past source:combustion of leaded
neurological dysfunction W gasoline.
Rolling 3WoMh urn 0.15 alma serene cases.
Ateringe
I#ydrogm 1 hour 0.03 ppm No National Nuisance odor rotten agg smelly, Geothermal pourer plants,petroleum
some Standard headache and breathing production and refining
difficulties higher concentrations..
Sullates 24 hour 25 FWM3 No National Decrease In entilatory functions; Industrial processes.
(Sp) Standard aggro etion of asthmatic
symptoms,aggro ation of cardio
pulmonary disease, ¢gelation
damage;degradation of Isibility;
property damage.
Visbdrry 8hour Extinctionof No National Reduces isibility,reducelaigprt Sea PMza
RMucmg 0.23Ikm; Standard safety,lower real estate Blue,
Particles isibilityof and discourages tourism.
10 miles or
mom
NOTE:ppm pans par million;ppb pads per Nlllon;Fglma nmicrugrsme per cubic meter.
SOURCE:CARB,20091 CARE,2016a.
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Nitrogen Dioxide
NOi is a reddish-brown gas that is a by-product of combustion processes.Automobiles and
industrial operations are the main sources of NOz.Combustion devices emit primarily nitric oxide
(NO),which reacts through oxidation in the atmosphere to form NOz. The combined emissions of
NO and NOz are referred to as NOx,which me reported as equivalent NO2.Aside from its
contribution to ozone formation,NOz can increase the risk of acute and chronic respiratory
disease and reduce visibility.NOz may be visible as a coloring component of a brown cloud on
high pollution days,especially in conjunction with high ozone levels.
Sulfur Dioxide
SOz is a colorless,extremely irritating gas or liquid that enters the atmosphere as a pollutant
mainly as a result of burning high sulfur-content fuel oils and coal,and from chemical processes
occurring at chemical plants and refineries.When SOz oxidizes in the atmosphere,it fors sulfur
trioxide(SOA Collectively,these pollutants are referred to as sulfur oxides(SOx).
Major sources of SOz include power plants,large industrial facilities,diesel vehicles,and oil-
burning residential heaters.Emissions of SOz aggravate lung diseases,especially bronchitis. This
compound also constricts the breathing passages,especially in people with asthma and people
involved in moderate to heavy exercise. SOz potentially causes wheezing, shortness of breath,and
coughing. Long-ter SOz exposure has been associated with increased risk of mortality from
respiratory or cardiovascular disease.
Particulate Matter
PM10 and PMz 5 consist of particulate matter that is 10 microns or less in diameter and
2.5 microns or less in diameter,respectively(a micron is one-millionth of a meter).PM10 and
PM2,5 represent fractions of particulate matter that can be inhaled into the air passages and the
lungs and can cause adverse health effects.Acute and chronic health effects associated with high
particulate levels include the aggravation of chronic respiratory diseases,heart and lung disease,
and coughing,bronchitis and respiratory illnesses in children. Recent mortality studies have
shown an association between morbidity and mortality and daily concentrations of particulate
matter in the air.Particulate matter can also damage materials and reduce visibility.One common
source of PMz.5 is diesel exhaust emissions.
PM10 consists of particulate matter emitted directly into the air(e.g.,fugitive dust,soot,and
smoke from mobile and stationary sources,construction operations,fires,and natural windblown
dust)and particulate matter formed in the atmosphere by condensation and/or transformation of
SOz and ROG. Traffic generates particulate matter emissions through entrainment of dust and dirt
particles that settle onto roadways and parking lots. PM]0 and PM2,5 are also emitted by burning
wood in residential wood stoves and fireplaces and open agricultural burning. PM2.5 can also be
formed through secondary processes such as airborne reactions with certain pollutant precursors,
including ROGs, ammonia(NHA NOx,and SOx.
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Lead
Lead is a metal found naturally in the environment and present in some manufactured products.
There are a variety of activities that can contribute to lead emissions,which are grouped into two
general categories, stationary and mobile sources. On-road mobile sources include light-duty
automobiles; light-,medium-,and heavy-duty trucks; and motorcycles.
Emissions of lead have dropped substantially over the past 40 years.The reduction before 1990 is
largely due to the phase-out of lead as an anti-knock agent in gasoline for on-road automobiles.
Substantial emission reductions have also been achieved due to enhanced controls in the metals
processing industry. In the SCAB,atmospheric lead is generated almost entirely by the
combustion of leaded gasoline and contributes less than one percent of the material collected as
total suspended particulates. As lead has been well below regulatory thresholds for decades and
the Proposed Project is not a source of lead,lead is not discussed further in this analysis.
Toxic Air Contaminants
Concentrations of toxic air contaminants(TACs),or in federal parlance,hazardous air pollutants
(HAPs),are also used as indicators of ambient air quality conditions.A TAC is defined as an air
pollutant that may cause or contribute to an increase in mortality or in serious illness, or that may
pose a hazard to human health.TACs are usually present in minute quantities in the ambient air;
however,their high toxicity or health risk may pose a threat to public health even at low
concentrations.
According to CARB,the majority of the estimated health risk from TACs can be attributed to
relatively few compounds,the most important being particulate matter from diesel-fueled engines
(DPM)which represents 70 percent of the risk(CARB,2016b).DPM differs from other TACs in
that it is not a single substance,but rather a complex mixture of hundreds of substances.Although
diesel PM is emitted by diesel-fueled internal combustion engines,the composition of the
emissions varies depending on engine type,operating conditions,fuel composition,lubricating
oil,and whether an emission control system is present.
Unlike the other TACs,no ambient monitoring data me available for diesel PM because no
routine measurement method currently exists. However,CARB has made preliminary
concentration estimates based on a particulate matter exposure method.This method uses the
CARB emissions inventory's PM10 database,ambient PM,monitoring data,and the results from
several studies to estimate concentrations of DPM. In addition to DPM,the TACs for which data
are available that pose the greatest existing ambient risk in California are benzene, 1,3-butadiene,
acetaldehyde,carbon tetrachloride,hexavalent chromium,pans-dichlorobenzene,formaldehyde,
methylene chloride, and perchloroethylene.
Odorous Emissions
Odors are generally regarded as an annoyance rather than a health hazard. However,
manifestations of a person's reaction to foul odors can range from psychological(e.g.,irritation,
anger,or anxiety)to physiological(e.g.,circulatory and respiratory effects,nausea,vomiting,and
headache). Offensive odors are unpleasant and can lead to public distress generating citizen
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complaints to local governments.Although unpleasant,offensive odors rarely cause physical
harm. The occurrence and severity of odor impacts depend on the nature,frequency,and intensity
of the source,wind speed,direction,and the sensitivity of receptors.
2.3 Project Area Air Quality
Existing Air Quality
SCAQMD maintains monitoring stations within district boundaries that monitor air quality and
compliance with associated ambient standards. The Project site is located in the North Orange
County Coastal Air Monitoring Subregion. Currently,the nearest monitoring station to the study
area is the Costa Mesa—MesaVerde Drive Station(2850 Mesa Verde Dr East,Costa Mesa,CA).
This station monitors ambient concentrations of ozone,NOr,CO,and SOr,but does not monitor
PMz.s or PM16. The nearest monitoring station that monitors ambient concentrations of PMr.r and
PM16 is the Anaheim station located at 1630 W.Pampas Lane. Historical data of ambient ozone,
NO,,CO, SOr, PM,,and PMr.r concentrations from these monitoring stations for the most recent
three years(2012—2014)are shown in Table 2.
Both CARB and USEPA use this type of monitoring data to designate areas according to their
attainment status for criteria air pollutants. The purpose of these designations is to identify the
areas with air quality problems and thereby initiate planning efforts for improvement. The three
basic designation categories are nonattainment,attainment,and unclassified.Unclassified is used
in an area that cannot be classified on the basis of available information as meeting or not
meeting the standards. In addition,the California designations include a subcategory of
nonattainment-transitional,which is given to nonattainment areas that are progressing and nearing
attainment. The current attainment stams for the SCAB is provided in Table 3.
2.4 Sensitive Receptors
Sensitive receptors are individuals who are considered more sensitive to air pollutants than others.
The reasons for greater than average sensitivity may include pre-existing health problems,
proximity to emissions sources,or duration of exposure to air pollutants. Schools,hospitals,and
convalescent homes are considered to be relatively sensitive to poor air quality because children,
elderly people,and the infinn are more susceptible to respiratory distress and other air quality-
related health problems than the general public.Residential areas are considered sensitive to poor
air quality because people usually stay home for extended periods of time,with associated greater
exposure to ambient air quality. Recreational uses are also considered sensitive due to the greater
exposure to ambient air quality conditions because vigorous exercise associated with recreation
places a high demand on the human respiratory system.
Currently,the sensitive uses located in the Project site vicinity include residential uses directly
west of Brookhurst Street from the OCSD Plant 2. The closest residence is located approximately
260 feet(78 meters)from the construction area.
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TABLE2
AIR QUALITY DATA SUMMARY(2012-2014)FOR PROJECT AREA
Monitoring Data by Year
Pollutant Standards 2012 2013 2014
Omne-Costa Nksa
Highest l Hour A@rage.ppm 0.090 0.095 0.096
Days odir State Standard 0.09 ppm 2 1 1
Highest 8 Hour Adirage ppmi 0.076 0,083 0.079
Days odir National Standard 0.075 ppm 1 0 4
Days odir Slate Standard 0.070 ppm 1 2 6
Carbon hbnoxide-Costa NEsa
Highest 8 Hour A®rage.ppm 1.7 2 1.9
Days ci National Standard 9.0 ppm 0 0 0
Days odic Stale Standard 9.0 ppm 0 0 0
Nitrogen l2oxale-Cosm Aksa
Highest 1 Hour A[erage Ppi 0.0744 0.0757 0.061
Days odir National Standard 0.100 ppm 0 0 0
Days ooer State Standard 0.18 ppm 0 0 0
Annual Adimge Ppm❑ 0.0104 0.0116 0.011
Days o®r National Standard 0.053 ppm 0 0 0
Days odir Stale Standard 0.030 ppm 0 0 0
Sulfur Dioxide-Costa Nast
Highest 24 Hour AlErage rppm❑ 0.0062 0.0042 0.009
Days odir State Standard 0.04 ppm 0 0 0
Pariculate bLtter(PMo)-Anaheim
Highest 24 Hour A erege pglm'd 48 77 85
Days odir National Standard 150 µg1m' 0 0 0
arleasured®
Days odir State Standard 50 µg/m' 0 1 2
®rleasured®
Annual Adirage 4glm36 20 µg/m' 22.4 25.4 26.8
Particulate Aktter(Pi-Anaheim
Highest 24 Hour Adirage Uglm'@ 50.1 37.8 56.2
Days odir National Standard 35 µg/m3 4 1 6
0neasurell5
Annual A®rage rµglm'd 12 µg/m' 10.81 10.1 10.3
NOTES:
ppm npus per million:pyri carrerams per cubic meter.
-U Insufficient data a.stable to determine the slue.
a Generally,slate standards and national standards are net W be exceeded more than once per year.
b Concentrators and arB2ge5 represent federal Slat1360a.State and federal shames may differ because 0di erent Sampling methods.
Measurements are usually collected ersh,six days.Days o-er the standard represent the measured number of days that the standard
has been exceeded.
SOURCE:SCAQMD 2014,2013a,2012.
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TABLES
SOUTH COAST AIR BASIN ATTAINMENT STATUS
Attalmaent Status
Pollutant California Standards Federal Standards
Oran Eolreme Nonaltainmenl Se.ere Nonaltainmenl
CO Attainment Unclassifedl
Attainment
NOz Attainment Unclassifedl
Attainment
soo Attainment Attainment
PM10 Nonaltainmenl Attainment
PMis Nonaltainment Nonattainment
Lead Attainment Nonaltainment
SOURCE:CARE,2013a;USEPA,2016a.
2.6 Regulatory Setting
Federal
The principal air quality regulatory mechanism at the federal level is the CAA and in particular,
the 1990 amendments to the CAA and the NAAQS that it establishes.These standards identify
the maximum ambient(background)concentration levels of criteria pollutants that are considered
to be safe,with an adequate margin of safety,to protect public health and welfare.As discussed
previously,the criteria pollutants include owne,CO,NO2(which is a form of NOx), S02(which
is a form of SOx),PM10,PM2.5, and lead.
The CAA also requires each state to prepare an air quality control plan,referred to as a state
implementation plan(SIP).The CAA Amendments of 1990(CAAA)added requirements for
states with nonattainment areas to revise their SIPS to incorporate additional control measures to
reduce air pollution. The SIP is modified periodically to reflect the latest emissions inventories,
planning documents,and rules and regulations of the air basins,as reported by their jurisdictional
agencies. USEPA is responsible for reviewing all SIPS to determine whether they conform to the
mandates of the CAA and its amendments, and to determine whether implementing the SIPS will
achieve air quality goals.
The USEPA also has regulatory and enforcement jurisdiction over emission sources beyond state
waters (outer continental shelf),and those that are under the exclusive authority of the Federal
government, such as aircraft,locomotives, and interstate trucking.USEPA's primary role at the
state level is to oversee the state air quality programs.USEPA sets federal vehicle and stationary
source emissions standards and provides research and guidance in air pollution programs.
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General Conformity Rule
The General Conformity Rule(40 CFR Part 93)requires that federal agencies demonstrate that
federal actions conform with the applicable State Implementation Plan(SIP)in order to ensure
that federal activities do not hamper local efforts to control air pollution. The EPA general
conformity rate applies to federal actions occurring in nonattainment or maintenance areas when
the total direct and indirect emissions of nonattainment pollutants(or their precursors)exceed
specified thresholds.The de minimis emission thresholds are based on the attainment status of
each air basin. Since the Project is located in an air basin that is designated attainment for all
federal criteria pollutants,it is not subject to the General Conformity emissions thresholds.
State
California Air Resources Board(CARB)
CARB,a department of the California Environmental Protection Agency(Cal/EPA), oversees air
quality planning and control throughout California by administering the SIP. Its primary
responsibility lies in ensuring implementation of the 1989 amendments to the CCAA,responding
to the federal CAA requirements, and regulating emissions from motor vehicles sold in
California.It also sets fuel specifications to further reduce vehicular emissions.
The amendments to the CCAA establish CAAQS, and a legal mandate to achieve these standards
by the earliest practical date.These standards apply to the same criteria pollutants as the federal
CAA,and also include sulfates,visibility reducing particulates,hydrogen sulfide and vinyl
chloride.They are also generally more stringent than the federal standards.
CARB is also responsible for regulations pertaining to TACs.The Air Toxics"Hot Spots"
Information and Assessment Act was enacted in 1987 as a means to establish a formal air toxics
emission inventory risk quantification program.Assembly Bill(AB)2588, as amended,
establishes a process that requires stationary sources to report the type and quantities of certain
substances their facilities routinely release.
California Green Building Standard Code
In January 2010,the State of California adopted the 2010 California Green Building Standards
Code(CALGreen),which became effective in January 2011. Building off of the initial 2008
California Green Building Code,the 2010 CALGreen Code represents a more stringent building
code that requires,at a minimum,that new buildings and renovations in California meet certain
sustainability and ecological standards.The 2010 CALGreen Code has mandatory Green
Building provisions for all new residential buildings that are three stories or fewer(including
hotels and motels)and all new non-residential buildings of any size that are not additions to
existing buildings.
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Local
South Coast Air Quality Management District (SCAQMD)
Criteria Air Pollutants
SCAQMD attains and maintains air quality conditions in the SCAB through a comprehensive
program of planning,regulation,enforcement,technical innovation,and promotion of the
understanding of air quality issues.The clean air strategy of SCAQMD includes preparation of
plans for attainment of ambient air quality standards, adoption and enforcement of rules and
regulations concerning sources of air pollution,and issuance of permits for stationary sources of
air pollution. SCAQMD also inspects stationary sources of air pollution and responds to citizen
complaints;monitors ambient air quality and meteorological conditions; and implements
programs and regulations required by the CAA, CAAA,and CCAA.
Air Quality Management Plan
SCAQMD and the Southern California Association of Governments(SCAG)are responsible for
preparing the air quality management plan(AQMP),which addresses federal and state CAA
requirements.The AQMP details goals,policies,and programs for improving air quality in the
SCAB.
The 2012 AQMP was adopted by the SCAQMD Governing Board on December 12, 2012. The
purpose of the 2012 AQMP for the SCAB is to set forth a comprehensive and integrated program
that will lead the region into compliance with the federal 24-hour PMi_y air quality standard,and
to provide an update to the SCAB's commitment towards meeting the federal 8-hour ozone
standards(SCAQMD,2013b).The AQMP would also serve to satisfy recent USEPA
requirements for a new attainment demonstration of the revoked 1-hour ozone standard,as well
as a vehicle miles travelled(VMT)emissions offset demonstration.I Specifically, the AQMP
would serve as the official SIP submittal for the federal 2006 24-hour PMns standard,for which
USEPA has established a due date of December 14,2012.2 In addition,the AQMP updates
specific new control measures and commitments for emissions reductions to implement the
attainment strategy for the 8-hour ozone SIP.The 2012 AQMP sets forth programs which require
integrated planning efforts and the cooperation of all levels of government local,regional, state,
and federal. Currently,SCAQMD staff has already begun initiating an early development process
for the next AQMP.
SCAQMD Rules and Regulations
All projects are subject to SCAQMD rules and regulations in effect at the time of construction.
Specific rules applicable to the construction anticipated under the proposed Project would include
the following:
1 Although the federal 1-hour omne standard was revoked in 2005,the USEPA has proposed to require a new 1-hour
ozone attainment demonstration in the South Coast extreme ozone nonattainment area as a result of a recent on
decision. Although USEPA has replaced the 1-hour omne standard with a more health protective 8-hour standard,
the CAA anti-backsliding provisions require that California have approved plans for attaining the 1-hour standard.
2 Although the 2012 AQMP was approved by the SCAQMD Board on December 7,2012,the plan did not gel
submitted to the USEPA by December 14,2012 as it first required approval from CARB.The 2012 AQMP was
subsequently approved by CARB on January 25,2013,and as of February 13,2013 the plan has been submitted by
CARB to the USEPA.
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Rule 401—Visible Emissions.A person shall not discharge into the atmosphere from any single
source of emission whatsoever any air contaminant for a period or periods aggregating more than
three minutes in any 1 hour that is as dark or darker in shade as that designated No. 1 on the
Ringelmann Chart,as published by the United States Bureau of Mines.
Rule 402—Nuisance.A person shall not discharge from any source whatsoever such quantities
of air contaminants or other material that cause injury,detriment,nuisance,or annoyance to any
considerable number of persons or to the public,or that endanger the comfort,repose,health,or
safety of any such persons or the public, or that cause,or have a natural tendency to cause, injury
or damage to business or property.The provisions of this rule do not apply to odors emanating
from agricultural operations necessary for the growing of crops or the raising of fowl or animals.
Rule 403—Fugitive Dust.This rate is intended to reduce the amount of particulate matter
entrained in the ambient air as a result of anthropogenic(human-made)fugitive dust sources by
requiring actions to prevent,reduce, or mitigate fugitive dust emissions. Rule 403 applies to any
activity or human-made condition capable of generating fugitive dust.
Rule 1113—Architectural Coatings.No person shall apply or solicit the application of any
architectural coating within the SCAQMD with VOC content in excess of the values specified in
a table incorporated in the Rule.
Toxic Air Contaminants
At the local level, air pollution control or management districts may adopt and enforce CARB
control measures.Under SCAQMD Regulation XIV(Toxics and Other Non-Criteria Pollutants),
and in particular Rule 1401 (New Source Review), all sources that possess the potential to emit
TACs are required to obtain permits from SCAQMD. Permits may be granted to these operations
if they are constructed and operated in accordance with applicable regulations,including new
source review standards and air toxics control measures. SCAQMD limits emissions and public
exposure to TACs through a number of programs. SCAQMD prioritizes TAC-emitting stationary
sources based on the quantity and toxicity of the TAC emissions and the proximity of the
facilities to sensitive receptors.
The Air Toxics Control Plan(March 2000,revised March 26,2004)is a planning document
designed to examine the overall direction of SCAQMD's air toxics control program. It includes
development and implementation of strategic initiatives to monitor and control air toxics
emissions. Control strategies that are deemed viable and are within SCAQMD's jurisdiction will
each be brought to the SCAQMD Board for further consideration through the normal public
review process. Strategies that me to be implemented by other agencies will be developed in a
cooperative effort,and the progress will be reported back to the Board periodically.
In May 2015 the SCAQMD completed the Multiple Air Toxics Exposure Study IV(MATES IV)
(SCAQMD,2015a). MATES IV is a monitoring and evaluation study conducted in the SCAB
and is a follow up to previous air toxics studies.The study is a follow up to the 2008 MATES III
study and consists of several elements including a monitoring program,an updated emissions
inventory of toxic air contaminants,and a modeling effort to characterize risk across the SCAB
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(SCAQMD,2008a).The study focuses on the carcinogenic risk from exposure to air toxics
(SCAQMD,2008b).However,it does not estimate mortality or other health effects from
particulate exposures.MATES IV shows that the region around the project site area has an
estimated carcinogenic risk from between 560 per million near the coast to the south and 801 in a
million near Ellis Avenue at the north(SCAQMD,2015a). These model estimates were based on
monitoring data collected at 10 fixed sites within the SCAB.
3. Climate Change Setting
3.1 Background on Greenhouse Gases and Climate Change
"Global warning"and"global climate change"are the Lemma used to describe the increase in the
average temperature of the earth's near-surface air and oceans since the mid-20th century and its
projected continuation.According to the International Panel on Climate Change(IPCC)warming of
the climate system is now considered unequivocal(IPCC,2007).Natural processes and human
actions have been identified as the causes of this warning.The IPCC has concluded that variations
in natural phenomena such as solar radiation and volcanoes produced most of the warming from
pre-industrial times to 1950 and had a small cooling effect afterward.After 1950,increasing GHG
concentrations resulting from human activity such as fossil fuel burning and deforestation are
believed to be responsible for most of the observed temperature increase.Increases in GHG
concentrations in the earth's atmosphere are thought to be the main cause of human-induced climate
change.Certain gases in the atmosphere naturally trap heat by impeding the exit of solar radiation
that is reflected back into space after striking the earth. This is sometimes referred to as the
"greenhouse effect"and the gases that cause it are called"greenhouse gases."Some GHGs occur
naturally and are necessary for keeping the earth's surface inhabitable.However,increases in the
concentrations of these gases in the atmosphere during the last 100 years have decreased the amount
of solar radiation that is reflected back into space,intensifying the natural greenhouse effect and
increasing average global temperatures.
Carbon dioxide(CO2),methane(CHa),nitrous oxide(N20),hydrofluorocarbons(HFCs),
perfluorocarbons(PFCs),and sulfur hexafluoride(SFe)are the principal GHGs.When
concentrations of these gases exceed natural concentrations in the atmosphere,the greenhouse
effect may be intensified. COz,CHa and N20 occur naturally,and through human activity.
Emissions of COr are largely by-products of fossil fuel combustion,whereas CHo results from
off-gassing3 associated with agricultural practices and landfills. Other human-generated GHGs
include fluorinated gases such as SFCs,PFCs and SFe,which have much higher heat-absorption
potential than COr,and are byproducts of certain industrial processes.
COr is the reference gas for climate change because it is the predominant GHG emitted.The
effect that each of the aforementioned gases can have on global warming is a combination of the
mass of their emissions and their global warming potential(GWP). GWP indicates, on a pound-
for-pound basis,how much a gas contributes to global warming relative to how much warming
would be caused by the same mass of COr.For example,CHa and N20 are substantially more
potent GHGs than COz,with GWPs of 21 and 310 times that of COY respectively.
3 Off-gassing is defined as the release of chemicals under normal conditions of temperature and pressure.
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In emissions inventories,GHG emissions are typically reported in terns of pounds or metric tons
Of COr equivalents(CO2e).COze is calculated as the product of the mass emitted of a given GHG
and its specific GWP.While C114 and N2O have much higher GWPs than COz,CO2 is emitted in
such vastly higher quantities that it accounts for the majority of GHG emissions in COze,both
from residential/commercial developments and human activity in general.
Some of the potential effects in California of global warming may include loss in snow pack, sea
level rise,more extreme heat days per year,more high owne days,more forest fires,and more
drought years(CARB,2009b). Globally,climate change has the potential to impact numerous
environmental resources through potential,though uncertain,impacts related to future air
temperatures and precipitation patterns.The projected effects of global warming on weather and
climate are likely to vary regionally,but are expected to include the following direct effects
(IPCC,2001):
• Higher maximum temperatures and more hot days over nearly all land areas;
• Higher minimum temperatures,fewer cold days and frost days over nearly all land areas;
• Reduced diurnal temperature range over most land areas;
• Increase of heat index over land areas; and
• More intense precipitation events.
Also,there are many secondary effects that are projected to result from global warming, including
global rise in sea level,impacts to agriculture,changes in disease vectors,and changes in habitat
and biodiversity.While the possible outcomes and the feedback mechanisms involved are not
fully understood and much research remains to be done,the potential for substantial
environmental, social, and economic consequences over the long term may be great.
3.2 Greenhouse Gas Emissions Estimates
Global Emissions
According to the United Nations Framework Convention on Climate Change(UNFCCC),
worldwide emissions of GHGs in 2004 were approximately 30 billion tons of COie per yen
(UNFCCC,2012).This includes both ongoing emissions from industrial and agricultural sources,
but excludes emissions from land use changes.
U.S. Emissions
In 2009,the United States emitted about 6.7 billion metric tons of COze or about 21 metric tons per
year per person.Of the four major sectors nationwide—residential,commercial,industrial,and
transportation—transportation accounts for the highest fraction of GHG emissions(approximately
33 percent);these emissions are entirely generated from direct fossil fuel combustion(USEPA,
2011).
State of California Emissions
In California,the transportation sector is the largest emitter of GHGs,followed by electricity
generation.Emissions of CO2 are byproducts of fossil fuel combustion.Methane,a highly potent
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GHG,results from off-gassing(the release of chemicals from nonmetallic substances under ambient
or greater pressure conditions)and is largely associated with agricultural practices and landfills.
Nitrous oxide is also largely attributable to agricultural practices and soil management.The main
natural carbon dioxide sinks,or reservoirs,are plants,oceans,and soils.Plants grab carbon dioxide
from the atmosphere to use in photosynthesis;some of this carbon is transferred to soil as plants die
and decompose. The oceans are a major carbon storage system for carbon dioxide.Marine animals
also take up the gas for photosynthesis,while some carbon dioxide simply dissolves in the seawater.
California produced approximately 459 million gross metric tons of COze in 2012. Combustion of
fossil fuel in the transportation sector was the single largest source of California's GHG emissions
in 2012,accounting for 37 percent of total GHG emissions in the State.This sector was followed by
the industrial sector(22 percent)and the electric power sector(including both in-state and out-of-
state sources)(21 percent)(GARB,2014a).
3.3 Regulatory Environment
Federal
The federal CAA does not specifically regulate GHG emissions;however,the U.S. Supreme
Court has determined that GHGs are pollutants that can be regulated under the federal CAA.
There are currently no federal regulations that set ambient air quality standards for GHGs.
State
Executive Order 5-3-05
In 2005, in recognition of California's vulnerability to the effects of climate change,Governor
Schwarzenegger established Executive Order 5-3-05,which set forth a series of target dates by
which statewide emissions of GHGs would be progressively reduced,as follows:
• By 2010,reduce GHG emissions to 2000 levels;
• By 2020,reduce GHG emissions to 1990 levels; and
• By 2050,reduce GHG emissions to 80 percent below 1990 levels.
Assembly Bill 32—California Global Warming Solutions Act
California Assembly Bill 32(AB 32),the Global Warming Solutions Act of 2006,requires
CARB to establish a statewide GHG emissions cap for 2020 based on 1990 emission levels.
AB 32 required CARR to adopt and enforce programs and regulations that identify and require
selected sectors or categories of emitters of GHGs to report and verify their statewide GHG
emissions. In December 2007 CARB adopted 427 MT COie as the statewide GHG emissions
limit equivalent to the statewide levels for 1990. This is approximately 28 percent below
forecasted 2020"business-as-usual"emissions of 596 MMT of COze,and about 10 percent below
average annual GHG emissions during the period of 2002 through 2004(CARB,2009b).
CARB published the Expanded List of Early Action Measures To Reduce Greenhouse Gas
Emissions In California Recommended For Board Consideration in September 2007(CARB,
2007). CARB adopted nine Early Action Measures for implementation,including Ship
Electrification at Ports, Reduction of High Global-Warming-Potential Gases in Consumer
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Products,Heavy-Duty Vehicle Greenhouse Gas Emission Reduction(Aerodynamic Efficiency),
Reduction of Perfluorocarbons from Semiconductor Manufacturing,Improved Landfill Gas
Capture,Reduction of Hydrofluorocarbon-134a from Do-It-Yourself Motor Vehicle Servicing,
Sulfur Hexaflouride Reductions from the Non-Electric Sector,a Tire Inflation Program,and a
Low Carbon Fuel Standard.
As of January 1, 2012,the GHG emissions limits and reduction measures adopted in 2011 by
CARB became enforceable. In designing emission reduction measures,CARB must aim to
minimize costs,maximize benefits, improve and modernize California's energy infrastructure,
maintain electric system reliability,maximize additional environmental and economic co-benefits
for California, and complement the state's efforts to improve air quality.
Climate Change Scoping Plan
In December 2008,CARB approved the AB 32 Scoping Plan outlining the state's strategy to
achieve the 2020 GHG emissions limit(CARB,2009b). This Scoping Plan,developed by CARB
in coordination with the Climate Action Team(CAT),proposes a comprehensive set of actions
designed to reduce overall GHG emissions in California,improve the environment,reduce
dependence on oil,diversify California's energy sources,save energy,create new jobs,and
enhance public health.
As required by AB 32,the Scoping Plan must be updated at least every five years to evaluate the
mix of AB 32 policies to ensure that California is on track to meet the targets set out in the
legislation. In October 2013,a draft Update to the initial Scoping Plan was developed by CARS
in collaboration with the California Climate Action Team(CCAT). The draft Update builds upon
the initial Scoping Plan with new strategies and expanded measures,and identifies opportunities
to leverage existing and new funds to drive GHG emission reductions through strategic planning
and targeted program investments. The draft Update to the initial Scoping Plan was presented to
CARB's Board for discussion at its February 20,2014 meeting. Subsequently,the first update to
the AB 32 Scoping Plan was approved on May 22,2014 by CARB.
As part of the proposed update to the Scoping Plan,the emissions reductions required to meet the
2020 statewide GHG emissions limit were further adjusted.The primary reason for adjusting the
2020 statewide emissions limit was based on the fact that the original Scoping Plan relied on the
Intergovernmental Panel on Climate Change's(IPCC) 1996 Second Assessment Report(SAR)to
assign the global warming potentials(GWPs)of greenhouse gases.Recently, in accordance the
United Nations Framework Convention on Climate Change(UNFCCC),international climate
agencies have agreed to begin using the scientifically updated GWP values in the IPCC's Fourth
Assessment Report(AR4)that was released in 2007.Because CARB has begun to transition to
the use of the AR4 I00-year GWPs in its climate change programs,CARS recalculated the
Scoping Plan's 1990 GHG emissions level with the AR4 GWPs.As the recalculation resulted in
431 MMTCOre,the 2020 GHG emissions limit established in response to AB 32 is now slightly
higher than the 427 MMTCOre in the initial Scoping Plan.Considering that the proposed update
also adjusted the 2020 BAU forecast of GHG emissions to 509 MMTCOie,a 15 percent
reduction below the estimated BAU levels was determined to be necessary to return to 1990
levels by 2020(CARB, 2014b).
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Executive Order 5-1-07
Executive Order 5-1-07,which was signed by Governor Schwarzenegger in 2007,proclaims that
the transportation sector is the main source of GHG emissions in California.It establishes a goal
to reduce the carbon intensity of transportation fuels sold in California by at least 10 percent by
2020. As a result of this order,CARB approved a proposed regulation to implement the low
carbon fuel standard(LCFS)on April 23,2009,which will reduce GHG emissions from the
transportation sector in California by about 16 MMT in 2020.The LCFS is designed to reduce
California's dependence on petroleum,create a lasting market for clean transportation
technology,and stimulate the production and use of alternative, low-carbon fuels in California.
The LCFS is designed to provide a durable framework that uses market mechanisms to spur the
steady introduction of lower carbon fuels.The framework establishes performance standards that
fuel producers and importers must meet each year beginning in 2011.
Senate Bill 375
SB 375,which establishes mechanisms for the development of regional targets for reducing
passenger vehicle greenhouse gas emissions,was adopted by the State on September 30,2008.
On September 23,2010,California ARB adopted the vehicular greenhouse gas emissions
reduction targets that had been developed in consultation with the metropolitan planning
organizations(MPOs);the targets require a 7 to 8 percent reduction by 2020 and between 13 to
16 percent reduction by 2035 for each MPO. SB 375 recognizes the importance of achieving
significant greenhouse gas reductions by working with cities and counties to change land use
patterns and improve transportation alternatives. Through the SB 375 process,MPOs, such as the
Southern California Council of Governments(SCAG)will work with local jurisdictions in the
development of sustainable communities strategies(SCS)designed to integrate development
patterns and the transportation network in a way that reduces greenhouse gas emissions while
meeting housing needs and other regional planning objectives. SCAG's reduction target for per
capita vehicular emissions is 8 percent by 2020 and 13 percent by 2035 (CARB 2010).The
MPOs will prepare their first SCS according to their respective regional transportation plan(RTP)
update schedule with the SCAG RTP/SCS adopted on April 4,2012.
Senate Bill 97
Senate Bill(SB)97,enacted in August 2007,required the Office of Planning and Research(OPR)
to develop guidelines for the mitigation of GHG emissions,or the effects related to releases of
GHG emissions. On April 13,2009,the OPR submitted proposed amendments to the Natural
Resources Agency in accordance with SB 97 regarding analysis and mitigation of GHG
emissions.As directed by SB 97,the Natural Resources Agency adopted Amendments to the
CEQA Guidelines for greenhouse gas emissions on December 30,2009. On February 16,2010,
the Office of Administrative Law approved the Amendments,and filed them with the Secretary
of State for inclusion in the California Code of Regulations. The Amendments became effective
on March 18, 2010.
California Green Building Standard Code
In early 2013 the California Building Standards Commission adopted the 2013 California
Building Standards Code that also included the latest 2013 CALGreen Code,which became
effective on January 1,2014.The mandatory provisions of the code are anticipated to reduce 3
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MMT of GHG emissions by 2020,reduce water use by 20 percent or more,and divert 50 percent
of construction waste from landfills.The 2013 California Energy Code(Title 24,Part 6),which is
also part of the CALGreen Code(Title 24,Part 11,Chapter 5.2),became effective on July 1,
2014.
Local
South Coast Air Quality Management District(SCAQMD)
As a method for determining significance under CEQA, SCAQMD developed a draft tiered
flowchart in 2008 for determining significance thresholds for GHGs for industrial projects where
SCAQMD is acting as the lead agency. In December 2008, SCAQMD adopted a 10,000
MTCOre/year for industrial facilities,but only with respect to projects where SCAQMD is the
lead agency. SCAQMD has not adopted a threshold for residential or commercial projects at the
time of this writing.
The SCAQMD flowchart uses a tiered approach in which a proposed project is deemed to have a
less than significant impact related to GHG emissions when any of the following conditions are met:
• GHG emissions are within GHG budgets in an approved regional plan;
• Incremental increases in GHG emissions due to the project are below the defined
Significance Screening Levels,or Mitigated to Less than the Significance Screening
Level;
• Performance standards are met by incorporating project design features and/or
implementing emission reduction measures; and
• Carbon offsets are made to achieve target significance screening level.
4. CEQA Air Quality Impacts and Mitigation Measures
This section describes the impact analysis relating to air quality under CEQA for the proposed
Project. It describes the methods and applicable thresholds used to determine the impacts of the
proposed Project on the environment.
4.1 Methodology
Criteria Pollutants
This technical report focuses on the nature and magnitude of the change in the air quality
environment due to implementation of the proposed Project. Air pollutant emissions associated
with the proposed Project would result from the construction and operation of the facility
expansion.
Construction activities would generate air pollutant emissions at the Project site and on roadways
resulting from construction-related traffic.The net increase in emissions generated by these
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activities and other secondary sources have been estimated and compared to the applicable
thresholds of significance recommended by SCAQMD.
Operational emission sources that would occur subsequent to the expansion include the increased
electrical usage for expanded facilities. It is assumed that there would be one new employee and
therefore minor new mobile source emissions or water consumption(process or employee use).
Based on the size of the buildings to house the pump station,it is estimated that increased
electrical consumption would be 13,860 kwh/year. Solid waste generation was based on the size
of the facility expansion and is estimated at 0.7 tons per year.Mobile source emissions will result
in both criteria and GHG emissions whereas electrical consumption,water consumption and solid
waste and wastewater generation are only applicable to the GHG analysis.
Construction Impacts
Short-term construction-generated emissions of criteria air pollutants and ozone precursors
associated with the proposed Project were modeled using emission factors taken from the
California Emissions Estimator Model(CalEEMod),Version 2013.2.2. Calculated emissions
from construction activities were used to determine whether short-term construction-related
emissions of criteria air pollutants associated with the proposed Project would exceed
SCAQMD's applicable regional thresholds and whether mitigation would be required.Modeling
was based on Project-specific data provided by the applicant.Modeling input and output files are
provided in Appendix A and B of this report respectively.
In addition,to determine whether or not construction activities associated with the proposed
Project would create significant adverse localized air quality impacts on nearby sensitive
receptors,the worst-case daily emissions contribution from the proposed Project were compared
to SCAQMD's localized significance thresholds(LSTs). The LSTs developed by SCAQMD are
based on the pounds of emissions per day that can be generated by a project without causing or
contributing to adverse localized air quality impacts,and only applies to the following criteria
pollutants: CO,NOx,PMIG,and PMzs.The analysis of localized air quality impacts focuses only
on the on-site activities of a project, and does not include emissions that are generated offsite
such as from on-road haul or delivery truck trips(SCAQMD,2003).
For the purpose of analyzing localized air quality impacts,SCAQMD has developed LSTs for
one-acre,two-acre,and five-acres.The LSTs established for each of the aforementioned site
acreages represent the amount of pollutant that can be emitted such that the most stringent
applicable federal or State ambient air quality standards would not be exceeded.Because of the
way the CalEEMod model estimates soil disturbance,the SCAQMD has developed a process by
which to determine acreage of disturbance per day based on the equipment usage. As the acreage
of the Project site disturbance is anticipated to be less than one acre,the LSTs for a one-acre site
are used to determine whether localized air quality impacts on nearby sensitive receptors would
result from the Project's on-site construction emissions.Under conditions where the Project's on-
site construction emissions implementing all appropriate mitigation would exceed the LSTs for a
one-acre site,air dispersion modeling of the Project's construction emissions would be required
to evaluate the potential localized air quality impacts of the proposed Project on its surrounding
off-site sensitive receptors,in accordance with SCAQMD's recommendation. However,under
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conditions where it is determined that the Project's peak daily construction emissions,with or
without mitigation,would not exceed the LSTs for a one-acre site,then it can be concluded that
the Project's construction emissions would not result in any adverse localized air quality impacts
on its surrounding off-site sensitive receptors.
In conducting the localized air quality analysis,which focuses only on on-site emissions,the
Project's on-site construction emissions generated from combustion sources(e.g.,off-road
construction equipment)under a worst-case construction scenario are evaluated against the LSTs.
The daily total on-site combustion,and fugitive dust emissions associated with each Project
construction phase(as well as construction phase overlaps where appropriate)were evaluated
against SCAQMD's LSTs for a one-acre site°. The LSTs were evaluated for the closest receptors
which are the single-family residential homes located approximately 260 feet(78 meters)from
the construction area directly across Brookhurst Street.
Operational Impacts
Long-term(i.e., operational)regional emissions of criteria air pollutants and precursors associated
with the proposed Project,were quantified using the CalEEMod computer model. Project
operations are anticipated to increase employees by one. Therefore,operational emissions
associated with criteria pollutants for the Project include water usage,wastewater and solid waste
generation,and mobile source emissions from the new employee. While additional pumps are
being added,these are electric and therefore do not result in direct emissions of criteria pollutants.
The resulting increase in long-term operational emissions was compared with the applicable
SCAQMD thresholds for determination of significance. Additionally,localized emissions from
operation were compared to the LSTs for a I acre site(as emissions would occur from an area
that is less than one acre)at 50 meters because the nearest sensitive receptors to the new tank are
located 78 meters directly across Brookhurst Street and the LSTs thresholds are provided for 25,
50, 100,200 and 1000 meters.
CO Hotspots
Historically,qualitative screening procedure provided in the procedures and guidelines contained
in Transportation Project-Level Carbon Monoxide Protocol(the Protocol)were used to determine
whether a project poses the potential for a CO hotspot(OCD ITS, 1997).According to the
Protocol,projects may worsen air quality if they increase the percentage of vehicles in cold start
modes by two percent or more; significantly increase traffic volumes(by five percent or more)
over existing volumes;or worsen traffic flow,defined for signalized intersections as increasing
average delay at intersections operating at level of service(LOS)E or F or causing an intersection
that would operate at LOS D or better without the project,to operate at LOS E or F.
As shown in Table 2,CO levels in the project area are substantially below the federal and state
standards. Maximum CO levels in recent years are 2 plan(eight-hour average)compared to the
threshold 9.0 ppm.Carbon monoxide decreased dramatically in the SCAB with the introduction
of the catalytic converter in 1975.No exceedances of CO have been recorded at monitoring
4 Although some construction sub phases are less than a one acre site,the SCAQMD methodology identifies the 1
acre thresholds as applicable for identifying risks for sites that are one acre or less.
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stations in the Air Basin for some time, and the Basin is currently designated as a CO attainment
area for both the CAAQS and NAAQS.
The SCAQMD conducted CO modeling for the 2003 AQMP for the four worst-case intersections
in the Air Basin. These include: (a)Wilshire Boulevard and Veteran Avenue;(b)Sunset
Boulevard and Highland Avenue;(c)La Cienega Boulevard and Century Boulevard;(d)Long
Beach Boulevard and Imperial Highway.In the 2003 AQMP,the SCAQMD notes that the
intersection of Wilshire Boulevard and Veteran Avenue is the most congested intersection in Los
Angeles County,with an average daily traffic volume of about 100,000 vehicles per day.5 This
intersection is located near the on-and off-ramps to Interstate 405 in West Los Angeles. The
evidence provided in Table 4-10 of Appendix V of the 2003 AQMP shows that the peak modeled
CO concentration due to vehicle emissions at these four intersections was 4.6 ppm(one-hour
average)and 3.2 (eight-hour average)at Wilshire Boulevard and Veteran Avenue.6 When added
to the existing background CO concentrations,the screening values would be 8.7 ppm(one-hour
average)and 5.6 ppm(eight-hour average).
As the Project would result in up to 3 new trips per day,the Project would not have the potential
to increase daily traffic in the area to levels that would result in a CO hotspot,and therefore,no
further evaluation of CO hotspots are discussed in the analysis.
Toxic Air Contaminants
TAC generators located within the SCAB are associated with diesel fueled vehicles and specific
types of facilities such as dry cleaners,gas stations, distribution centers,and ports.As there are no
onsite sources of TACs during operation, and because of the limited duration and area of
construction activities,TAC emissions are discussed qualitatively.
4.2 Thresholds of Significance
Based on the state CEQA Guidelines,a project would have a significant adverse effect on air
quality resources if it would:
• Conflict with or obstruct implementation of the applicable air quality plan;
• Violate any air quality standard or contribute substantially to an existing or projected air
quality violation;
• Expose sensitive receptors to substantial pollutant concentrations;
• Create objectionable odors affecting a substantial number of people; or
• Result in a cumulatively considerable net increase of any criteria pollutant for which the
project region is non-attainment under an applicable federal or state ambient air quality
standard(including releasing emissions which exceed quantitative thresholds for ozone
precursors);
5 South Coast Air Quality Management District,2003 Air Quality Management Plan,Appendix V:Modeling and
Attainment Demonstrations,(2003)V4-24.
6 The eight-hour average is based on a 0.7 persistence factor,as recommended by the SCAQMD.
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The OCWD and the City of Huntington Beach have not developed specific air quality thresholds
for air quality impacts.However, as stated in Appendix G of the CEQA Guidelines,the significance
criteria established by the applicable air quality management or air pollution control district may be
relied upon to make the above determinations.As such,the significance thresholds and analysis
methodologies in SCAQMD's CEQA Air Quality Handbook are used in evaluating project impacts.
SCAQMD has established daily mass thresholds for regional pollutant emissions,which are shown
in Table 4.
Aside from regional air quality impacts,projects in the SCAB are also required to analyze local
air quality impacts. As discussed previously, SCAQMD has developed LSTs that represent the
maximum emissions from a project that are not expected to cause or contribute to an exceedance
of the most stringent applicable federal or state ambient air quality standards,and thus would not
cause or contribute to localized air quality impacts. LSTs are developed based on the ambient
concentrations of that pollutant for each of the 38 source receptor areas(SRAs)in the SCAB.The
localized thresholds,which are found in the mass rate look-up tables in SCAQMD's Final
Localized Significance Threshold Methodology document,were developed for use on projects
that are less than or equal to five acres in size and are only applicable to the following criteria
pollutants: NOx,CO,PM]e,and PM2.5. The construction and operational LSTs for a one-acre site
in SRA 18(North Costal Orange County),which is where the Project site is located,are shown in
Table 5.
It should be noted that with regards to NOx emissions,the two principal species of NOx are NO
and NO,with the vast majority(95 percent)of the NOx emissions being comprised of NO.
However,because adverse health effects are associated with NOz,not NO,the analysis of
localized air quality impacts associated with NOx emissions is focused on NOz levels. For
combustion sources,SCAQMD assumes that the conversion of NO to NOz is complete at a
distance of 5,000 meters from the source.
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TABLE4
SCAQMD REGIONAL AIR QUALITY SIGNIFICANCE THRESHOLDS
Mass Daily Thresholds(lbs/day)
Pollutant Construction Operations
Oxides of Nitrogen 11 100 55
Reactis Organic Gases POGO 75 55
Respirable Particulate Matter PMji 150 150
Fine Particulate Matter Plii 55 55
Oxides of Sulfur SOx0 150 150
Carbon Monoxide ECOO 550 550
TACs 1rcluding carcinogens and Maximum Incremental Cancer Risk
non Carcinogens a 10 in 1 million
Cancer Burden
>0.5 excess Cancer cases(in areas i 1 in 1 million)
Chronic O Acute Hard Index
a 1.0(project increment)
' As the proposed Troiect workhatin al a the be a lopment fany major lead emissions souRes.lead
a flunions..to not be amly ed further.,this repmL
SOURCE:SCACIMD 20151a
TABLES
SCAQMD LOCALIZED SIGNIFICANCE THRESHOLDS
one-Acre Site
Allowable emissions(poundslday)as a function of receptor
distance(het)from site boundary
Pollutant Monitored Within SRA 18—
North Coastal Orange County 25(m) 50(m) 10( (m) 200(m) 500(m)
Construction Thresholds
Nitrogen Oxides @l0„d 92 93 108 140 219
Carbon Monoxide COO 647 738 1,090 2,096 6,841
Respirable Particulate Matter PMtr0 4 13 27 54 135
Fine Particulate Matter PM2.50 3 5 9 22 76
Operational Thresholds
Nitrogen Oxides CJO„d 92 93 108 140 219
Carbon Monoxide COO 647 738 1,090 2.096 6,841
Respirable Particulate Matter PM,,O 1 4 7 13 33
Fine Particulate Matter PMzs 1 2 3 6 19
' The lccali ad thresholds listed for NOx in this table take into consideration the gradual con ersion of NOW Ni analysis of
locate M air rally Impacts associated with NOx emissions focuses on NOs le els as they are associated with ad areahealth efleda.
SOURCE: SCAOMD,2003 Re iced 2009.
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4.3 Project Impacts
AQ- 1 Consistency with Applicable Air Quality Plan
The proposed Project would not conflict with or obstruct the implementation of the applicable
air quality plan. The Project impacts would be less than significant and no mitigation is
required
The proposed Project is located within the SCAB,which is under the jurisdiction of the
SCAQMD. As such, SCAQMD's 2012 AQMP is the applicable air quality plan for the proposed
Project.Projects that are consistent with the regional population,housing, and employment
forecasts identified by SCAG are considered to be consistent with the AQMP growth projections,
since the forecast assumptions by SCAG forms the basis of the land use and transportation
control portions of the AQMP.Additionally,because SCAG's regional growth forecasts are
based upon,among other things,land uses designated in general plans,a project that is consistent
with the land use designated in a general plan would also be consistent with the SCAG's regional
forecast projections,and thus also with the AQMP growth projections.
The proposed Project implements a temporary water storage tank to support the expansion of the
GWRS but will only increase the employment by at most one employee and therefore does not
increase the number ofjobs significantly or in excess of growth anticipated within the 2012
AQMP.Nor does the Project result in the creation of new housing or potential residential growth.
Because the land use will not change, and bas been in operation since before the creation of the
2012 AQMP,the proposed Project would not change the regional growth forecasts as identified
in the local General Plan or those of the 2012 AQMP. Therefore,the proposed Project would not
conflict with,or obstruct,implementation of the AQMP, and this impact would be less than
significant.
AQ-2 Violation of Air Quality Standards
The proposed Project would not violate existing air quality standard during construction or
operational activities.Project impacts would be less than significant,and no mitigation is
required
Construction
The proposed Project develops a secondary effluent flow equalization tank at OCSD Plant No. 2
in order to receive the maximum water production at the GWRS facility as detailed in Section 1
above. Construction activities associated with the proposed Project would generate pollutant
emissions from the following construction activities: (1)site preparation,grading, and
excavation;(2)construction workers traveling to and from Project site; (3)delivery and hauling
of construction supplies to,and debris from,the Project site; (4)fuel combustion by on-site
construction equipment; (5)tank and building construction and the application of architectural
coatings.These construction activities would temporarily create emissions of dust,fumes,
equipment exhaust,and other air contaminants.The amount of emissions generated on a daily
basis would vary,depending on the intensity and types of construction activities occurring
simultaneously.
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Construction of proposed Project is anticipated to occur between August 2020 and December
2022 with various phases occurring over different time periods. The construction phases and their
estimated duration are shown in Table 6. Construction activity would be limited to 7:00 A.M.to
7:00 P.M.Monday through Friday and Saturdays where necessary from 8:00 A.M.to 5:00 P.M.
Construction would occur over a portion of the OCSD site,with a maximum of 1.5-acre7 of the
Project site being graded on a peak construction day.
TABLE6
ANTICIPATED CONSTRUCTION SCHEDULE
Phase Description Stan nnorahtyear)
Start Finish
1A Exca EntionlSite PreplPipeline Sep 2020 Dec 2020
1B Tank Piles Dan 2021 April 2021
1C Tank Pad May 2021 Aug 2021
1D Assembly❑Coating of Steel Tank Sep 2021 Dec 2021
1E Edipping Sep 2021 Dec 2021
Sea Appandlx 8 Wr NII schedule.
Construction emissions are considered short term and temporary,but have the potential to
represent a significant impact with respect to air quality. Particulate matter(i.e.,PM10 and PM2.5)
are among the pollutants of greatest localized concern with respect to construction activities.
Particulate emissions from construction activities can lead to adverse health effects and nuisance
concerns,such as reduced visibility and soiling of exposed surfaces. Particulate emissions can
result from a variety of construction activities,including excavation,grading, demolition,vehicle
travel on paved and unpaved surfaces, and vehicle and equipment exhaust. Construction
emissions of PM can vary greatly depending on the level of activity,the specific operations
taking place,the number and types of equipment operated, local soil conditions,weather
conditions,and the amount of earth disturbance.
Emissions of ozone precursors ROG and NOx are primarily generated from mobile sources and
vary as a function of vehicle trips per day associated with debris hauling,delivery of construction
materials,vendor trips,and worker commute trips,and the types and number of heavy-duty, off-
road equipment used and the intensity and frequency of their operation.A large portion of
construction-related ROG emissions also result from the application of architectural coatings and
vary depending on the amount of coatings applied each day.
It is mandatory for all construction projects in the SCAB to comply with SCAQMD Rule 403 for
controlling fugitive dust. Incorporating Rule 403 into the proposed Project reduces regional PM10
and PMr,s emissions from construction activities. Specific Rule 403 control requirements include,
but me not limited to,applying water in sufficient quantities to prevent the generation of visible
dust plumes,applying soil binders to uncovered areas,reestablishing ground cover as quickly as
7 Ground disturbance for grading is based on the equipment used and not the area of the site.Disturbance takes into
account depth as well as surface area.
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possible,utilizing a wheel washing system to remove bulk material from tires and vehicle
undercarriages before vehicles exit the proposed Project site,covering all trucks hauling soil with
a fabric cover and maintaining a freeboard height of 12 inches,and maintaining effective cover
over exposed areas. Compliance with Rule 403 was accounted for in the construction emissions
modeling.
Table 7 summarizes the modeled peak daily emissions of criteria air pollutants and ozone
precursors associated with the proposed Project for each individual phase as well as for overlaps
where construction of different phases occurs at the same time. For the project's construction,
OCWD provided the full inventory of the equipment that would be used during the peak day for
each of the construction phase.
As shown in Table 7,the maximum daily construction emissions generated by the proposed
Project's worst-case construction scenario would not exceed SCAQMD's daily significance
threshold for any criteria pollutant and therefore would result in less than significant impacts.No
mitigation is required.
TABLE 7
PROPOSED REGIONAL CONSTRUCTION EMISSIONS
Estimated Maximum Daily Emissions(lbsiday)
Construction AdWhies
ROG NO, CD Sox PM,o PM',s
Indi]dual Phase Emissions
1A 4.66 63.38 28.25 0.13 8.35 4.63
1 B 1.52 17.88 11.34 0.04 0.90 0.63
1 C 0.90 11.15 10.44 0.02 0.73 0.46
1 D 59.65 19.79 21.85 0.03 0.94 1.56
1 E 1.22 16.03 17.49 0.03 0.74 1.35
Phase Osrlap Emissions
1D,1E 60.88 35.82 39.34 0.06 1.68 2.91
Maximum Daily Emissions
Maximum Emissions
60.88 63.38 39.34 0.13 8.35 4.63
Regional Significance 75 100 550 150 150 55
Threshold
Significant Impact0 No No No No No No
Source:ESA,201e.
Operation
Implementation of the proposed Project would result in long-term regional emissions of criteria
air pollutants and ozone precursors associated with the operation of the new tank,pump station,
and pipeline resulting from the addition of a new employee. Operations emissions associated with
the proposed Project were modeled using CaIEEMod model.Model defaults were used to develop
a conservative estimate of emissions.Modeled operations emissions we presented in Table 8.As
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shown in Table 8,the proposed Project would result in long-term regional emissions of criteria air
pollutants and ozone precursors that are below SCAQMD's applicable thresholds.Therefore,the
Project's operational emissions would not result in or substantially contribute to emissions
concentrations that exceed the NAAQS and CAAQS and no mitigation would be required.
TABLE8
PROPOSED PROJECT OPERATIONAL EMISSIONS
Estimated Emissions(lbslday)
Emissions Source ROG NOa 00 SOa Pule Petra
Total Operational Emissions 0.0359 0.0179 0.0879 3.5eA 0.0258 7.1le3
Regional Significance 55 55 550 150 100 55
Threshold
Significant Impact^ No No No No No No
AQ-3 Exposure of Sensitive Receptors to Substantial Pollutant
Concentrations
The proposed Project would not expose sensitive receptors to substantial pollutant
concentrations. Proposed Project impacts would be less than significant, and no mitigation is
required.
Separate discussions are provided below analyzing the potential for sensitive receptors to be
exposed to localized air quality impacts from criteria pollutants and TACs from on-site sources
during Project construction and operations. As discussed previously, CO hotspots are not
addressed as there are limited new mobile source emissions resulting from the project as
discussed in the methodology section above.
Localized Construction Air Quality Impacts- Criteria Air Pollutants
The daily on-site construction emissions generated by the proposed Project were evaluated
against SCAQMD's LSTs for a one-acre site to determine whether the emissions would cause or
contribute to adverse localized air quality impacts.s The newest sensitive receptors to the Project
site are the residential neighborhoods located across Brookhlust Street. to the west.The nearest
residential buildings are located over 50 meters away from where the construction activities
would occur. Since the mass rate look-up tables provided by SCAQMD only provides LSTs at
receptor distances of 25, 50, 100,200,and 500 meters,the LSTs for a receptor distance of 50
meters are used to evaluate the potential localized air quality impacts associated with the Project's
peak day construction emissions.
Table 9 identifies the daily unmitigated,localized on-site emissions that are estimated to occur
during the Project's worst-case construction scenarios based on receptor distance and phase.
As shown in Table 9,the daily unmitigated emissions generated onsite by the proposed Project's
worst-case construction scenario would not exceed the applicable SCAQMD LST for any criteria
8 According to SCAQMD's LST methodology,LSTs are only applicable to the on-site construction emissions that
are generated by a project and do not apply to emissions generated offslte such as mobile emissions on roadways
from worker,vendor,and haul truck trips.
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Air Quality are Greenhouse Gas Emssions Toorical asoat Rily 2016
pollutants.Because the Project's worst-case construction emissions would not exceed
SCAQMD's applicable LSTs,the project would be less than significant for localized construction
impacts and no mitigation measures are required.
TABLES
PROPOSED PROJECT UNMITIGATED LOCALIZED DAILY CONSTRUCTION EMISSIONS
Estimated Maximum Daily On-Sits Emissions
(lbalday)
Construction Phase NO. CO Pit PMoa
50 meters to receptor
Max Individual Phase 35.68 21.41 5.63 3.66
1D,1E overlap 35.34 38.24 1.52 2.86
Localized Significance Threshold' 93 738 13 5
Significant Impact- No No No No
' Emissions account for implementation ofduet control measures as nslired by Si Rule 403n
Fug id aDust.
" LSTsfor a one acre skein SRA le are receptordistancaof50 metervand 200 meters.
Source: ESA2016
Localized Operational Air Quality Impacts— Criteria Air Pollutants
During project operations,the daily amount of localized pollutant emissions generated onsite by
the Project would not be substantial.The proposed Project would not result in a net increase in
on-site operational emissions as there are no localized criteria pollutant emissions associated with
electrical or water consumption,solid waste or wastewater generation,or consumer product use.
All criteria pollutant emissions we associated with mobile sources or consumer products(ROGs)
which we not considered in the LST analysis.Therefore,the proposed Project would result in no
impacts with respect to operational LSTs,and no mitigation is required.
Localized Construction Air Quality Impacts— TACs
Project construction would result in short-teen emissions of diesel PM,a TAC. Diesel PM poses
a carcinogenic health risk that is measured using an exposure period of 70 years. The exhaust of
off-road heavy-duty diesel equipment would emit diesel PM during demolition,site preparation
(e.g.,clearing); site grading and excavation;paving; installation of utilities,materials transport
and handling;building construction;and other miscellaneous activities. SCAQMD has not
adopted a methodology for analyzing such impacts and has not recommended that health risk
assessments be completed for construction-related emissions of TACs.
The dose to which receptors are exposed is the primary factor used to determine health risk(i.e.,
the potential exposure to TACs to be compared to applicable standards).Dose is a function of the
concentration of a substance or substances in the environment and the duration of exposure to the
substance.Dose is positively correlated with time,meaning that a longer exposure period would
result in a higher exposure level for the maximally exposed individual.Thus,the risks estimated
for a maximally exposed individual we higher if a fixed exposure occurs over a longer period of
time.According to the Office of Environmental Health Hazard Assessment(OEHHA),
carcinogenic health risk assessments,which determine the exposure of sensitive receptors to TAC
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emissions,should be based on a 70-year exposure period;however, such assessments should be
limited to the period or duration of activities associated with the proposed Project.
The construction period for the proposed Project would be much less than the 70-year period used
for risk determination(1.25 years).Because off-road heavy-duty diesel equipment would be used
only for short time periods,project construction would not expose sensitive receptors to
substantial emissions of TACs.This impact would be less than significant.
Project Operations— TACs
Typical sources of acutely and chronically hazardous TACs include industrial manufacturing
processes,automotive repair facilities, and dry cleaning facilities.The Project would not include
any of these potential sources, although minimal emissions may result from the use of consumer
products.As such,operation of the proposed Project would not expose surrounding sensitive
receptors to substantial pollutant or TAC emissions.
AQ-4 Objectionable Odors
The proposed Project would not create objectionable odors affecting a substantial number of
people. This impact is less than significant,and no mitigation is required
During construction of the proposed Project,exhaust from equipment and activities associated
with the application of architectural coatings and other interior and exterior finishes may produce
discernible odors typical of most construction sites. Such odors would be a temporary source of
nuisance to adjacent uses,but would not affect a substantial number of people. As odors
associated with Project construction would be temporary and intermittent in nature,the odors
would not be considered to be a significant environmental impact.Therefore,impacts associated
with objectionable odors would be less than significant.
Land uses that are associated with odor complaints typically include agricultural uses,wastewater
treatment plants,food processing plants,chemical plants, composting,refineries,landfills,
dairies,and fiberglass molding.The current Project is adding a temporary storage tank at OCSD's
Plant#2 to facilitate the expansion of the OCWD groundwater recharge facility.While the new
tank will store water processed at the OCSD's wastewater treatment plant,it will not increase the
throughput of the wastewater treatment plant. Additionally,the OCSD facility has not had any
odor complaints in the last twenty years filed with the SCAQMD. Therefore,because the
proposed Project is not increasing throughput of a land use type that is associated with nuisance
odors,and there have been no odor complaints within the last two decade,this impact would be
less than significant,and no mitigation is required.
AQ-5 Cumulative Air Quality Impacts
The proposed Project would not result in cumulatively considerable increases in criteria
pollutants during construction or operational activities. Therefore the proposed Project impacts
with respect to cumulatively considerable increases of criteria pollutants would be less than
significant, and no mitigation is required.
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The Project site is located within the SCAB,which is considered the cumulative study area for air
quality.Because the SCAB is currently classified as a state nonattainment area for ozone,PMiD,
and PM2,5,cumulative development consisting of the proposed Project along with other
reasonably foreseeable future projects in the SCAB as a whole could violate an air quality
standard or contribute to an existing or projected air quality violation. However,based on
SCAQMD's cumulative air quality impact methodology, SCAQMD recommends that if an
individual project results in air emissions of criteria pollutants(ROG, CO,NOx, SOx,PM]e, and
PM2,5)that exceed the SCAQMD's recommended daily thresholds for project-specific impacts,
then it would also result in a cumulatively considerable net increase of these criteria pollutants for
which the proposed project region is in non-attainment under an applicable federal or state
ambient air quality standard.As shown in Table 7,the Project's construction emissions would not
exceed SCAQMD's daily thresholds.Thus,because the proposed Project's construction-period
impact would be less than significant,the proposed Project would not result in a significant
cumulative impact,when considered with other past,present and reasonably foreseeable projects.
In addition,the operational emissions associated with the proposed Project would also not exceed
the SCAQMD's thresholds of significance for any of the criteria pollutants(see Table 8).
Furthermore,the proposed Project would also be consistent with SCAQMD's AQMP. Thus,the
proposed Project would not conflict with SCAQMD's air quality planning efforts for
nonattainment pollutants and would not lead to a cumulatively considerable net increase in
nonattainment pollutants during operations.
Overall,the proposed Project's construction and operational emissions contribution to cumulative
air quality impacts would be less than significant,and no mitigation is required.
5. CEQA GHG Impacts and Mitigation Measures
This section describes the impact analysis relating to greenhouse gas(GHG)emissions for the
proposed Project. It describes the methods and applicable thresholds used to determine the
impacts of the proposed Project
5.1 Methodology
At the time of this analysis,neither the OCWD nor SCAQMD have formally adopted a
methodology for analyzing impacts related to GHG emissions on global climate change.
Pursuant to full disclosure and according to OPR's CEQA Guidelines section 15064.4(a)that
states,"A lead agency should make a good-faith effort,based to the extent possible on scientific
and factual data,to describe,calculate or estimate the amount of GHG emissions resulting from a
project," the construction and operational emissions associated with the proposed project have
been quantified using methods described below.
Construction-related GHG emissions were estimated using a similar methodology to that
described above for criteria air pollutants. GHG emissions Of COi and CHo were converted to
Core emissions using the updated GWPs from IPCC's AR4.The GHG analysis incorporates the
same assumptions as the air quality analysis. Based on SCAQMD's 2008 Draft Guidance
Document—Interim CEQA Greenhouse Gas (GHG)Significance Threshold document,
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SCAQMD recommends that for construction GHG emissions the total emissions for a project be
amortized over a 30-year period and added to its operational emission estimates(SCAQMD,
2008c).
Operational emissions of GHGs, including GHGs generated by direct and indirect sources,are
estimated according to the recommended methodologies from SCAQMD.Direct sources include
the natural gas consumption onsite.Indirect sources include off-site emissions occurring as a
result of the Project's operations such as electricity and water consumption, solid waste disposal,
mobile sources,and wastewater disposal and treatment.The direct and indirect emissions
generated during the proposed Project's operations were estimated using CaIEEMod.The
operational emissions of CHa and N2O were extracted from the CaIEEMod output file and
converted to Core emissions using the GWPs from IPCC's AR4, as currently CaIEEMod uses the
GWPs from AR2.
The methodology used to analyze the Project's contribution to global climate change includes
evaluating the Project's total net annual GHG emissions(contraction and operational)against
the proposed GHG emissions screening level for commercial or residential projects in
SCAQMD's 2008 Draft Guidance Document—Interim CEQA Greenhouse Gas(GHG)
Significance Threshold document. Although no formal significance threshold for GHG emissions
has been adopted by SCAQMD at this juncture, Section 15064.7(c)of the State CEQA Guidelines
states"when adopting thresholds of significance,a lead agency may consider thresholds of
significance previously adopted or recommended by other public agencies...". SCAQMD's
recommended 3,000 MTCOre per year screening level was intended to achieve the same policy
objective of capturing 90 percent of the GHG emissions from new development projects in the
residential/commercial sectors.
All GHG emission estimate assumptions and calculations are provided in Appendix A to this
report.
5.2 Thresholds of Significance
The following GHG significance thresholds that are used in this report are also based on the state
CEQA Guidelines. Implementation of the Project would result in a significant GHG-related
impact if it would:
• Generate greenhouse gas emissions, either directly or indirectly, that may have a
significant impact on the environment; or
• Conflict with an applicable plan, policy, or regulation adopted for the purpose of
reducing the emissions of greenhouse gases.
The California Supreme Court recently considered the CEQA issue of determining the
significance of GHG emissions in its decision,Center for Biological Diversity v. California
Department of Fish and Wildlife and Newhall Land and Fanning(CBD vs. CDFW).The Court
questioned a common CEQA approach to GHG analyses for development projects that compares
project emissions to the reductions from`business as usual"(BAU)that will be needed statewide
to reduce emissions to 1990 levels by 2020, as required by AB 32. The court upheld the BAU
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method as valid in theory,but concluded that the BAU method was improperly applied in the
case of the Newhall project because the target for the project was incorrectly deemed consistent
with the statewide emission target of 29 percent below BAU for the year 2020. In other words,
the court said that the percent below BAU target developed by the AB 32 Scoping Plan is
intended as a measure of the GHG reduction effort required by the State as a whole,and it cannot
necessarily be applied to the impacts of a specific project in a specific location.The Court
provided some guidance to evaluating the cumulative significance of a proposed land use
project's GHG emissions,but noted that none of the approaches could be guaranteed to satisfy
CEQA for a particular project. The Court's suggested"pathways to compliance"include:
1. Use a geographically specific GHG emission reduction plan(e.g.,climate action
plan)that outlines how the jurisdiction will reduce emissions consistent with State
reduction targets,to provide the basis for streamlining project-level CEQA
analysis,as described in CEQA § 15183.5.
2. Utilize the Scoping Plan's business-as-usual reduction goal,but provide substantial
evidence to bridge the gap between the statewide goal and the project's emissions
reductions;
3. Assess consistency with AB 32`s goal in whole or part by looking to compliance
with regulatory programs designed to reduce GHG emissions from particular
activities;as an example,the Court points out that projects consistent with an SB
375 Sustainable Communities Strategy(SCS)may need to re-evaluate GHG
emissions from cars and light trucks.
4. Rely on existing numerical thresholds of significance for GHG emissions,such as
those developed by an air district.
The City of Huntington Beach have not adopted a CEQA-qualified Climate Action Plan,
therefore compliance pathway#1 is not a viable method for determining significance for this
project.
Regarding compliance pathway#2,the Court acknowledged that"a business-as-usual comparison
based on the Scoping Plans methodology may be possible,"and that"a lead agency might be
able to determine what level of reduction from business as usual a new land use development at
the proposed location must contribute in order to comply with statewide goals."However, in this
case,there is not sufficient information to assess whether the Project's emissions can be
compared with the State target of 29%below BAU by 2020.
Compliance pathway#3 can work if it can be shown how regulatory programs or performance-
based standards apply to a project's emissions,but this type of analysis can be difficult,especially
if some GHG-emitting elements of projects are covered by such standards and others are not.
Transportation emissions in particular are not regulated by the Scoping Plan because local
government retains control over the location and density of residential and commercial
development.
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Compliance pathway#4 is the most straightforward approach to analysis. Although no formal
significance threshold for GHG emissions associated with development-type land uses has been
adopted by the Cities or SCAQMD at this juncture, Section 15064.7(c)of the State CEQA
Guidelines states"when adopting thresholds of significance,a lead agency may consider
thresholds of significance previously adopted or recommended by other public agencies..." The
SCAQMD has proposed brightline threshold value of 3,000 MTCOze per year as presented by the
Stakeholder Working Group in November 2009(SCAQMD,2009). Since OCWD has not
adopted any significance criteria for GHG analysis at the time of this writing,it is reasonable
under CEQA for OCWD,as the lead agency,to utilize the two part efficiency threshold that was
proposed by SCAQMD,which is the applicable air pollution control agency for OCWD.
The GHG analysis uses SCAQMD's brightline threshold of 3,000 MTCOze per year. SCAQMD
developed these thresholds by comparing emission reductions included in CARB's Scoping Plan
to those achievable in the South Coast Air Basin from CEQA projects(SCAQMD, 2009).The
SCAQMD thresholds were designed to meet the AB32 goal of reducing GHG emissions to 1990
levels by 2020. EO B-30-15 requires that California attain a reduction in GHG emissions of 40%
below 1990 levels by 2030.Using the 40%below 1990 levels by 2030 reduction target,a project
built out at 2030 would need to reach an efficiency standard that is 40%below the 3,000
MTCOze per year threshold. Projects built out in 2030 would need to reach a 1,800 MTCOze per
year standard. Projects built out between these two dates should strive to meet the 2030 reduction,
however due to the limited technology available and the lack of existing State and local measures
to reduce emissions(for example from regional traffic planning and trip reduction measures),
placing the full burden of reaching the 2030 reduction on the project may unnecessarily inflate
the reductions that the project would need to achieve.
This threshold directly applies to Impact GHG-1 as it is a comparison to the quantification of
GHG emissions from the proposed project. This threshold indirectly applies to Impact GHG-2 in
that the SCAQMD has established the threshold to help guide the region towards the achievement
of the reduction goals under AB 32.
5.3 Project Impacts
GHGA: Project-Generated GHG Emissions
The proposed Project would not generate greenhouse gas emissions,either directly or
indirectly,that would have a significant impact on the environment. The proposed Project
results in less than significant impacts,and no mitigation is required.
The proposed Project would generate GHG emissions from a variety of sources. First, GHG
emissions would be generated during construction of the Project. Once fully operational,the
Project's operations would generate GHG emissions from direct sources such as natural gas
consumption and indirect sources such as electrical and water consumption, solid waste and
wastewater generation,and mobile sources from the one new employee.
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Construction Emissions
Construction-related GHG emissions for the proposed Project were estimated using the same
assumptions as the air quality analysis. Total estimated construction-related GHG emissions for
the proposed Project are shown in Table 10. As shown,the Project's total estimated unmitigated
and mitigated GHG emissions during construction would be approximately 908 MTCO2e.This
would equal to approximately 30 MTCO2e per year after amortization over 30 years per
SCAQMD methodology.
TABLE 10
ESTIMATED TOTAL CONSTRUCTION-RELATED GHG EMISSIONS
COa CHs Estimated CO,b
Emission Source Emissions
Unmitigated Construction Emissions
1A 543.13 0.03
16 47.71 0.01
1C 118.06 0.00
1D 97.91 0.03
lE 98.14 0.03
Total' 904.94 2.60 907.54 :MT�
Annual Construction Pmomi oar 30 years_ 30.25(MT/yr)
NOTES: CO¢enc Mon dioxide 0s isalenit MT metictons;MT/yr-metric tons per year.
Total Emissions take Into account the global wamtlng ratenbal a CH4 which Is 25.Therefore the tool CH4 emissions
Will not a ual Me sum of the indi Idual phase emissions as shown in the table.
Operational Emissions
The estimated operational GHG emissions resulting from Project implementation are shown in
Table 11. Additionally,in accordance with SCAQMD's recommendation,the Project's
amortized construction-related GHG emissions from Table 10 are added to the operational
emissions estimate in order to determine the Project's total annual GHG emissions.
As shown in Table 11,the proposed Project's total net annual GHG emissions would be
approximately 39.97 MTCO2e per year (detailed calculations are included in Appendix A of this
report),which would not exceed SCAQMD's proposed screening level of 3,000 MTCO2C per
year 2020 threshold or the 1,800 MTCO2e per year 2030 threshold.Therefore,the net increase in
GHG emissions resulting from Project implementation is considered to be less than significant.
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TABLE 11
ESTIMATED CONSTRUCTION AND OPERATIONAL RELATED GHG EMISSIONS
Estimated Emissions
Emission Source COA(MT/yr)
Construction
Annual Mitigated Construction[AmoN[ad ooer 30 years 30.257
Project Operations
Area Sources 0.00
Energy Consumption 3.98
Mobile Soumes 4.22
Solid Waste 0.35
Water Consumption 1.174
Total(Operafional Emissions) 9.72
Total Net Increase In Emissions 39.97
Greater than 3,000 MTCOze per year0 No
Greater than 1,800 MTCOz per yearn No
NOTES: COO tarpon dioxide erul-alent Mt/yr n manic tons per year;n rpercent.
source:ESA 2016
GHG-2: Consistency with GHG Emissions Reduction Plans or
Policies
The proposed Project would not conflict with an applicable plan,policy, or regulation adopted
for the purposes of reducing GHG emissions. The proposed Project results in less than
significant impacts,and no mitigation is required.
Consistency with AB 32
As discussed under Impact GHG-1 above,the proposed Project would not result in annual GHG
emissions exceeding the SCAQMD's 3,000 MTCO2e threshold which was designed to help the
region attain the goals of AB 32. Therefore,the proposed Project would be consistent with the
goals of AB 32,and no mitigation is required.
Consistency with EO B-30-15
As discussed under Impact GHG-1 above,the proposed Project would not result in annual GHG
emissions exceeding 1,800 MTCO2e,or the brightline threshold adjusted to reduce emissions to
40 percent below 1990 levels by 2030. Therefore,the proposed Project would be consistent with
the goals of EO-B-30-15,and no mitigation is required.
Consistency with City of Huntington Beach Energy Action Plan
The City of Huntington Beach Energy Action Plan addresses GHG reductions through 2020,
consistent with AB 32's goal of reducing GHG emissions to 1990 levels. As demonstrated under
GHG-1 above,the proposed Project would not exceed the SCAQMD's 3,000 MT brightline
threshold developed to help the region attain 1990 GHG emission levels by 2020.Therefore, the
ora,,ceudywdx oiaud r W..l wion Enneewmed Rmltcl 38 ESA INX87
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proposed Project would not interfere with the City of Huntington Beach Energy Action Plan as
the Project would not excessively increase GHG emissions within the City.
Consistency with SB 375
The key goal of the Sustainable Communities Standard(SCS)is to achieve GHG emission
reduction targets through integrated land use and transportation strategies. The focus of these
reductions is on transportation and land use strategies that influence vehicle travel. The proposed
Project would not increase vehicle traffic within the City or the region.Therefore,the proposed
Project would not conflict with the implementation of SB 375.No mitigation is required.
As discussed above,the proposed project would be consistent with the CARB Scoping Plan,EO-B-30-15,
SB 375 and with the City's Energy Action Plan. Therefore,the proposed project would have a less than
significant impact related to applicable GHG plans and policies
6. NEPA Conformity Analysis
6.1 Methodology
The NEPA analysis compares the proposed Project's impacts with the Federal thresholds in order
to determine if impacts to Clean Air Act pollutants would exceed federal thresholds. Considering
the standards developed for the State of California are more restrictive than the federal thresholds,
the analysis detailed above for Air Quality and Greenhouse Gasses would serve to prove
compliance with the NEPA analysis.
The SCAQMD is responsible for the development of the Basin's portion of the State
Implementation Plan(SIP),which is required under the federal Clean Air Act for areas that are in
nonattainment for criteria pollutants.The project may obtain state funding and therefore,under
the Clean Air Act,the project would be subject to a SIP conformity determination.This is
because the project is in a severe nonattainment area for 8-hour ozone,a moderate nonattainment
area for PM10 and a maintenance area for CO and PM1o.Table 1 shows the federal thresholds
while Table 3 shows the attainment status for each of the criteria air pollutants. Under the Clean
Air Act de minimis levels for criteria pollutants have been established as a screening level to
determine the potential for a proposed Project to adversely impact air emissions. Emissions are
compared to these levels for the SIP conformity determination(de minions). If the project is
below the de minimis levels then the project is determined to be in conformance with the SIP.If a
project exceeds the de minimis levels then a full conformity analysis must be conducted.
6.2 Thresholds of Significance
40 CFR 93 § 153 defines de minimis levels,that is,the minimum threshold for which a
conformity determination must be performed,for various criteria pollutants in various areas.The
information is summarized in Table 12.
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TABLE 12
DE MINIMS EMISSION LEVELS
Pollutant Area Type Tonslyear
Serious nonattonment 50
O[one iVOC or NOxo Seas nonattainment 25
Extreme nonattainment 10
Other areas outside an o one transport region 100
Marginal and moderate nonattainment inside an omne 100
Omne MOxo transportation region
Maintenance 100
Marginal and moderate nonattainment inside an omne 50
transport region
Omne WC, Maintenance within an acne transport region 50
Maintenance outside an omne transport region 100
CO,SO,NO, All nonattainment and maintenance 100
Serious nonattainment 70
PM,e
Moderate nonattainment and maintenance 100
PM'.' All nonattainment and maintenance 100
Source:USEPA,201aa,USEPA 20165
6.3 Project Impacts
NEPA-1: Conformity Analysis
The proposed Project would be consistent with the SIP as indicated by emissions being below
the de minimis thresholds,and therefore,a detailed conformity analysis is not warranted No
mitigation is required.
As shown in Table 13,ozone precursors are below the de minimis thresholds for construction and
operational activities,and therefore,the project is consistent with the SIP. Construction emissions
show only the maximum emissions for the proposed Project in tons per year and are based on the
maximum days of construction per subphase.Because the Project emissions are below the de
minimis thresholds,a detailed conformity analysis is not warranted.
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TABLE 13
SIP CONFORMITY EVALUATION
Threshold Maximum Operational
Nonattainment of Construction
Pollutant Federal Status Rates Significance Emissions Emissions
(tons/year)
(tone/year) (tons/year)
Ozone(Oy) Nonattainment Extreme See(VOC&NOx)
Ahainment/
Carbon Monoxide(CO) Maintenance N/A 100 0.64 0.0155
Oxides of Nitrogen(NOx) N/A N/A 10 1.43 3.3e-3
volatile Organic Compounds
(VOC) N/A N/A 10 0.91 6.5e-3
Lead(Pb) Attainment N/A N/A N/A N/A
Particulate matter less than 2.5
microns(PM,,)* Nonattainment Moderate 100 0.10 4.62e-3
Particulate matter less than 10 Attainment/
micron6(PM0* Maintenance N/A 100 0.19 1.27e-3
Sulfur Dioxide(SO2) Attainment N/A N/A 0.00 6.0e-5
Notes:N/A=Non-applicable
Source: ESA 2016;USEPA,2016a,USEPA 20166
As discussed previously,no growth-inducing development or land use would occur under the project,and
therefore,the project would not conflict with the City's General Plan.Therefore the project would be
consistent with the AQMP.Additionally,as the annual emissions from the project would be well below
the de minimis thresholds for SIP conformity,the proposed project is considered to be in conformance
with the SIP. No mitigation would be required.
7. References
California Air Resources Board(CARB)2016a.Ambient Air Quality Standards.Last revised:
May 4,2016.Available: <http://www.ub.ca.gov/research/aags/caags/cmgs.htm>.
Accessed:June 27,2016.
CARE 2016b. Overview:Diesel Exhaust and Health. Available:
http://www.ub.ca.gov/research/diesel/dieset-health.htm.Accessed:June 27,2016.
California Air Resources Board(CARB).2014a. California Greenhouse Gas Inventory for 2000-
2012—by Category as Defined in the 2008 Scoping Plan.Available:
hUn//www.arb.ca.2ov/cc/inventory/data/tables/2h2 inventor� scooineolan 00-12 2014-
03-24.odf
CARB.2014b.Proposed First Update to the Climate Change Scoping Plana Building on the
Framework.February.
CARB.2013a. Area Designation Maps/State and National. Available:
<www.ub.ca.gov/desig/adm/adm.htmh. Accessed June 2016.
CARB.2010.Proposed SB 375 Greenhouse Gas Targets:Documentation of the Resulting
Emission Reductions based on AIPO Data,August 9,2010.
coanae eoumywew Dismct n wow RWeclpn anaeowmem amps 41 EW160367
Ai,Gualiryand Greenhouse Gae F.w.7.00g1 Resort �Iy 2016
CARB.2009a.APB Fact Sheet:Air Pollution Sources, Effects and Control,
http://www.ub.ca.gov/researchlbealth/fs/fs2/fs2.htm.
CARB,2009b. Climate Change Scoping Plan:A Frameworkfor Change, available online:
http://www.ub.ca.gov/cc/scopingplan/document/adopted_coping_plan.pdf,published
December 2008,amended version included errata and Bond requested modifications posted
May 11,2009.
CARB.2007.Expanded List of Early Action Measures To Reduce Greenhouse Gas Emissions In
California Recommended For Board Consideration.
Intergovernmental Panel on Climate Change(B°CC). 2007. Climate Change 2007: Synthesis
Report. Available at: ipcc.ch/publications_and_data/ar4/syr/en/spms3.html.Accessed on
June, 2016.
IPCC 2001. Climate Change 2001: Working Group P The Scientific Basis.Last revised:2001.
Available:<http://www.grida.no/climate/ipcc%5Ftu/wgl/032.htm#f5>.
South Coast Air Quality Management District(SCAQMD).2015.Multiple Air Taxies Exposure
Study in the South Coast Air Basin MATES IV. May.Accessed
http://www.agmd.gov/home/library/air-quality-data-studies/health-studies/mates-iv.
November 1,2015.
SCAQMD.2015b.SCAQMD Air Quality Significance Thresholds. Revised Much.Available:<
http://www.agmd.gov/home/regulations/cega/air-quality-analysis-hmdbook>Accessed:
June 2016.
SCAQMD 2014. 2014 Air Quality Data Tables. Available:
http://www.agmd.gov/home/library/air-quality-data-studies/historical-data-byyear.
Accessed:June 27,2016.
SCAQMD 2013. 2013 Air Quality Data Tables. Available:
httn://www.agmd.eov/home/library/air-quality-data-smdies/historical-data-by year.
Accessed:June 27,2016.
SCAQMD. 2013b.Final2012 Air Quality Management Plan. February.
SCAQMD 2012.2012 Air Quality Data Tables. Available:
htm://www.agmd.eov/home/library/air-quality-data-smdies/historical-data-by_vear.
Accessed:June 27,2016.
SCAQMD.2009.Greenhouse Gas CEQA Significance Threshold Stakeholder Working Group#14.
November 19.Accessed http://www.agmd.gov/home/regulations/cega/air-quality-nalysis-
hmdbook/ghg-significance-thresholds March 30,2015.Southem California Edison(SCE).
2015. Our Renewable Power Summary for 2014.Accessed online:
https://www.sce.com/wps/portal/home/about-us/mvim ment/renewable-
power/!ut/p/bl/he_fwMwFAbwV_EF5jk2m8u43Q2ZbQTBV luSixpKphYojTs7Rdhuxhs7b
k6B34fnA84NMCNu}IVKTN1gRD_ftHmM IjndshLZoSo3yBKWOmKRRfiOHnx4gP8Mx
UfSGvhvklfxsyeLFckTRgoOvg_S-
Adscsy2u8MMCoKMFLgvKS Wly29w58kdcNUPrS9cJ8Brv19Fbg5GTUvWCfi VZ2mlDS_
DOEHjnAvbzgjwNOi_l CiFPV2uwgo9QIO-
ZIGVRjrR9jLwil WfgU_gbtLSTHDVDXbsib_e3ugX_so-
Fg!!/dl4/d5/L2dBISEvZOFBIS9nQSEh/?from—powerandenvironment/renewables. July 24,
2015.
aanae COUM W DlWd r wawv unwn ennanwmem rmp 42 EWIW66r
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SCAQMD.2008a.Mates III Final Report. September.Accessed
http://www.agmd.gov/home/library/air-quality-data-studies/health-studies/mates-iii/mates-
iii-final-report.May 2015
SCAQMD.2008b.Multiple Air Taxies Exposure Study III Model Estimated Carcinogenic Risk.
Accessed http://www3.agmd.gov/webappl/matesiii/.May 2015.
SCAQMD.2008c.Draft Guidance Document—Interim CEQA Greenhouse Gas (GHG)
Significance Threshold.October.
SCAQMD. 2003.Final Localized Significance Threshold Methodology,Appendix C—Mass Rate
LST Look-up Tables. Revised October 21,2009.
UC Davis,Institute of Transportation Studies(UCD ITS). 1997. Transportation Project-Level
Carbon Monoxide Protocol-Revised 1997. USD-ITS-RR-99-21. Available
http://www.dot.ca.gov/hq/lnfoSvcs/EngApps/softwue.htm
United Nations Framework Convention on Climate Change(UNFCCC). 2012. Total COi
Equivalent Emissions without counting Land-Use, Land-Use Change and Forestry
(LULUCF).Available at
unfccc.int/ghg_emissions_data/pmdefined_queries/items/3814.php.
United States Environmental Protection Agency(USEPA).2016a. The GreenbookNonattainment
Areas for Criteria Pollutants. Available at
http://www.epa.gov/air/oaqps/greenbk/index.html. Accessed June, 2016.
USEPA.2016b.De Minimis Emission Levels, Updated June 2016.Available:
https://www.epa.gov/geneml-conformity/de-minimis-emission-levels.Accessed: June
2016.
USEPA.2011.Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990-2009;Executive
Summary, Table ES-2. April 2011.
Western Regional Climate Center(WRCC),2016.Period of Record Monthly Climate Summary for
Newport Beach Harbor, California.Available:<http://www.wrcc.dri.edu/cgi-
bin/cliMAIN.pl?ca6175>.Accessed June 27,2016.
aanae COUM We Diamn n waw vro dOn ennanwmnt ampd 43 EWIW667
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APPENDIX A
Air Quality and Greenhouse Gas Emissions Assumptions
and Calculations
Orange county water oiWd r water R ajdOn Ennanwmam Pra c EGA/1W067
Air duality and G...W.ee Gae Fm'aiana 7.00g1 Rear) �Iy 2016
Orange County Water District - EQ Flow Tank
Operational Assumptions
CalEEMod Inputs(Non-Default information only)
Project Location
County Orange
Air District South Coast
Climate Zone 8
Operational Year 2022
Utility Provider Southern California Edison
Land Use Sq Ft KSF Acers CaIEEMod Land Use Type
Pump Station 2,250 2.25 default Heavy Industrial
70,720 inside tank area -Used for architectural coating only
39,320 exterior tank area -Used for architectural coating only
"General Heavy Industrial is used for estimation of electrical and water usage;and solid waste and wastewater generation associated with the new EQ Flow Tank. Square footage is the floor
area of of the pump house and vault to provide a conservative estimate of electric usage for the pumps.
Trio Generation: Assumes 1 new employee @ 2.5 trips per day per employee=2.5 trips per day(round to 3 trips per day)
1.33 trips/ksf
Area Emissions: Assumes no new Landscaping
Assumes no new building maintenance/upkeep intensity than currently occurs.
Assumes default consumer product use
Enerev Use: Electrical usage for buildings are based on size of the building and CaIEEMod default consumption rates.
0 kBTU/year No natural gas assocaited with the operation of the new EQ tank
13,860 kWh/year electrical consumption based on new building size
Water Use: Assumes 1 new employee
Default: 346,875 &/year
Project: 260,156 &/year (Default based on trip rates assumes 1.3 employees,new employees would be 75%of default)
-No septic onsite,disposal/treatments adjusted to remove septic.
Solid Waste Generation: Tons/year
CaIEEMod Project Reduced'
1 extra employee 1.86 1.40 0.70 (Default based on trip rates assumes 1.3 employees,new employees would be 75%of default)
`CaIEEMOd doesn't take into account the fact that California on a whole has reduced waste to la ndfill by greater than 50 percent Modeling accounts for the minimum 50
percent recycling.
Orange Can"Water olrtticL EQFIM Tank
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anlaq wwNm lamry I.IW l to nll Iaeml —1 g
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m
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m.,w
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Orange County Water District - EQ Flow Tank
Vehicle Trips
Daily Total
Haul Haul Haul off Concrete
Worker Vendor Trips Trips (CY) (CY)
1A: Excavation, Hauling,Grading for Flow EQTank, Pump Station, and Pipeline 10 1 20 80 1000
IA: Excavation, Hauling,Grading for Flow EQTank, Pump Station, and Pipeline 12 168 2300
1B: Piles Construction for Flow EQTank 10 2 2 6 40
2 6 40
1C: Flow EQTank Pad Construction 10 2 12 288 2330
1D: Flow EQTank Assembly and Coating 5 2 -- --
lE:Assembly of Flow EQ Pumps and Meter Vault 1 5 1 4 1 -- I --
Orange County Water District - EQ Flow Tank
Schedule
2020 2021
Jan-Apr May-Aug Sep-Dec Jan-Apr May-Aug Sep-Dec
OCSD Plant No.2 Flow EQ Facilities
Flow EQ Tank, PS, Piping& Meter Vault
Excaion/Site Prep/Pipeline (lA)
Tank pal
les(1B)
Tank Pad (1C)
Assembly&Coating of Steel Tank(11))
Flow EQ PS& Meter Vault
Equipping(IE)
Orange County Water District-EQ Flow Tank
Unmltigate l Mine Emissions
WaMes Gays a. 1. W ny
IA:Exavatlan Xaulln.Gratne for Flax EQ Tank.Pump Soatlo,and Pinellne l0 45 00303 ... O IS O.Wl3 0113 0'W03 .,.SS a.
18',P8es C0ns[mdoo For Flow EQTank 10 35 00303 0.0108 0429 0W13 OFFS 00303 )4833A 0 115
1C Flow EQTank Patl Consirutlion 10 20 0.0303 OC108 EA29 0.." OFFS 0.03N 2386,152 0.IIW
l0'.Flow EQTank Assembly and L ning 5 30 OD1515 00204 0.I. I OW365 00565 OOl5I5 1A91.345 0..
IE:Assembly of Now EQ Pumps and Mewr Vault 5 30 0.01515 00204 1 0.2145 1 OW265 00565 00150 A91345 0069
Vemor oava an 10 to c,
IA:Exavatlan,Xaulln.G-d1ng for lav EQ Tank.Pump Statlo,and Pipeline l 45 O.W83I 00739 0.1115 OW221 00]]41 000285 935W95 000675
18',Pdes COns[rv[tlon fw Flow EQTank 2 25 001e@ OF478 0,223 OW)42 001482 OW9 1039653 0WJ3
1C'.FIw EQTank Patl Consirutlion 2 24 0.01662 0308 0.12S OCW42 0.81402 O.LOS] 998.%M O.LO72
10'.FIaw EQTank Assemblyand1.ang 2 30 0.03662 0108 0.223 0CW42 0.8I482 O.WS] 1247SM O.W9
]E:Assembl of Flaw EQ Pumps and Meter Va ult 4 30 OD3324 02956 0,46 1 OW284 002964 0,0l14 W95.1R 0018
Tatll Xaul
T—maVs Tn s f0.
]A Ewavad,Haulln,Gman for Flow EQTank,Pum Station,and Pi line 20 BO 099 ]B.298 B.]34 Od 1694 0.658 450121.E S
1A:Ex[aaatlaq Hauling.Grading lm Fbw EQTank,Pump Slatlan,and Pipeline 13 1W 0594 ]0.9]BB 5.34W 00345E ]0164 0.3943 56]]54.4 39l]W
]B:PIIes Cons[mttlan fw Flaw EQTank 2 6 O0. 1IA29e 08J34 0.0057E 1.104 00658 3375919 1 OM328
Cawete Talal Xaol
im[ks Tn s IK f0.
]0'.Piles Lons[rvRion Fw flow EQTank 2 6 0.0354 04852 018 OW146 00424 0MIA 2MWl2 OW636
]G FIw EQTank Patl Cnnslmtllon II 208 0.2124 39112 358 OLOB]6 OS544 009324 2483I0.3 1d31a9
Orange County Water District- EQ Flow Tank
Fugitive Dust Emissions(lbs/day)
Fugitive emissions from truck loading
PM. kx(0.0032)x((U/5)"/(M/2)''4) k= particle size(PM30=0.35,PM2.5=0.053)
0.35 x(0.0032)x((5.82/5)''3/(12/2)1A) U= wind speed(miles-hour)= 5.82
= 0.000110958 lbs/ton M= Material moisture content=12%
PM,, = k x(0.0032)x((U/5)"/(M/2)1.4)
0.053 x(0.0032)x((5.82/5)s3/(12/2)1A)
1.68023E-05 lbs/ton
Unreduced Rule 403
Cubic Yards #Trucks Tons PMr4 PMzs PMr4 PMzs (Daily Emissions)
Phase 1A 1,000 20 380 0.042164 0.006385 0.018974 0.002873
Phase 3A 2300 1 12 1 228 1 0.0252991 0.0038311 0.0113841 0.001724
Phase 18 1 40 1 2 1 38 1 0.0042161 0.0006381 0.0018971 0.000287
Orange County Water District- ED Flow Tank
Fugitive Dust Emissions(Ibs/day)
Fugitive emissions from Dozers and Excavators:
PIVI. ((C,..x s's)/M")x F... Cpvjs= arbitary coefficient used by AP-92=1
((I x 6.9''5)/7.91'4)x 0.75 s= material silt content=6.9%
= 0.752760759 lbs/hr M= material moisture content=7.9%
Fpv.= PM,,scaling factor default of 0.75
PM,, = ((Cxx s` )/M'a)x Fpmzs Cnp= arbits ry coefficient used by APA2=5.7
((5.7 x 6.9")/7.9s's)x 105 Fpiazs= PMi S scaling factor default of 0.105
= 0.413778428 Ibs/hr
Unreduced Rule 403
hrs/day PMco PMu Pmu, I PMu (Daily Emissions)
lA Excavators 6 4.516565 2.482671 2.032454 1.117202
1A Bull Dozer 6 4.5165651 2.4826711 2.0324541 1.117202
Orange County Water District - EQ Flow Tank
Unmitigated Emission Factors by Equipment
Ibs/vehicle/hr
HP
Equipment Description Rating voc NOx co so, PMip PM,., Wz cHa
Asphalt Paver 175 0.0543 0.6006 0.4871 7.80E-04 0.0293 0.027 78.7418 0.0245
Backhoe 150 0.0362 0.3861 0.3823 5.90E-04 0.0194 0.0179 59.1968 0.0184
Bull Dozer 250 0.1458 1.5704 0.5472 1.07E-03 0.0763 0.0702 107.5489 0.0335
Compactor 200 0.034 0.4368 0.194 0.00082 0.0133 0.0122 82.5539 0.0257
Concrete Trucks 350
Crane 300 0.0705 0.8831 0.6073 9.30E-04 0.0356 0.0328 93.5371 0.0291
Drill Rig 500 0.0743 0.9621 0.5688 2.60E-03 1 0.0288 1 0.0265 267.694 1 0.0833
Dump Trucks 350
Excavators 200 0.034 0.4368 0.194 8.20E-04 0.0133 0.0122 82.5539 0.0257
Flatbed Truck 350
Fork Lifts 120 0.0236 0.3026 0.3477 5.20E-04 0.0145 0.0133 52.2408 0.0163
Man Lifts 75 6.21E-03 0.1052 0.1614 2.50E-04 2.91E-03 2.68E-02 24.9945 7.78E-03
Pick-Up Truck 300
Pile Driver 500 0.1149 1.4501 0.83 2.25E-03 0.0525 0.0483 225.9096 0.0703
Water Trucks 350 0.0846 0.9306 0.4596 1.45E-03 0.0332 0.0306 145.4268 0.0453
Welding Eq. (Truck Mounted) 300 0.0824 0.7232 0.3214 1.49E-03 1 0.0238 1 0.0238 1169.13951 7.44E-03
Ibs/vehicle/trip
Offsite
Worker 3.03E-03 4.08E-03 0.0429 1.30E-04 0.0113 3.03E-03 9.9423 44.60E-04
Vendor 8.31E-03 0.0739 0.1115 2.10E-04 7.41E-03 2.85E-03 20.7931 1.50E-04
Concrete Trucks 0.0177 0.2426 0.215 7.30E-04 0.0212 8.27E-03 71.8201 5.30E-04
Haul Trucks 0.0495 0.9149 0.4367 2.85E-03 0.0847 0.0329 281.3266 1.94E-03
Orange County Water District - EQ Flow Tank
Unmitigated Criteria Pollutant Emissions Summary (lbs/day)
Emissions by Phase
ROG NOz CO soxL0.73
PM,, PM,,
3A Total 4.66 63.38 28.25EO.O4
4.63
1B Total 1.52 17.88 11.34 0.63
1C Total 0.90 11.15 30.44 0.46
1D Total 59.65 19.79 21.85 1.56
1E Total 1.22 16.03 17.49 1.35
Phase Overlaps
1D,1E ITotal 1 60.88 1 35.82 1 39.34 1 0.06 1 1.68 2.91
Max Emissions by Phase
Total 60.88 1 63.38 39.34 1 0.13 8.35 1 4.63
SCAQMD Thresholdl 75 1 100 1 550 1 150 1 150 1 55
Exceed Threshold?l No I No I No I No I No I No
LST Emissions
Distance
(m) NOx co sox PM, PM,.,
1A Total 51 35.68 15.57 5.63 3.66
1B Total 51 15.37 9.38 0.56 0.51
1C Total 51 8.05 7.21 0.35 0.32
11) Total 51 19.62 21.41 0.87 1.54
1E Total 51 15.72 16.83 0.65 1.32
Phase Overlaps
1D,ie ITotal 1 51 m 1 35.34 1 38.24 1 1 1.52 1 2.86
Max Emissions by Phase
Max 1 35.68 38.24 1 5.63 1 3,66
SCAQMD Thresholdl 50 1 93 1 738 1 13 5
Exceed Threshold?i I No I No I I No I No
Orange County Water District - EQ Flow Tank
Emissions by Phase
ROG Nox I CO I Sox PM30 PM2.5 002 CN4
Ibs/day Ibs/subphase
Onsite 3.04 33.99 13.74 0.04 1.421 1.31 174,367.961 54.31
Fugitive 4.10 2.24
3A Offsite 1.62 29.39 14.51 0.09 2.83 1.09 1,022,686.71 7.23
Coating 3.72 1.68 1.83 0.00 0.11 0.11 281.45 0.02
Total 4.66 63.38 28.25 0.13 8.35 4.63 1,197,054.67 61.53
Onsite 1.34 15.37 9.38 0.03 0.55 0.51 97,397.62 30.32
1B Fugitive 0.00 0.00
Mite 0.18 2.50 1.96 0.01 0.34 0.12 7,762.99 0.15
Total 1.52 17.881 11.341 0.04 0.90 0.63 105,160.61 30.48
Onsite 0.64 8.05 7.21 0.01 0.351 0.32 8,607.32 2.68
SC Fugitive 0.00 0.00
Offsite 0.26 3.10 3.23 0.01 0.38 0.14 251,594.49 1.95
Total 0.90 IS.IS 10.44 0.02 0.73 0.46 260,201.81 4.63
Onsite 1.18 15.72 16.83 0.03 0.65 1.32 212,303.36 66.20
Fugitive 0.00 0.00
1D1 Mite 0.03 0.17 0.44 0.00 0.07 0,02 2,738.93 0.08
Coating 58.45 3.90 4.58 0.01 0.22 0.221 748.72 0.04
Total 59.65 19.791 21.85 0.031 0.94 1.561 215,791.01 66.32
Onsite 1.18 15.72 16.83 0.031 0.65 1.32 212,303.36 66.20
M Fugitive 1 0.00 0.00
Offsite 0.05 0.32 0.66 0.00 a09 0.031 3,986.52 0.09
Total 1.22 16.03 17.49 0.031 0.74 1.351 216,289.87 66.28
Table 4-phase 4 Construction Equipment Mix
Orange County Water District-EQ flow Tank
Equipment Dst
Equipment Bondsmen Time Total Total He ROG Nose CO I SOx pMe pMss Mi Ora
Activity Desarilstion Quantity (Hall (Dayst (Hours) Rtlmp bauder fief sub Frio
MD Him EQTank,PS,Meter Vauk&Pipeline(IA) Bull Dozer 2 6 90 3w 250 1J496 18.8418 6.5664 0.01284 0.9156 0.0424 ]]0.35.208 24.12
Co.,.., 1 6 3o ED 200 0304 E6208 1.164 0.00492 0.0798 0,0732 4953234 1542
Easavators 2 6 20 240 2M 0408 5.2416 2.328 Durres 0.1596 0.1464 99625.872 12,936
Sell Dump Trucks 4 6 4 96 350 0 D 0 0 0 D D 0
Demo Dump Trucks 4 6 14 3" 350 0 0 0 0 0 0 0 0
Water Trucks 1 0 45 3M 350 0.6768 7.2818 367E8 0.0116 0.2656 0.2448 52353.648 16,308
06D Flow EQTank Mi.(18) Drill Rig 1 6 2D 120 SM 0.4458 5.7126 34128 0.0156 0.1728 Use 32123.28 9.996
Bill 1 6 20 .0 LSO 0.2172 2.3166 2.2938 0.00354 0.11" 0.1074 7103.616 2208
Concrete Trucks 1 5 3 15 350 a 0 0 0 a 0 0 0
Oump Tracks 2 5 3 30 3" 0 0 0 0 0 0 0 0
Vim,Tracks 2 4 25 200 350 0.6768 T.2848 3.6268 0.0116 0.26M 0.2MB 58170.72 18.12
MD FIow EQTank past if Crane 1 5 5 25 300 0.3525 4.4155 30365 Del 0,128 0.164 2338.4275 0.2225
Fork Llhs 2 6 5 ED 120 0.2832 3.6312 4,1224 0.80624 0,124 0.1596 6268896 1956
Concrete Trucks 0 5 24 4bJ 350 0 0 0 0 0 M3192
0 0
MD Flow EQTank Assembly&Coating(to) Crane 1 6 10 fA 3M 0423 5.2986 36438 0.80558 D2136 5612226 1146
Fork Lifts 4 6 30 220 120 0.5654 2.2624 8.3149 0.01218 0.318 150153.504 46914
Man Lifts 5 6 15 450 25 0.1863 3.156 4.84E 0.0025 O.M23 56237.625 12.505
06D Flow EQ pS&Meter VaukE ui in (IE) Crane 1 6 SO M 3M 0423 5.2986 3.6438 DOZ58 0.2136 5612.226 1246
Fork Lifts 4 6 30 22O 120 056" Z2624 8.3458 001248 0.M8 1504535M 46944
Man LlXs 5 6 L5 450 T5 0.1863 3.156 484E 0.OW5 OM23 56237,Q5 12.505
Orange County Water District - EQ Flow Tank
Unmitigated GHG Emissions Summary (MTCO2e/yr)
Construction GHG Emissions
Ibs/phase Metric Tons/phase
CO, CH, CO, CH,
lA 1,197,054.67 61.53 543.13 0.03
16 105,160.61 30.48 47.71 0.01
1C 260,201.81 4.63 118.06 0.00
11) 215,791.01 66.32 97.91 0.03
JE 216,289.87 66.28 98.14 0.03
Total 1,994,497.97 229.24 904.94 0.10 Ibs/total Construction Period
1 25 GWP
904.94 2.60 MT COie/Total Construction Period
90 7.54 Total MT CO,e
30.25 Amortized Emissions
Operational GHG Emissions
co, CH, N20 COze
Area I 4.00E-05 0.00E+00 0.00E+00 0.00
Energy 3.9663 1.80E-04 4.00E-05 3.98
Mobile 4.2125 1.40E-04 0.00E+00 4.22
Waste 0.1421 8.40E-03 0.00E+00 0.35
Water 1.0614 2.69E-03 2.10E-04 1.17
Total 9.38234 0.01141 0.00025 9.72
Const 30.25
Total 39.97
3 HEx,000 MT COie SCAQMD Threshold
No
ceed?
-CO 2e emissions include GWPs of 25 for CH4 and 198 for N20-
Orange County Water District - EQ Flow Tank
Unmitigated NEPA Emissions Summary (tons/year)
Unmitigated Emissions by Phase
ROG NOx co sox PM,, PMz.s
3A Total 0.10 1.43 0.64 0.003 0.19 0.10
1B Total 0.02 0.22 0.14 0.000 0.01 0.01
1C Total 0.01 0.13 0.13 0.000 0.01 0.01
1D Total 0.89 0.30 0.33 0.001 0.01 0.02
3E Total 0.02 0.24 0.26 0.000 0.01 0.02
Phase Overlaps
1o,tE 0.91 1 0.54 0.59 0.00 1 0.03 0.04
Max Emissions
0.91 1 1.43 0.64 0.00 0.19 0.10
SCAQMD Thresholdl 75 1 100 1 550 150 1 150 55
Exceed Threshold?I No I No I No No I No No
APPENDIX B
CaIEEMod output.
Grange count'wap opmn n waW Rdudnnn ennanwman amps 45 EWIW667
q4 Queny and GreenMuee Gae F ssbne 7000n 1Reactl my 2016
CaIEEMod Version: CalEEMod.2013.2.2 Page 1 of 18 Date: 7/16/2016 10:31 PM
EQ FLow Tank
Orange County, Winter
1.0 Project Characteristics
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population
General Heavy Industry 1.50 10001 0.03 1,501 0
1.2 Other Project Characteristics
Urbanization Urban Wind Speed(ni 2.2 Precipitation Freq(Days) 30
Climate Zone 8 Operational Year 2022
Utility Company Southern California Edison
CO2 Intensity 630.89 CH4 Intensity 0,029 N20 Intensity 0.00617
(IbIMWhr) (IbIMWhr) (Ib/MWhr)
1.3 User Entered Comments & Non-Default Data
CalEEMod Version: CalEEMod.2013.2.2 Page 2 of 18 Date: 7/16/2016 10:31 PM
Project Characteristics- Determination of emissions for Dril Rig,Architectural Coating Emissions, and operational Activities
Land Use-
Construction Phase- Building and Tank Architectural Coating and Dril Rig Emission factor determination only
Off-road Equipment-See Assumptions
Off-road Equipment- Generator for use with sand blaster for prepping tank for coating
Trips and VMT-See Assumptions
Architectural Coating-See Assumptions
Vehicle Trips-See Assumptions
Area Coating-See Assumptions
Landscape Equipment-See Assumptions
Energy Use-See Assumptions
Water And Wastewater-See Assumptions
Solid Waste-See Assumptions
Construction Off-road Equipment Mitigation-
Off-road Equipment-
Table Name Column Name Default Value New Value
tblArchitecturalCoating Consb%rea_Nomesidential_Extenor 750.00 39,320.00
......................9------i-----------------------------}_____________________________�......... 70,72 ............
tblkchitecturalCoatin Consbkrea_Nome.idential_Imenor 2,250.00 ]0,]20.00
------------------ng--------- --------------n-----rcent-----i.______________'O ?------------ U ------.----.
Ratel
tblAreaCoati
.............................i-----------------------------}-----------------------------4..........................
tblConstructionPhase NumDdys 5.00 22.00
-----------------------------{-----------------------------
}--------------
5.__00-------------------------1--0.00------------.
tblConstructionPhase NumDaye
.............................i-----------------------------}-----------------------------4..........................
tblConstructionPhase NumDdys 2.00 1.00
-------tblConstructionPhase----------------------4-----------------------------t-----------1Y27Y2021 ----------?---------11/30/-------------
PhaseEndDatei
tblConstructionPhase -----------PhaseEndDate r ---- -- --------
r
12/2812020
-------tblConstructionPhase ------ ---------PhaseStanDate --------------------
12/292020----------?--------- 11/12021 --- - -
.............................i-----------------------------------------------------------4..........................
tblConstructionPhase PhaseStartDate 1/2/2018 1VI512020
-----------------------------4-----------------------------4------------------------------ --------------------------
tblEnergyUse NT24NG 6.86 0.00
CalEEMod Version: CalEEMod.2013.2.2 Page 3 of 18 Date: 7/16/2016 10:31 PM
tblEnergyUse T24NG 14.78 0.00
................q.P......._.. ----------.........----------¢------------ ------------4..........................
t i&iRoatlE ui ment Horse Power i 205.00 500.00
..............................-----------------------------------------------------------4..........................
1b106RoadEquipmenl OflRoadEquipmentType i Bore/Drill Rigs
.............................4-----------------------------------------------------------4--------------------------
tbIOlfRoatlEquipment OflRoadEquipmenlType i Genemlor Sets
..............................-----------------------------------------------------------4..........................
1b106RoadEquipmenl OffRoadEquipmentUnitAmount i 1.00 0.00
.............................4-----------------------------------------------------------4--------------------------
tbIOlfRoatlEquipment OffRoadEquipmenlUnit ount i 1.00 0.00
..............................-----------------------------------------------------------4..........................
1b106RoadEquipmenl OffRoadEquipmentUnitAmount i 2.00 0.00
..................-----------4-----------------------------------------------------------4..........................
IblProjectOharactenstics N20intensilyFactor i 0.006 0.00617
......................-------4-----------------------------------------------------------4..........................
iblProjedCharacteristics OperetionalVear i 2014 2022
.............................i-----------------------------}_____________________________4..........................
tblsolidWaste Solid WasteGenerationRate 1 1.86 0]0
...................---------- -----------------------------------------------------------4..........................
1blTripsMdVMT WorkerTripNumber i 3.00 0.00
..................P......._..4-----------------------------}_____________________________4..........................
tblVehicleTri s CC_TTP i 28.00 0.00
.............................4-----------........----------}_____________________________4..........................
tbNehicleTrips CNW_TTP i 13.00 0.00
---------
.........P......._..4---------------_H------------------------------------------4..........................
tbNehicleTri s CW_TTP 1 59.00 100.00
...........................................................+_____________________________4..........................
1blVehicleTripa DV_TP i 5.00 0.00
..................P......._..4-----------------------------}_____________________________4..........................
tbNehicleTri s PB_TP i 3.00 0.00
.............................4................-------------------------------------------4..........................
tbNehicleTrips PR_TP i 92.00 100.00
..................P......._..i-----------------------------}_____________ _____________4..........................
tbNehi.... s ST_TR i 1.50 1.33
............................. ------------.................}_____________________________4..........................
tbNehicleTrips SU_TR i 1.50 1.33
..................P......._..4-----------------------------}_____________ _____________4..........................
tblVehicleTri s WD_TR i 1.50 1.33
------------.....------------4-----------------------------------------------------------4..........................
tblWater AerobicPeroent r 87.46 97.54
.............................%n.e bimndF--------goonsP----}________________-------------4------------..............
tblWaler •AnaerobicantlFacultativeLagoonsPercenl+ 2.21 2.46
------------.....------------4-----------------------------------------------------------4..........................
tblWater IndoorWaterUseRate i 346,875.00 260,156.00
.............................4-----------------------------4------------------------------k..........................
tblWaler SepticTankPercent 10.33 0.00
2.0 Emissions Summary
CaIEEMod Version: CalEEMod.2013.2.2 Page 4 of 18 Date: 7/16/2016 10:31 PM
2.1 Overall Construction (Maximum Daily Emission)
Unmitigated Construction
ROG I NO. I 00 I 002 I Fugitive Ex6aun PM10 Fugitive Ex6ausl PM2.5 BIo-COF NBia-002 ToWICO2 GMN20 1 002.
PM10 I PM10 Total PM2.5 PM2.5 ToW
Veer IWday IWEay
2018 n 0.0743 1 0%21 0.5688 1 26600e- 1 00000 00288 1 0.0288 1 00000 1 00265 0.0265 • 00000 1267,6904126]69041 0N33 0,0000 1269,4405
.I
003 I ; i i ; I I I I
i
___________•I-------'--------
_-------'------- -------,-------'-------'_______�_______�_______�-------1 _ _ _ _ _I
2020 3.7184 1 1.8030 1 1.0314 1 2.9700e- i 0.0000 1 0.1109 1 0.1109 1 0.0000 1 0.1109 1 0.1109 • 0.0000 1281.4481 1 281.4481 i 0.0210 1 0.0000 1 201.9057
.I
I I I 003
•I I I I I I I i •
•I _______�_______�_______1 _ _ _ _ _
____ I
2021 504455 1 3.9D15 1 4.5011 1 7.9000e- i 0.00DD 1 0.2199 1 0.2199 1 0.0000 1 0.2199 1 0.2199 • 0.0000 I ]48.]240 i 748.7240 i 0.0432 1 0.0000 1 749.8303
I 1 I 003
I
TOW 62.2383 I 6.5474 6,9813 1 0.0135 1 0.0000 0.3596 1 0.3596 I 0.000 j 0.3573 1 0.3573 • 0.0000 11,297.862 11,297.8621 0.14 3 1 0.0000 1,300.976
11 4 4 4
Mitigated Construction
ROG NO. CO 002 Fugitive Ex6ausl PM10 Fugitive Ex6auM PM2.5 Bio-CO2 NBia-0O2 T.WICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Vear IWEay IWEay
2018 1 0 0743 1 0%21 0 5688 1 2 6600e- 1 0 0000 0 0288 1 00288 1 0 0000 j 0 0265 00265 • 0 0000 1 267 6904 1 267 69N 1 0 0933 0 0000 1 269 4405
003 1
.-------.-----------._.._,.......1------------------------._______........
2020 •I 33184 1 16838 i 1,8314 139]OO - i 00000 i 0.1109 i DA109 i 00000 01109 0.1f09 00000 128144811281 A4811 0.0218 i 0,0000 1281e057
003
1 ______1_______ _______'_______x_______ _______'_______;_______v_______.._._.._.. 1 0.0000 1
2021 A655 I 3.9015 I 6.5811 I ].90000- i 0.0000 I 0.2199 I 0.2199 I 0.0000 1 0.2199 0.2199 • 0.0000 I ]68.7240 i 748.]240 0.0632 58 0.0000 7496303
003
Tool 62.230 1 6.5474 6.9813 1 0.0136 1 0,0000 0,3696 1 0.3596 1 0.0000 0.3573 0.3673 • 0.0000 1,297.80211,297.8621 0.1483 0.0000 11,300.975
11 4 4 4
CaIEEMod Version: CaIEEMod.2013.2.2 Page 5 of 18 Date: 7/16/2016 10:31 PM
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive ExM1aua[ PM2.5 Bio-0O2 NBio-COY Total CO2 CH4 N20 CO
PM10 PM10 Total PM2.5 PM" Total
Percent 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 1 0.00 0.00 0.00 1 0.00 1 0.00 0.00 0.00
Reduction
CaIEEMod Version: CalEEMod.2013.2.2 Page 6 of 18 Date: 7/16/2016 10:31 PM
2.2 Overall Operational
Unmitigated Operational
ROG NOx I 00 I 502 I Fugitive Exbaun PM10 Fugitive Exbaust PM2.5 BIo-COF NBia-002 TotWICO2 CMN20 1 002.
PM10 I PM10 Total PM2.5 PM2.5 Total
category luear lueay
Area n 0.0297 r 00000 15000c l 0.0000 r 00000 r O.000O r 0WOO ; O.000O r 33000, l 3.3000e- I 0WOO r 35000e-
.r
ON r i i i r ON r 004 t i 004
________ •r -------_-------�-------- r
r t
Energy 0.0000 r O.W00 r 0.0000 r 0.0000 r r 0.0000 r 0.0000 r r 0.0000 ; 0.0000 • r 0.0000 r 0.0000 r 0.0000 r 0.0000 i 0.0000
t t t t i i r i i i t
•r r r r r r r r
-------_-------�-------- t
Mobile B.ZZOOe- l 0.0179 r 0.0841 r 3.4000e- l 0.0255 r 3.3000e- l 0.0258 r 6.8000e- l 3.1000e- ; 7.1100e- • r 25.2350 r 25.2350 r B.6000e- I i 25.2531
003 t t t 004 t i 004 t t 003 i 004 003 t t 004 i t
t
Total 0.0359 r 0.0179 r 0.0843 r 3A000e- r 0.0255 3.3000a- r 0.0258 r 8.8000e- 3.1000> 7.1100e- • r 25.3354 r 35.2354 r B.B000a- 0.0000 25.253d
004 ow oe3 Ba o03 ON
Mitigated Operational
ROG I NO. I CO I 502 I Fugitive ExbauM PM10 Fugitive Exbauet P. Bio-CO2 NBia-0O2 T.WICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category IWeay IWeay
Area r 00297 r 0WOO j 15000e- r 00000 r 00000 r 00000 r 00000 ; 00000 r 33000e- r 33000e- r 00000 j 35000e-
.� 1 ON 1 I 1 i ; I ON I 004 1 i i 004
...........a_______-_______________________ .......I_______._______._______._______------.
Energy •r Omm 00000 0.0000 0.0000 AOOOO 0.0000 0.0000 Omm r 0.0000 OOM 0.0000 0.0000 00000
........... ______i______ ______ -------i______I_______._______; r........................ ---------------r ___ . .....
Mobile 6.2200e- r 0.0179 0.0641 3.4000e- r 0.0255 3.3000e- 0.0258 t 6.8000e 3.1BBBe- ; 7.1100e- i 25.2360 25.2350 8.6000e 25.2531
003 t r ON r om t t 003 ON 003 r t ON
To I 0.030 r 0.0179 0.OM3 r 3.=. r 0.0256 3.3000e- r 0.0250 r 6.3000e- 3.1000e- 7.1100e- • 25.2354 r 25.2364 r B.B000e- g.0000 r 25.2534
11 eos o04 M ao4 003 004
CalEEMod Version: CalEEMod.2013.2.2 Page 7 of 18 Date: 7/16/2016 10:31 PM
ROG NOx CO 502 Fugitive Exhaust PM10 Fugitive Exhaust PM25 Bio-0O2 NBio-0O2 Total COT CH4 N20 CO2e
PM10 PM10 Total PM2.5 P1112.5 Total
Percent 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Retluctian
3.0 Construction Detail
Construction Phase
Phase Phase Name Phase Type Start Date End Date Num Days Num Days Phase Description
Number Week
1 •Dnll Rig Emissions Estimate lGrading 11/l/2018 11/1/2018 i 51 11
.......s........................{......................J------------4------------4--------4------"`-------------------------
2 •Architectural Coating for PS 1Arrhitectural Coating 112/15I2020 112/28I2020 51 101
........................or Tank ............Coating ......1-'-2021 1-_—----—_- _______
3 •Architecturel Coating For Tank :Architectural Coating •7111/2027 •71I30/2021 5• 22•
Acres of Grading (Site Preparation Phase): 0
Acres of Grading(Grading Phase): 0
Acres of Paving: 0
Residential Indoor: 0; Residential Outdoor: 0; Non-Residential Indoor: 70,720; Non-Residential Outdoor: 39,320 (Architectural Coating-sgft)
OffRoad Equipment
Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor
Architectural Coating For Tank lAir Compressors 1! 6.001 78: 0.48
Drill Rig Emissions Estimate 1... Drill Rigs . 7 7.001 500:--4 0.50
9 t i 1, 8.00 __-______ 841 0.74
Architectural Coatin For Tank rGenerelor Sets
............................:........................... {------------1""""'- _.........
Drill Rig Emissions Estimate 1.....t........ Saws 01 8.001 81• 0.73
............................t..._......_...._._.._._....__________.._..�_.__________' ----- 7;...._.........
Architectural Coating for PS tar Compressors 1! 8.00- 78' 0.48
Drill Rig Emissions Estimate I Tired Dozers 01 7.001 255• 0.40
-----
t k r
Drill Rig Emissions Estimate •TractorslLoatlerslBackhoes 0• 8.00' 9]• 0.3]
CalEEMod Version: CalEEMod.2013.2.2 Page 8 of 18 Date: 7/16/2016 10:31 PM
Trios and VMT
Phase Name ORroad Equipment I Worker Trip Vendor Trip Hauling Trip Worker Trip Vendor Trip Hauling Trip Worker Vehicle Vendor Hauling
Count Number Number Number Leni Length Length Class Vehicle Class Vehicle Class
Architectural Coating ! 1; 0.00• 0.001 0.00; 14.70' 6.90; 20.00I1D Mix IHDT_Mix iHHDT
. R............ ..............:..._.._..---------------------------------------4------------ -----...._.............
---------- -
Drill
Rig Emissions i 1; 0.00• --- --- 1--- 6.90; ---- - -- 1HDT_Mix I----
• r _4 • _4 _a- t r _♦
Architectural Coating 2• 0.00' 0.00' 0.00' 14.70• 6.90• 20.00•LD_Mix •HDT_Mix •HHDT
3.1 Mitigation Measures Construction
Clean Paved Roads
3.2 Drill Rig Emissions Estimate - 2018
Unmitigated Construction On-Site
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitve I Exhaust PM2.5 Blo-CO2 NBio-CO2 Tatal CO2 CH4 N20 CO2e
PM10 PM10 Total Pas PM2.5 TOUI
Category Iblday IWday
F,hfi,a Dust I 0.0000 0.0000 l 0.0000 l 00000 0.0000 ; 00000 • l 00000 0.0000
I I I I I
-----------_ _- _____II
I_______ _______ _______ ______
.I O. 43 I 0.9821 I 0.5888 2.8600 0.0288 0.028 0. 85 00285 1284
287.8904 ; 0.0633 l 289.4405
003 I
I
Total 0.01 I 0.9621 I 0.5888 I2.6601I 0.0000 I 0.0288 I 0.0288 I 0.0000 0.0265 0.020 • 1267.6904I 261I 0.0833 I 269.6008
11 003
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3.2 Drill Rig Emissions Estimate - 2018
Unmitigated Construction Off-Site
ROG NOx CO 502 Fugitive Exhaust PM10 Fugitve ExM1aust PM2.5 Blo-CO2 NBio-CO2 T.WICO2 CM N20 CO2e
PM10 PM10 Tolal PM2.5 PM2.5 Twat
Category IWday Iblday
Hauling n 00000 1 0.0000 ' 0.0000 ' 00000 ' Owito 1 0.0000 ' Omoo ' 00000 1 0.0000 00000 I 0.0000 ' 00000 1 0.0000 I 0.0000
.I
•I I I I I I I • '
__ _______�
I I
Vendor 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' O.W00 ' 0.0000 ' 0.0000 ' O.00DD ' 0.0000 ; 00000 • I O.00W ' O.00DD ' 0.0000 ' i 0.0000
•I
•I I I I I I I • I I
Worker 0.000D ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ; 00000 • I 0.0000 ' O.000D ' 0.0000 ' i 0.0000
I
Total 0.0000 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 0.0000 ' 0.0000 ' 0.0000 0.0000 0.0000 • ' 0.0000 ' 0.0000 0.0000 ' 0.0000
Mitigated Construction On-Site
ROG NOx CO 502 Fugitive ExM1auet PM10 Fugitive Exhaust PM25 Bo-CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category Iladay Iblday
F,Mve Dual • ' ' 00000 1 00000 ' 00000 ' 00000 1 00000 00000 • j 00000 i 0.000U
I I I • i
,I 1 I I 1 I I I I • • I I I
..� a • a ! ! a i -I 1 1 I 1
Off-Road •I 00T43 f 0.9621 i 0.5688 i 2.6600e- i 0.0288 ' 0.0288 ' 0.0285 00285 0.0000 1267s904 26Z69041 0.0833 1289 e405
003
i
Total 0.070 0.9621 ' 0.6688 ' 2.81 1 0.0000 0.0299 ' 0.0288 ' 0.0000 0.0205 0.0285 • 0.0000 1 287.8904 28).e9pd 0.0833 ' 209.4409
11 003
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3.2 Drill Rig Emissions Estimate - 2018
Mitigated Construction Off-Site
ROG NOx CO 502 Fugitive ExM1auat PM10 Fugitve ExM1aust PM2.5 Blo-CO2 NBio-CO2 TersICO2 CM N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Twat
Category IWday Iblday
Hauling n 00000 OOOOO ' 0.0000 ' 00000 ' Owito 0.0000 ' Omoo ' 00000 1 0.0000 ; 00000 i 0.0000 ' 00000 0.0000 I 0.0000
Vendor 9.9oao ' 0.0000 ' 9.0099 ' O.99ao ' 9.og99 ' 0.0000 ' 0.0000 ' 0.0oD0 ' 0.9900 ; Om i 0.0000 ' 0.0oD0 ' 0.0000 0.0000
i i i i i
a
Worker 0.000D ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ; 00000 0.0000 ' O.000D ' 0.0000 ' i 0.0000
i
Total 0.0000 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 0.0000 ' 0.0000 ' 0.0000 0.0000 0.0000 • ' 0.0000 ' 0.0000 0.0000 ' 0.0000
3.3 Architectural Coating for PS -2020
Unmitigated Construction On-Site
ROG NOx CO 502 Fugitive Exhaust PM10 Fugitive Exhau# PM25 Blo-CO2 NBio-CO2 To1aICO2 CH4 N20 I CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category Mey Iblday
I hlt Coating • 34763 j 00000 ' 00000 ' 00000 ; 00000 • j 00000 i 0.01M
• ' ' ' ' ' '
•� a • a �_______ _______ _______ _______1 ______
Off-Road 01422 ' 1.8838 ' 1.8314 ' 2.9]OOe- i i 0.1109 i 0.1109 i 0.1109 0.1109 261.4a81 2&1 A4E1 0.0218 i i 281 9057
003
i
Total 3.7181 1.038 ' 1.8314 ' 2.9700e- 1 0.1100 ' 0.1109 ' 0.1109 0.1109 • 211 1 1 281.4181 0.0218 ' MAW
003
CaIEEMod Version: CalEEMod.2013.2.2 Page 11 of 18 Date: 7/16/2016 10:31 PM
3.3 Architectural Coating for PS - 2020
Unmitigated Construction Off-Site
ROG NOx CO S02 Fugitive ExM1auet PM10 Fugitve ExM1aust PM2.5 Blo-CO2 NBio-CO2 T.WICO2 GM N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Twat
Category IWday Iblday
Hauling n 00000 OOOOO ' 0.0000 ' 00000 ' Owito 0.0000 ' 0.0000 ' 00000 1 0.0000 ; 00000 i 0.0000 ' 00000 0.0000 I 0.0000
__ _______
000 �
Vendor 0.0 ' 0.0000 ' 0.0000 ' 0.0000 ' O.W00 ' 0.0000 ' 0.0000 ' O.00DD ' 0.0000 ; 00000 • � 0.0000 ' O.00DD ' 0.0000 ' i 0.0000
a
Worker 0.000D ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ; 00000 0.0000 ' O.000D ' 0.0000 ' i 0.0000
i
Total 0.0000 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 0.0000 ' 0.0000 ' 0.0000 0.0000 0.0000 • ' 0.0000 ' 0.0000 0.0000 ' 0.0000
Mitigated Construction On-Site
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive Exhau# PM25 Blo-CO2 NBio-CO2 Total CO2 CH4 N20 I CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category Iladay Iblday
I hlt Coating • 34763 j 00000 ' 00000 ' 00000 ; 00000 • j 00000 0.0m
Off-Road •i (1d22 f 1.6838 1.8314 2.9]OOe- 0.1109 ' 0.1109 0.1109 0.1109 00000 i 281 A481 � 91 e481 f 0.0218 � � 281 9057
003
i
Total 3.7184 1.038 ' 1.8314 ' 2.97000- 1 0.1109 ' 0.1109 ' 0.1109 0.1109 • 0.0000 281771 ' 281 0.0218 ' 28i905]
003
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3.3 Architectural Coating for PS - 2020
Mitigated Construction Off-Site
ROG NOx CO S02 Fugitive ExM1auet PM10 FugiSve ExM1aust PM2.5 Blo-CO2 NBio-CO2 TersICO2 CM N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Twat
Category IWday Iblday
Hauling n 00000 00000 ' 0.0000 ' 00000 ' 00000 0.0000 ' 0.0000 ' 00000 1 0.0000 00000 i 0.0000 ' 00000 0.0000 I 0.0000
Vendor 9.9oao ' 0.0000 ' 9.0099 ' 0.99ao ' 9.og99 ' 0.0000 ' 0.0000 ' 0.0" ' 0.0900 00000 i 0.0000 ' 0.0oD0 ' 0.0000 0.0000
a
Worker 0.000D ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ; 00000 0.0000 ' O.000D ' 0.0000 ' i 0.0000
i
Total 0.0000 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 0.0000 ' 0.0009 ' 0.0000 0.0000 0.0000 • ' 0.0000 ' 0.0000 0.0000 ' 0.0000
3.4 Architectural Coating For Tank-2021
Unmitigated Construction On-Site
ROG NOx CO S02 Fugitive ExM1auet PM10 Fugitive Exhaust PM25 Bo-CO2 NBio-CO2 To1aICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category Mey Iblday
I hlt Coating 579586 j 00000 ' 00000 ' 00000 00000 • j 00000 0.000U
..A a • a ; ; a • .I 1 1 I t
Off-Road •, 0e8]0 i 3.9015 i 4.5811 ].9000e- i i 0.2199 ' 0.2199 ' 02199 03198 ]40]2ag , 748.]240 0.0432 ]498303
q 003 i
i
Total 581 3.9015 ' 4.5811 ' 7.9000e- 1 02109 ' 0.2199 ' 0.2190 0.2199 • 748.7240 1 748.7M 0."32
003
CaIEEMod Version: CalEEMod.2013.2.2 Page 13 of 13 Date: 7/16/2016 10:31 PM
3.4 Architectural Coating For Tank -2021
Unmitigated Construction Off-Site
ROG NOx CO 502 Fugitive ExM1auet PM10 Fugitve ExM1aust P12.5 Blo-CO2 NBio-CO2 TeraICO2 CM N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Twat
Category IWday Iblday
Hauling n 00000 00000 ' 0.0000 ' 00000 ' 00000 0.0000 ' 0.0000 ' 00000 1 0.0000 ; 00000 i 0.0000 ' 00000 0.0000 I 0.0000
Vendor 9.9aao ' o.og09 ' 9.9999 ' 9.99ao ' 9.0999 ' 0.9999 ' 9.9990 ' 9.9099 ' 0.9999 ; Om 9.9990 ' 9.9099 ' 0.0999 9.9oao
a
Worker 0.000D ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ; 00000 0.0000 ' O.000D ' 0.0000 ' i 0.0000
i
Total 0.0000 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 0.0000 ' 0.0000 ' 0.0000 0.0000 0.0000 • ' 0.0000 ' 0.0000 0.0000 ' 0.0000
Mitigated Construction On-Site
ROG NOx CO 502 Fugitive ExM1auet PM10 Fugitive Exhaust PM25 Bo-CO2 NBio-CO2 To1aICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category Iladay Iblday
I hlt Coating 579586 j 00000 ' 00000 ' 00000 ; 00000 • j 00000 0.000U
Off-Road •i (i f 3.9015 4.5811 7.9000e- 0.2199 ' 0.2199 ' 02199 01198 00000 i 748J240 ]48.7240 f 0.0432 ]498303
003
i
Total Si 3.9015 ' 4.5811 ' T.9000e. 1 01199 ' 0.2199 ' 0.2199 1 0.21" • 0.0000 1 7487240 749.7M 1 0.0432 ' 1 749.003
11 003
CaIEEMod Version: CaIEEMod.2013.2.2 Page 14 of 13 Date: 7/16/2016 10:31 PM
3.4 Architectural Coating For Tank -2021
Mitigated Construction Off-Site
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive ExM1aust PM2.5 Blo-CO2 NBio-CO2 TotaICO2 GM N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 TneaI
Category IWday IWday
Hauling n 00000 00000 ' 0.0000 ' 11 ' 00000 0.0000 ' 0.0000 ' 00000 1 0.0000 � 00000 i 0.0000 ' 00000 0.0000 1 0.0000
Ventlor g.gbbo ' o.og0g ' 9.66gg ' 6.gggo ' g.og99 ' o.Bggg ' g.gggo ' g.gogg ' o.B966 6ogoo • � 6.gggo ' g.gogg ' o.oggg ' 1 g.gobo
1 i i i i i i
a
Worker 0.000D ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ; 00000 0.0000 ' 0.000D ' 0.0000 ' I 0.0000
i
Total 0.0000 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 0.0000 ' 0.0000 ' 0.0000 0.0000 0.0000 • ' 0.0000 ' 0.0000 0.0000 ' 0.0000
4.0 Operational Detail - Mobile
4.1 Mitigation Measures Mobile
ROG I NO. 1 CO S02 Fugitive Exhaust PM10 Fugitiva Exdauat PM2ii F- 2
02 'Tina 02 CH4 N20 G02e
PM10 PM 10 TMaI PM2.5 PM2.5 TassI
cawgory IWday lblday
MNgatetl • 6.22008- 1 0.0179 i 0.0&41 1 3.40008- i 00255 3.3000s- 0.0258 i 6.8000a- 13.1000e- ; 7.1100.- . i 25.2350 � 8.6000e- 1 � 252531
1 003 004 004 003 004 003 1 004 i
......aced -_.._.-4._.0179 __.._.I-._.00.- _........_y__.._I-.002W .__..-F_.._._r-•1---_........{-.5,2350 ..-2350 _..__I_.__..e.......
Unmiagetetl 6.2200e- 0.01]9 0.0841 3.4000e- 00255 33000e- 0.0258 6.8000e- 3.1000e- ].1100e- 252350 252350 8.6000o- 252531
003 004 004 003 004 003 004
CaIEEMod Version: CalEEMod.2013.2.2 Page 15 of 18 Date: 7/16/2016 10:31 PM
4.2 Trip Summary Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMr
General Heavy Industry 2.00 2.00 2.00 12,055 12,055
Total 2.00 2.00 2.00 12,055 12,055
4.3 Trip Type Information
Mlles Trip% Trip Purpose%
Land Use H-W or C-W H-S or C-C H-O or C-NW H-W or C-W H-S or C-C I HA or C-NW I Primary I Diverted I Pass-by
General Heavy Industry 16.60 8,40 6.90 100,00 0,00 000 100 0 0
L0 LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCV SBUS MH
5043• 0,056653• 0 0.5 .194832• 0.151784• 0,042126• 0005989• 0.016072• 0.016505• 0.001461• 0.002178: 0.004464: 0.000494: 0.002401
g.g 4Fgglpypeta!I
Historical Energy Use: N
5.1 Mitigation Measures Energy
ROG NO. CO I S02 I Fugitive Exhaust PM10 Fugitive Exhaust PM2.5 Blo-CO2 NBio-CO2 TotaICO2 CH4 N20 002s
PM10 PM TOUI PM2S PM2.5 TOUI
Category Wday IWda,
NalumlGas v 0.0000 0.0000 I 0,0000 I 00000 I i 0.0000 I 0.0000 I 0.0000 0.0000 i 0.0000 0.0000 1 0.0000 1 0.0000 00000
Miligatetl
NaluralGas •• OOOOD 0.0000 0.0000 00000 0.0000 0.0000 0.0000 00000 0.0000 OOOOD O.OD00 0.0000 00000
unmiogatea
CaIEEMod Version: CalEEMod.2013.2.2 Page 16 of 18 Date: 7/16/2016 10:31 PM
5.2 Energy by Land Use - NaturalGas
Unmitigated
NaturalGa ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM2.5 Bia-002 1 NBb CO2 Total 002 1 CH6 I N20 1 CO2e
.Use PM10 PM10 Total PM2.5 PM2.5 TOWI
Land Use kBTUNr Ihlday dday
General Has 0 n 0.0000 0.0000 OOCOD 0.D000 00000 0.OD00 0.0000 0.0000 • 0.0000 0.0000 0.0000 0.0005 O.o000
Industry
i
Total • 0.0000 1 0.0000 ' 0.0000 0.0000 0.0000 O.00oo 1 0.0000 0.0000 • 0.0000 0.0000 1 0.0000 ' O.000o 0.0000
Mitigated
Natu.IGa ROG NOx 00 502 Fugftive Exhaust PM10 Fugitive Exhaust PM2.5 Bio-0O2 I NBio-0O2 TOWI CO2 I CH4 I N20 I CO2e
s Use PM10 PM10 TOWI PM2.5 PM2.5 TOWI
Land Use kBTUN'r Ib/day May
General rvea, 0 o D000 o 0000 0 DODD a DDoo ' 0 0000 ' a D000 ' o ooaa a ODoo • a ODDO 0 0000 o 0000 a DODO o D000
ToM 0.0000 ' 0.0000 1 0.0000 0.0000 ' 0.0000 1 0.0000 ' 0.0000 0.0000 O.ODDO 0.0000 ' 0.0000 1 O.00DD a.D000
6.0 Area Detail
6.1 Mitigation Measures Area
CaIEEMod Version: CaIEEMod.2013.2.2 Page 17 of 18 Date: 7/16/2016 10:31 PM
ROG NO. CO 502 Fu9i4ve Exhaust PM10 Fugitive Exhaust PM2.5 Bio-CO2 NBie-0O2 T.Wi CO2 OMN20 002.
PM10 PM10 Total PM2.5 PM2.5 Total
category IbleaY IWeay
Mitigated n 0.0297 ' 00000 1 1.5000, I 0.0000 ' 1 0.0000 ' 0.0000 I 00000 0.0000 • 133000e- 13.3000e- I 00000 1 ' 3.5000e-
i ON ON I 004 I i 000
I I '
•I I I I I I i ' I I
...........
'~.-..- ..--.. .-----________ ------
Unmitigated •• 0.029] 0.0000 15000e- 0.0000 0.0000 0.0000 0.0000 0.0000 3.3000a- 3.3000e- 0.0000 3.5000e-
ON ON 004 004
6.2 Area by SubCategory
Unmitigated
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM2.5 Bio-0O2 N8io-0O2 Total CO2 CHO I N20 I CO2e
PM10 PM10 Total PM25 PM2.5 Tolal
3ubCategory lWday lWday
Nchitectuvii •I 0.0000 I 0.0000 0.0000 1 0.0000 0.0000 • 0.0000 I 0.0000
Coating I I '
, I I � I 1 I • ,
rer d a a a a a ; I1
t t 10297 0.0000 0.0000 0.000 0.0000 0.0000 0.0000
Phodusta Lentlacaping 1.000Oe- I 0.0000 1 1.50001 I 0.0000 I 0.0000 I 0.0000 i I 0.0000 0.0000 • 13.3000e- j 3.3000e- j 0.0000 j 3.50001
005 009 ON OOd I 9ga
i i I i i i i
Tail0.029T 0.0000 1.5000a, 0.0000 0.0000 0.0000 0.0000 0.0000 • ' 3.3000e- 3.3000e- 0.0000 ' 3.5000e-
ON 0. 000 004
CaIEEMod Version: CalEEMod.2013.2.2 Page 18 of 18 Date: 7/16/2016 10:31 PM
6.2 Area by SubCategory
Mitigated
ROG NO. CO S02 Fugitve EMaua PM10 Fugitive Exbausl PM2.5 Blo-CO2 NBic-002 Told CO2 CMN20 1 002a
PM10 PM10 Tolal PM2.5 PM2.5 Tolal
SubCategory Ibltlay Ibltlay
Consumer I 0.0297 I 00000 I 0.0000 I 1 000oo � 0.0000 I 00000 I 1 00000
Proau dt i i I i i I
I I I I
q 1 I I I • �
I I I I I I •
• _♦ _� _� _� _� _� _i_______ _______�_______I ______ ______ _______I ______
I I I
006 0
Lantlscaping v 1.WOOe- I O.W00 1 1 S 0OOOe- i 0.0000 I I 0.0000 I 0.0000 I I 0.0000 0.0000 13.300De- i 3.3000e- I 0.0000 I 13.S000e-
005 I i 00 I i I i I ONI I I I
I •
'I I I I I I I • I I I
ArMOectu2l v 0.0000 I I I I I 0.0000 I 0.0000 I I O.ODoO � 0.0000 • I 0.0000 I I I --0.0000
coating i i i i I
I
TZI 0.0297 I 0.0000 1.5000a. I 0.0000 I 0.0000 I 0.0000 I 0.0000 0.0000 • 13.=. 13.3000e- I 0.0000 I 3.50000-
o0a ooa o0a Bna
7.0 Water Detail
7.1 Mitigation Measures Water
8.0 Waste Detail
8.1 Mitigation Measures Waste
9.0 Operational Offroad
Equipment Type Number Hours Day Days(Year Horse Power Load Factor Fuel Type
10.0 Vegetation
CaIEEMod Version: CalEEMod.2013.2.2 Page 1 of 18 Date: 7/16/2016 10:30 PM
EQ FLow Tank
Orange County, Summer
1.0 Project Characteristics
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population
General Heavy Industry 1.50 10001 0.03 1,501 0
1.2 Other Project Characteristics
Urbanization Urban Wind Speed(ri 2.2 Precipitation Freq(Days) 30
Climate Zone 8 Operational Year 2022
Utility Company Southern California Edison
CO2 Intensity 630.89 CH4 Intensity 0,029 N20 Intensity 0.00617
(Ibllilli QbIMWhr) (lb/MWhr)
1.3 User Entered Comments & Non-Default Data
CalEEMod Version: CalEEMod.2013.2.2 Page 2 of 18 Date: 7/16/2016 10:30 PM
Project Characteristics- Determination of emissions for Dril Rig,Architectural Coating Emissions, and operational Activities
Land Use-
Construction Phase- Building and Tank Architectural Coating and Dril Rig Emission factor determination only
Off-road Equipment-See Assumptions
Off-road Equipment- Generator for use with sand blaster for prepping tank for coating
Trips and VMT-See Assumptions
Architectural Coating-See Assumptions
Vehicle Trips-See Assumptions
Area Coating-See Assumptions
Landscape Equipment-See Assumptions
Energy Use-See Assumptions
Water And Wastewater-See Assumptions
Solid Waste-See Assumptions
Construction Off-road Equipment Mitigation-
Off-road Equipment-
Table Name Column Name Default Value New Value
tblArchitecturalCoating Consb%rea_Nomesidential_Extenor 750.00 39,320.00
......................9------i-----------------------------}_____________________________�......... 70,72 ............
tblkchitecturalCoatin Consbkrea_Nome.idential_Imenor 2,250.00 ]0,]20.00
------------------ng--------- --------------n-----rcent-----i.______________'O ?------------ U ------.----.
Ratel
tblAreaCoati
.............................i-----------------------------}-----------------------------4..........................
tblConstructionPhase NumDdys 5.00 22.00
-----------------------------{-----------------------------
}--------------
5.__00-------------------------1--0.00------------.
tblConstructionPhase NumDaye
.............................i-----------------------------}-----------------------------4..........................
tblConstructionPhase NumDdys 2.00 1.00
-------tblConstructionPhase----------------------4-----------------------------t-----------1Y27Y2021 ----------?---------11/30/-------------
PhaseEndDatei
tblConstructionPhase -----------PhaseEndDate r ---- -- --------
r
12/2812020
-------tblConstructionPhase ------ ---------PhaseStanDate --------------------
12/292020----------?--------- 11/12021 --- - -
.............................i-----------------------------------------------------------4..........................
tblConstructionPhase PhaseStartDate 1/2/2018 1VI512020
-----------------------------4-----------------------------4------------------------------ --------------------------
tblEnergyUse NT24NG 6.86 0.00
CalEEMod Version: CalEEMod.2013.2.2 Page 3 of 18 Date: 7/16/2016 10:30 PM
tblEnergyUse T24NG 14.78 0.00
................q.P......._.. ----------.........----------¢------------ ------------4..........................
t i&iRoatlE ui ment Horse Power i 205.00 500.00
..............................-----------------------------------------------------------4..........................
1b106RoadEquipmenl OflRoadEquipmentType i Bore/Drill Rigs
.............................4-----------------------------------------------------------4--------------------------
tbIOlfRoatlEquipment OflRoadEquipmenlType i Genemlor Sets
..............................-----------------------------------------------------------4..........................
1b106RoadEquipmenl OffRoadEquipmentUnitAmount i 1.00 0.00
.............................4-----------------------------------------------------------4--------------------------
tbIOlfRoatlEquipment OffRoadEquipmenlUnit ount i 1.00 0.00
..............................-----------------------------------------------------------4..........................
1b106RoadEquipmenl OffRoadEquipmentUnitAmount i 2.00 0.00
..................-----------4-----------------------------------------------------------4..........................
IblProjectOharactenstics N20intensilyFactor i 0.006 0.00617
......................-------4-----------------------------------------------------------4..........................
iblProjedCharacteristics OperetionalVear i 2014 2022
.............................i-----------------------------}_____________________________4..........................
tblsolidWaste Solid WasteGenerationRate 1 1.86 0]0
...................---------- -----------------------------------------------------------4..........................
1blTripsMdVMT WorkerTripNumber i 3.00 0.00
..................P......._..4-----------------------------}_____________________________4..........................
tblVehicleTri s CC_TTP i 28.00 0.00
.............................4-----------........----------}_____________________________4..........................
tbNehicleTrips CNW_TTP i 13.00 0.00
---------
.........P......._..4---------------_H------------------------------------------4..........................
tbNehicleTri s CW_TTP 1 59.00 100.00
...........................................................+_____________________________4..........................
1blVehicleTripa DV_TP i 5.00 0.00
..................P......._..4-----------------------------}_____________________________4..........................
tbNehicleTri s PB_TP i 3.00 0.00
.............................4................-------------------------------------------4..........................
tbNehicleTrips PR_TP i 92.00 100.00
..................P......._..i-----------------------------}_____________ _____________4..........................
tbNehi.... s ST_TR i 1.50 1.33
............................. ------------.................}_____________________________4..........................
tbNehicleTrips SU_TR i 1.50 1.33
..................P......._..4-----------------------------}_____________ _____________4..........................
tblVehicleTri s WD_TR i 1.50 1.33
------------.....------------4-----------------------------------------------------------4..........................
tblWater AerobicPeroent r 87.46 97.54
.............................%n.e bimndF--------goonsP----}________________-------------4------------..............
tblWaler •AnaerobicantlFacultativeLagoonsPercenl+ 2.21 2.46
------------.....------------4-----------------------------------------------------------4..........................
tblWater IndoorWaterUseRate i 346,875.00 260,156.00
.............................4-----------------------------4------------------------------k..........................
tblWaler SepticTankPercent 10.33 0.00
2.0 Emissions Summary
CaIEEMod Version: CalEEMod.2013.2.2 Page 4 of 18 Date: 7/16/2016 10:30 PM
2.1 Overall Construction (Maximum Daily Emission)
Unmitigated Construction
ROG I NO. I 00 I 002 I Fugitive Ex6aun PM10 Fugitive Ex6ausl PM2.5 BIo-COF NBia-002 ToWICO2 GMN20 1 002.
PM10 I PM10 Total PM2.5 PM2.5 ToW
Veer IWday IWEay
2018 n 0.0743 1 0%21 0.5688 1 26600e- 1 00000 00288 1 0.0288 1 00000 1 00265 0.0265 • 00000 1267,6904126]69041 0N33 0,0000 1269,4405
.I
003 I ; i i ; I I I I
i
___________•I-------'--------
_-------'------- -------,-------'-------'_______�_______�_______�-------1 _ _ _ _ _I
2020 3.7184 1 1.8030 1 1.0314 1 2.9700e- i 0.0000 1 0.1109 1 0.1109 1 0.0000 1 0.1109 1 0.1109 • 0.0000 1281.4481 1 281.4481 i 0.0210 1 0.0000 1 201.9057
.I
I I I 003
•I I I I I I I i •
•I _______�_______�_______1 _ _ _ _ _
____ I
2021 504455 1 3.9D15 1 4.5011 1 7.9000e- i 0.00DD 1 0.2199 1 0.2199 1 0.0000 1 0.2199 1 0.2199 • 0.0000 I ]48.]240 i 748.7240 i 0.0432 1 0.0000 1 749.8303
I 1 I 003
I
TOW 62.2383 I 6.5474 6,9813 1 0.0135 1 0.0000 0.3596 1 0.3596 I 0.000 j 0.3573 1 0.3573 • 0.0000 11,297.862 11,297.8621 0.14 3 1 0.0000 1,300.976
11 4 4 4
Mitigated Construction
ROG NO. CO 002 Fugitive Ex6ausl PM10 Fugitive Ex6auM PM2.5 Bio-CO2 NBia-0O2 T.WICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Vear IWEay IWEay
2018 1 0 0743 1 0%21 0 5688 1 2 6600e- 1 0 0000 0 0288 1 00288 1 0 0000 j 0 0265 00265 • 0 0000 1 267 6904 1 267 69N 1 0 0933 0 0000 1 269 4405
003 1
.-------.-----------._.._,.......1------------------------._______........
2020 •I 33184 1 16838 i 1,8314 139]OO - i 00000 i 0.1109 i DA109 i 00000 01109 0.1f09 00000 128144811281 A4811 0.0218 i 0,0000 1281e057
003
1 ______1_______ _______'_______x_______ _______'_______;_______v_______.._._.._.. 1 0.0000 1
2021 A655 I 3.9015 I 6.5811 I ].90000- i 0.0000 I 0.2199 I 0.2199 I 0.0000 1 0.2199 0.2199 • 0.0000 I ]68.7240 i 748.]240 0.0632 58 0.0000 7496303
003
Tool 62.230 1 6.5474 6.9813 1 0.0136 1 0,0000 0,3696 1 0.3596 1 0.0000 0.3573 0.3673 • 0.0000 1,297.80211,297.8621 0.1483 0.0000 11,300.975
11 4 4 4
CaIEEMod Version: CaIEEMod.2013.2.2 Page 5 of 18 Date: 7/16/2016 10:30 PM
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM2.5 Bio-0O2 NBio-COY Total CO2 CH4 N20 CO2
PM10 PM10 Total PM2.5 PM" Total
Percent 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 1 0.00 0.00 0.00 1 0.00 1 0.00 0.00 1 0.00
Reduction
CaIEEMod Version: CalEEMod.2013.2.2 Page 6 of 18 Date: 7/16/2016 10:30 PM
2.2 Overall Operational
Unmitigated Operational
ROG NOx I 00 I 502 I Fugitive Exbaun PM10 Fugitive Exbaust PM2.5 BIo-COF NBio-002 TotWICO2 CMN20 1 002.
PM10 I PM10 Total PM2.5 PM2.5 Total
category Wear IWeay
Area n 0.0297 r 00000 15000c I 0.0000 r 00000 r O.000O r 0WOO ; O.000O r 33000, 13.3000e- I 0WOO r 35000e-
.r
ON r i i i r ON r 004 t i 004
________ •r -------_-------�-------- r
r t
Energy 0.0000 r O.W00 r 0.0000 r 0.0000 r r 0.0000 r 0.0000 r r 0.0000 ; 0.0000 • r 0.0000 r 0.0000 r 0.0000 r 0.0000 i 0.0000
t t t t i i r i i i t
•r r r r r r r r
-------_-------�-------- t
Mobile 8.0100e- I 0.0189 r 0.0876 r 3.5000e- I 0.0255 r 3.3000e- I 0.0258 r 6.8000e- 13.1000e- ; 7.1100e- • r 28.3875 r 28.3675 r B.6000e- I i 28.3855
003 t t t 004 t i 004 t t 003 i 004 003 t t 004 i t
t
Total 0.035J r 0.0188 r 0.06]6 r 3.5000e- r 0.0255 3.3000a- r 0.0258 r 8.8000e- 3.1000> J.1100e- • r 26.3678 r 36.3878 r 8.6000> 0.0000 28.3659
000 001 003 0,0 003 004
Mitigated Operational
ROG I NO. I CO I 502 I Fugitive ExbauM PM10 Fugitive Exhaust P. Bio-CO2 NBia-0O2 T.WICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category IWeay IWeay
Area r 00297 r 0WOO j 15000e- r 00000 r 00000 r 00000 r 00000 ; 00000 r 33000e- r 33000e- r 00000 j 35000e-
,� I ON 1 I 1 i ; ON I 004 1 i i 004
...........,I_-----------____-------_-----------------------.------- ________._._.._,.......I_______._______._______a-------i.......
Energy •r Omm 0.0000 0.0000 0.0000 f 0.0000 0.0000 f 0.0000 Omm r 0.0000 OOM 0.0000 0.0000 1 00000
• r r r r r r r r , r
...........•r x_______ _______'_______x_______ _______a_______'_______v_______�._._.._�......._____ I________---------------_-------- ------
Mobile 8.0100e- 0.0189 t 0.0876 t 3.5000e- 0.0255 3.3000e- 0.0258 t 8.8000e- 3.1000o- ; 7.11o0e- r 26.3675 28.3675 8.6000e- 263855
003 t i r 004 t 004 t t 003 00! 003 t 04 0
Tobl 0.0357 r 0.0180 0.0879 r 3.S000e- r 0.0255 a.aaeee- r 0.0258 r B.8000e- 3.1000e- 7.1100e- • 26.3678 r 20.3670 r 8.6000e- 0.0000 r 26.3a59
11 004 004 003 000 003 004
CalEEMod Version: CalEEMod.2013.2.2 Page 7 of 18 Date: 7/16/2016 10:30 PM
ROG NOx CO 502 Fugitive Exhaust PM10 Fugitive Exhaust PM25 Bio-0O2 NBio-0O2 Total COT CH4 N20 CO2e
PM10 PM10 Total PM2.5 P1112.5 Total
Percent 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Retluctian
3.0 Construction Detail
Construction Phase
Phase Phase Name Phase Type Start Date End Date Num Days Num Days Phase Description
Number Week
1 •Dnll Rig Emissions Estimate lGrading 11/l/2018 11/1/2018 i 51 11
.......s........................{......................J------------4------------4--------4------"`-------------------------
2 •Architectural Coating for PS 1Arrhitectural Coating 112/15I2020 112/28I2020 51 101
........................or Tank ............Coating ......1-'-2021 1-_—----—_- _______
3 •Architecturel Coating For Tank :Architectural Coating •7111/2027 •71I30/2021 5• 22•
Acres of Grading (Site Preparation Phase): 0
Acres of Grading(Grading Phase): 0
Acres of Paving: 0
Residential Indoor: 0; Residential Outdoor: 0; Non-Residential Indoor: 70,720; Non-Residential Outdoor: 39,320 (Architectural Coating-sgft)
OffRoad Equipment
Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor
Architectural Coating For Tank lAir Compressors 1! 6.001 78: 0.48
Drill Rig Emissions Estimate 1... Drill Rigs . 7 7.001 500:--4 0.50
9 t i 1, 8.00 __-______ 841 0.74
Architectural Coatin For Tank rGenerelor Sets
............................:........................... {------------1""""'- _.........
Drill Rig Emissions Estimate 1.....t........ Saws 01 8.001 81• 0.73
............................t..._......_...._._.._._....__________.._..�_.__________' ----- 7;...._.........
Architectural Coating for PS tar Compressors 1! 8.00- 78' 0.48
Drill Rig Emissions Estimate I Tired Dozers 01 7.001 255• 0.40
-----
t k r
Drill Rig Emissions Estimate •TractorslLoatlerslBackhoes 0• 8.00' 9]• 0.3]
CalEEMod Version: CalEEMod.2013.2.2 Page 8 of 18 Date: 7/16/2016 10:30 PM
Trios and VMT
Phase Name ORroad Equipment I Worker Trip Vendor Trip Hauling Trip Worker Trip Vendor Trip Hauling Trip Worker Vehicle Vendor Hauling
Count Number Number Number Leni Length Length Class Vehicle Class Vehicle Class
Architectural Coating ! 1; 0.00• 0.001 0.00; 14.70' 6.90; 20.00I1D Mix IHDT_Mix iHHDT
. R............ ..............:..._.._..---------------------------------------4------------ -----...._.............
---------- -
Drill
Rig Emissions i 1; 0.00• --- --- 1--- 6.90; ---- - -- 1HDT_Mix I----
• r _4 • _4 _a- t r _♦
Architectural Coating 2• 0.00' 0.00' 0.00' 14.70• 6.90• 20.00•LD_Mix •HDT_Mix •HHDT
3.1 Mitigation Measures Construction
Clean Paved Roads
3.2 Drill Rig Emissions Estimate - 2018
Unmitigated Construction On-Site
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitve I Exhaust PM2.5 Blo-CO2 NBio-CO2 Tatal CO2 CH4 N20 CO2e
PM10 PM10 Total Pas PM2.5 TOUI
Category Iblday IWday
F,hfi,a Dust I 0.0000 0.0000 l 0.0000 l 00000 0.0000 ; 00000 • l 00000 0.0000
I I I I I
-----------_ _- _____II
I_______ _______ _______ ______
.I O. 43 I 0.9821 I 0.5888 2.8600 0.0288 0.028 0. 85 00285 1284
287.8904 ; 0.0633 l 289.4405
003 I
I
Total 0.01 I 0.9621 I 0.5888 I2.6601I 0.0000 I 0.0288 I 0.0288 I 0.0000 0.0265 0.020 • 1267.6904I 261I 0.0833 I 269.6008
11 003
CaIEEMod Version: CalEEMod.2013.2.2 Page 9 of 18 Date: 7/16/2016 10:30 PM
3.2 Drill Rig Emissions Estimate - 2018
Unmitigated Construction Off-Site
ROG NOx CO 502 Fugitive Exhaust PM10 Fugitve ExM1aust PM2.5 Blo-CO2 NBio-CO2 T.WICO2 CM N20 CO2e
PM10 PM10 Tolal PM2.5 PM2.5 Twat
Category IWday Iblday
Hauling n 00000 1 0.0000 ' 0.0000 ' 00000 ' Owito 1 0.0000 ' Omoo ' 00000 1 0.0000 00000 I 0.0000 ' 00000 1 0.0000 I 0.0000
.I
•I I I I I I I • '
__ _______�
I I
Vendor 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' O.W00 ' 0.0000 ' 0.0000 ' O.00DD ' 0.0000 ; 00000 • I O.00W ' O.00DD ' 0.0000 ' i 0.0000
•I
•I I I I I I I • I I
Worker 0.000D ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ; 00000 • I 0.0000 ' O.000D ' 0.0000 ' i 0.0000
I
Total 0.0000 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 0.0000 ' 0.0000 ' 0.0000 0.0000 0.0000 • ' 0.0000 ' 0.0000 0.0000 ' 0.0000
Mitigated Construction On-Site
ROG NOx CO 502 Fugitive ExM1auet PM10 Fugitive Exhaust PM25 Bo-CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category Iladay Iblday
F,Mve Dual • ' ' 00000 1 00000 ' 00000 ' 00000 1 00000 00000 • j 00000 i 0.000U
I I I • i
,I 1 I I 1 I I I I • • I I I
..� a • a ! ! a i -I 1 1 I 1
Off-Road •I 00T43 f 0.9621 i 0.5688 i 2.6600e- i 0.0288 ' 0.0288 ' 0.0285 00285 0.0000 1267s904 26Z69041 0.0833 1289 e405
003
i
Total 0.070 0.9621 ' 0.6688 ' 2.81 1 0.0000 0.0299 ' 0.0288 ' 0.0000 0.0205 0.0285 • 0.0000 1 287.8904 28).e9pd 0.0833 ' 209.4409
11 003
CaIEEMod Version: CalEEMod.2013.2.2 Page 10 of 18 Date: 7/16/2016 10:30 PM
3.2 Drill Rig Emissions Estimate - 2018
Mitigated Construction Off-Site
ROG NOx CO 502 Fugitive ExM1auat PM10 Fugitve ExM1aust PM2.5 Blo-CO2 NBio-CO2 TersICO2 CM N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Twat
Category IWday Iblday
Hauling n 00000 OOOOO ' 0.0000 ' 00000 ' Owito 0.0000 ' Omoo ' 00000 1 0.0000 ; 00000 i 0.0000 ' 00000 0.0000 I 0.0000
Vendor 9.9oao ' 0.0000 ' 9.0099 ' O.99ao ' 9.og99 ' 0.0000 ' 0.0000 ' 0.0oD0 ' 0.9900 ; Om i 0.0000 ' 0.0oD0 ' 0.0000 0.0000
i i i i i
a
Worker 0.000D ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ; 00000 0.0000 ' O.000D ' 0.0000 ' i 0.0000
i
Total 0.0000 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 0.0000 ' 0.0000 ' 0.0000 0.0000 0.0000 • ' 0.0000 ' 0.0000 0.0000 ' 0.0000
3.3 Architectural Coating for PS -2020
Unmitigated Construction On-Site
ROG NOx CO 502 Fugitive Exhaust PM10 Fugitive Exhau# PM25 Blo-CO2 NBio-CO2 To1aICO2 CH4 N20 I CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category Mey Iblday
I hlt Coating • 34763 j 00000 ' 00000 ' 00000 ; 00000 • j 00000 i 0.01M
• ' ' ' ' ' '
•� a • a �_______ _______ _______ _______1 ______
Off-Road 01422 ' 1.8838 ' 1.8314 ' 2.9]OOe- i i 0.1109 i 0.1109 i 0.1109 0.1109 261.4a81 2&1 A4E1 0.0218 i i 281 9057
003
i
Total 3.7181 1.038 ' 1.8314 ' 2.9700e- 1 0.1100 ' 0.1109 ' 0.1109 0.1109 • 211 1 1 281.4181 0.0218 ' MAW
003
CaIEEMod Version: CalEEMod.2013.2.2 Page 11 of 18 Date: 7/16/2016 10:30 PM
3.3 Architectural Coating for PS - 2020
Unmitigated Construction Off-Site
ROG NOx CO S02 Fugitive ExM1auet PM10 Fugitve ExM1aust PM2.5 Blo-CO2 NBio-CO2 T.WICO2 GM N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Twat
Category IWday Iblday
Hauling n 00000 OOOOO ' 0.0000 ' 00000 ' Owito 0.0000 ' 0.0000 ' 00000 1 0.0000 ; 00000 i 0.0000 ' 00000 0.0000 I 0.0000
__ _______
000 �
Vendor 0.0 ' 0.0000 ' 0.0000 ' 0.0000 ' O.W00 ' 0.0000 ' 0.0000 ' O.00DD ' 0.0000 ; 00000 • � 0.0000 ' O.00DD ' 0.0000 ' i 0.0000
a
Worker 0.000D ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ; 00000 0.0000 ' O.000D ' 0.0000 ' i 0.0000
i
Total 0.0000 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 0.0000 ' 0.0000 ' 0.0000 0.0000 0.0000 • ' 0.0000 ' 0.0000 0.0000 ' 0.0000
Mitigated Construction On-Site
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive Exhau# PM25 Blo-CO2 NBio-CO2 Total CO2 CH4 N20 I CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category Iladay Iblday
I hlt Coating • 34763 j 00000 ' 00000 ' 00000 ; 00000 • j 00000 0.0m
Off-Road •i (1d22 f 1.6838 1.8314 2.9]OOe- 0.1109 ' 0.1109 0.1109 0.1109 00000 i 281 A481 � 91 e481 f 0.0218 � � 281 9057
003
i
Total 3.7184 1.038 ' 1.8314 ' 2.97000- 1 0.1109 ' 0.1109 ' 0.1109 0.1109 • 0.0000 281771 ' 281 0.0218 ' 28i905]
003
CaIEEMod Version: CalEEMod.2013.2.2 Page 12 of 18 Date: 7/16/2016 10:30 PM
3.3 Architectural Coating for PS - 2020
Mitigated Construction Off-Site
ROG NOx CO S02 Fugitive ExM1auet PM10 FugiSve ExM1aust PM2.5 Blo-CO2 NBio-CO2 TersICO2 CM N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Twat
Category IWday Iblday
Hauling n 00000 00000 ' 0.0000 ' 00000 ' 00000 0.0000 ' 0.0000 ' 00000 1 0.0000 00000 i 0.0000 ' 00000 0.0000 I 0.0000
Vendor 9.9oao ' 0.0000 ' 9.0099 ' 0.99ao ' 9.og99 ' 0.0000 ' 0.0000 ' 0.0" ' 0.0900 00000 i 0.0000 ' 0.0oD0 ' 0.0000 0.0000
a
Worker 0.000D ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ; 00000 0.0000 ' O.000D ' 0.0000 ' i 0.0000
i
Total 0.0000 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 0.0000 ' 0.0009 ' 0.0000 0.0000 0.0000 • ' 0.0000 ' 0.0000 0.0000 ' 0.0000
3.4 Architectural Coating For Tank-2021
Unmitigated Construction On-Site
ROG NOx CO S02 Fugitive ExM1auet PM10 Fugitive Exhaust PM25 Bo-CO2 NBio-CO2 To1aICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category Mey Iblday
I hlt Coating 579586 j 00000 ' 00000 ' 00000 00000 • j 00000 0.000U
..A a • a ; ; a • .I 1 1 I t
Off-Road •, 0e8]0 i 3.9015 i 4.5811 ].9000e- i i 0.2199 ' 0.2199 ' 02199 03198 ]40]2ag , 748.]240 0.0432 ]498303
q 003 i
i
Total 581 3.9015 ' 4.5811 ' 7.9000e- 1 02109 ' 0.2199 ' 0.2190 0.2199 • 748.7240 1 748.7M 0."32
003
CaIEEMod Version: CalEEMod.2013.2.2 Page 13 of 13 Date: 7/16/2016 10:30 PM
3.4 Architectural Coating For Tank -2021
Unmitigated Construction Off-Site
ROG NOx CO 502 Fugitive ExM1auet PM10 Fugitve ExM1aust P12.5 Blo-CO2 NBio-CO2 TeraICO2 CM N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Twat
Category IWday Iblday
Hauling n 00000 00000 ' 0.0000 ' 00000 ' 00000 0.0000 ' 0.0000 ' 00000 1 0.0000 ; 00000 i 0.0000 ' 00000 0.0000 I 0.0000
Vendor 9.9aao ' o.og09 ' 9.9999 ' 9.99ao ' 9.0999 ' 0.9999 ' 9.9990 ' 9.9099 ' 0.9999 ; Om 9.9990 ' 9.9099 ' 0.0999 9.9oao
a
Worker 0.000D ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ; 00000 0.0000 ' O.000D ' 0.0000 ' i 0.0000
i
Total 0.0000 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 0.0000 ' 0.0000 ' 0.0000 0.0000 0.0000 • ' 0.0000 ' 0.0000 0.0000 ' 0.0000
Mitigated Construction On-Site
ROG NOx CO 502 Fugitive ExM1auet PM10 Fugitive Exhaust PM25 Bo-CO2 NBio-CO2 To1aICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category Iladay Iblday
I hlt Coating 579586 j 00000 ' 00000 ' 00000 ; 00000 • j 00000 0.000U
Off-Road •i (i f 3.9015 4.5811 7.9000e- 0.2199 ' 0.2199 ' 02199 01198 00000 i 748J240 ]48.7240 f 0.0432 ]498303
003
i
Total Si 3.9015 ' 4.5811 ' T.9000e. 1 01199 ' 0.2199 ' 0.2199 1 0.21" • 0.0000 1 7487240 749.7M 1 0.0432 ' 1 749.003
11 003
CaIEEMod Version: CaIEEMod.2013.2.2 Page 14 of 13 Date: 7/16/2016 10:30 PM
3.4 Architectural Coating For Tank -2021
Mitigated Construction Off-Site
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitve ExM1aust PM2.5 Blo-CO2 NBio-CO2 TotaICO2 GM N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 TneaI
Category IWday IWday
Hauling n 00000 00000 ' 0.0000 ' 11 ' 00000 0.0000 ' 0.0000 ' 00000 1 0.0000 � 00000 i 0.0000 ' 00000 0.0000 1 0.0000
Ventlor g.gbbo ' o.og0g ' 9.66gg ' 6.gggo ' g.og99 ' o.Bggg ' g.gggo ' g.gogg ' o.B966 6ogoo • � 6.gggo ' g.gogg ' o.oggg ' 1 g.gobo
1 i i i i i i
a
Worker 0.000D ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 ; 00000 0.0000 ' 0.000D ' 0.0000 ' I 0.0000
i
Total 0.0000 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 0.0000 ' 0.0000 ' 0.0000 0.0000 0.0000 • ' 0.0000 ' 0.0000 0.0000 ' 0.0000
4.0 Operational Detail - Mobile
4.1 Mitigation Measures Mobile
ROG NO. CO S02 Fugitive Exhaust PM10 Fugitiva Exdauat PM2ii Blo-0O2 NBio-CO2 'Tina 02 CH4 N20 G02e
PM10 PM 10 TMaI PM2.5 P12.6 TassI
cawgory IWday lblday
MNgatetl • 6.0100a- 1 0.0169 i 0.0878 1 3.5000e- i 00255 3.3000s- 0.0258 i 6.8000a- 13.1000e- ; 7.1100.- • 26.3.75 1 2fi.3675 � 8.6000e- 1 � 26.3855
1 003 004 004 003 004 003 1 004 i
......aced -_.._.-4._.0169 __.._.I-._.00.- _........_y__.._I-.002W .__..-F_.._._r-•1---_-.......{-.6,3675 -_._5 8,6.__I_.__..e......
UnmiOgetetl 6.0100e- 0.0169 0.0878 3.S000e- 00255 33000e- 0.0258 6.8000e- 3.1000e- ].1100e- 263fi]5 2fi.36]5 8.6000o- 26.3855
003 004 004 003 004 003 004
CaIEEMod Version: CalEEMod.2013.2.2 Page 15 of 18 Date: 7/16/2016 10:30 PM
4.2 Trip Summary Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMr
General Heavy Industry 2.00 2.00 2.00 12,055 12,055
Total 2.00 2.00 2.00 12,055 12,055
4.3 Trip Type Information
Mlles Trip% Trip Purpose%
Land Use H-W or C-W H-S or C-C H-O or C-NW H-W or C-W H-S or C-C I HA or C-NW I Primary I Diverted I Pass-by
General Heavy Industry 16.60 8,40 6.90 100,00 0,00 000 100 0 0
L0 LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCV SBUS MH
5043• 0,056653• 0 0.5 .194832• 0.151784• 0,042126• 0005989• 0.016072• 0.016505• 0.001461• 0.002178: 0.004464: 0.000494: 0.002401
g.g 4Fgglpypeta!I
Historical Energy Use: N
5.1 Mitigation Measures Energy
ROG NO. CO I S02 I Fugitive Exhaust PM10 Fugitive Exhaust PM2.5 Blo-CO2 NBio-CO2 TotaICO2 CH4 N20 002s
PM10 PM TOUI PM2S PM2.5 TOUI
Category Wday IWda,
NalumlGas v 0.0000 0.0000 I 0,0000 I 00000 I i 0.0000 I 0.0000 I 0.0000 0.0000 i 0.0000 0.0000 1 0.0000 1 0.0000 00000
Miligatetl
NaluralGas •• OOOOD 0.0000 0.0000 00000 0.0000 0.0000 0.0000 00000 0.0000 OOOOD O.OD00 0.0000 00000
unmiogatea
CaIEEMod Version: CalEEMod.2013.2.2 Page 16 of 18 Date: 7/16/2016 10:30 PM
5.2 Energy by Land Use - NaturalGas
Unmitigated
NaturalGa ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM2.5 Bia-002 1 NBb CO2 Total 002 1 CH6 I N20 1 CO2e
.Use PM10 PM10 Total PM2.5 PM2.5 TOWI
Land Use kBTUNr Ihlday dday
General Has 0 n 0.0000 0.0000 OOCOD 0.D000 00000 0.OD00 0.0000 0.0000 • 0.0000 0.0000 0.0000 0.0005 O.o000
Industry
i
Total • 0.0000 1 0.0000 ' 0.0000 0.0000 0.0000 O.00oo 1 0.0000 0.0000 • 0.0000 0.0000 1 0.0000 ' O.000o 0.0000
Mitigated
Natu.IGa ROG NOx 00 502 Fugftive Exhaust PM10 Fugitive Exhaust PM2.5 Bio-0O2 I NBio-0O2 TOWI CO2 I CH4 I N20 I CO2e
s Use PM10 PM10 TOWI PM2.5 PM2.5 TOWI
Land Use kBTUN'r Ib/day May
General rvea, 0 o D000 o 0000 0 DODD a DDoo ' 0 0000 ' a D000 ' o ooaa a ODoo • a ODDO 0 0000 o 0000 a DODO o D000
ToM 0.0000 ' 0.0000 1 0.0000 0.0000 ' 0.0000 1 0.0000 ' 0.0000 0.0000 O.ODDO 0.0000 ' 0.0000 1 O.00DD a.D000
6.0 Area Detail
6.1 Mitigation Measures Area
CaIEEMod Version: CaIEEMod.2013.2.2 Page 17 of 18 Date: 7/16/2016 10:30 PM
ROG NO. CO 502 Fu9i4ve Exhaust PM10 Fugitive ExOausl PM2.5 Bio-CO2 NBie-0O2 T.Wi CO2 OMN20 002e
PM10 PM10 Total PM2.5 PM2.5 Total
category IWeaY IWeay
Mitigated n 0.0297 ' 00000 1 1.5000, I 0.0000 ' 1 0.0000 ' 0.0000 I 00000 0.0000 • 133000e- 13.MON I 00000 1 ' 3.5000e-
i ON ON ' 004 I i 000
I I '
•I I I I I I i ' I I
...........
'~.-..- ..--.. .-----________ ------
Unmitigated •• 0.029] 0.0000 15000e- 0,0000 0.0000 O.000O 0.0000 0.0000 3.3000a- 3.3000e- 0.0000 3.5000e-
ON ON 004 004
6.2 Area by SubCategory
Unmitigated
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM2.5 Bio-0O2 N8io-0O2 Total CO2 CHO I N20 I CO2e
PM10 PM10 Total PM25 PM2.5 Tolal
SubCategory lWday lWday
Consumer I 0.0297 I 0.0000 0.0000 1 0.0000 0.0000 0.0000 I 0.0000
Produce
I I � I 1 I I I • ,
-a a a . a a a a
I I I '
tlsce 1.0001 0.0000 1S000e 0.0000 0.0000 0.0000 0.000 0.0000 3.3000e- 3.3000a- 0. 000I
I
3.S000e-
L e_rcn_M1_Oa_c_N_ra_ 005 00 I I I I I 00 i 0
004
-----------------------_-------_-------_-------_-------_-------_---------------------- -------i_______i
_______i --
Con 0.0000 0.0000 0.0000 0.000 0.0000 0.0� o99 o
Total 0.029T j 0.0000 j 1.5000a, 0.0000 0.0000 0.0000 0.0000 0.0000 • ' 3.301 ' 3.3000e- 0.-00 ' 3.5000e-
ON 004 ON 000
CaIEEMod Version: CalEEMod.2013.2.2 Page 18 of 18 Date: 7/16/2016 10:30 PM
6.2 Area by SubCategory
Mitigated
ROG NO. CO S02 Fugitve EMaua PM10 Fugitive Exbausl PM2.5 Blo-CO2 NBic-002 Told CO2 CMN20 1 002a
PM10 PM10 Tolal PM2.5 PM2.5 Tolal
SubCategory Ibltlay Ibltlay
Consumer I 0.0297 I 00000 I 0.0000 I 1 000oo � 0.0000 I 00000 I 1 00000
Proau dt i i I i i I
I I I I
q 1 I I I • �
I I I I I I •
• _♦ _� _� _� _� _� _i_______ _______�_______I ______ ______ _______I ______
I I I
006 0
Lantlscaping v 1.WOOe- I O.W00 1 1 S 0OOOe- i 0.0000 I I 0.0000 I 0.0000 I I 0.0000 0.0000 13.300De- i 3.3000e- I 0.0000 I 13.S000e-
005 I i 00 I i I i I ONI I I I
I •
'I I I I I I I • I I I
ArMOectu2l v 0.0000 I I I I I 0.0000 I 0.0000 I I O.ODoO � 0.0000 • I 0.0000 I I I --0.0000
coating i i i i I
I
TZI 0.0297 I 0.0000 1.5000a. I 0.0000 I 0.0000 I 0.0000 I 0.0000 0.0000 • 13.=. 13.3000e- I 0.0000 I 3.50000-
o0a ooa o0a Bna
7.0 Water Detail
7.1 Mitigation Measures Water
8.0 Waste Detail
8.1 Mitigation Measures Waste
9.0 Operational Offroad
Equipment Type Number Hours Day Days(Year Horse Power Load Factor Fuel Type
10.0 Vegetation
CaIEEMod Version: CalEEMod.2013.2.2 Page 1 of 22 Date: 7/16/2016 11:30 PM
EQ FLow Tank
Orange County, Annual
1.0 Project Characteristics
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population
General Heavy Industry 1.50 10001 0.03 1,501 0
1.2 Other Project Characteristics
Urbanization Urban Wind Speed(ni 2.2 Precipitation Freq(Days) 30
Climate Zone 8 Operational Year 2022
Utility Company Southern California Edison
CO2 Intensity 630.89 CH4 Intensity 0,029 N20 Intensity 0.00617
(IbIMWhr) (IbIMWhr) (IbIMWhr)
1.3 User Entered Comments & Non-Default Data
CalEEMod Version: CalEEMod.2013.2.2 Page 2 of 22 Date: 7/16/2016 11:30 PM
Project Characteristics- Determination of emissions for Dril Rig,Architectural Coating Emissions, and operational Activities
Land Use-
Construction Phase- Building and Tank Architectural Coating and Dril Rig Emission factor determination only
Off-road Equipment-See Assumptions
Off-road Equipment- Generator for use with sand blaster for prepping tank for coating
Trips and VMT-See Assumptions
Architectural Coating-See Assumptions
Vehicle Trips-See Assumptions
Area Coating-See Assumptions
Landscape Equipment-See Assumptions
Energy Use-See Assumptions
Water And Wastewater-See Assumptions
Solid Waste-See Assumptions
Construction Off-road Equipment Mitigation-
Off-road Equipment-
Table Name Column Name Default Value New Value
tblArchitecturalCoating Consb%rea_Nomesidential_Extenor 750.00 39,320.00
......................9------i-----------------------------}_____________________________�......... 70,72 ............
tblkchitecturalCoatin Consbkrea_Nome.idential_Imenor 2,250.00 ]0,]20.00
------------------ng--------- --------------n-----rcent-----i.______________'O ?------------ U ------.----.
Ratel
tblAreaCoati
.............................i-----------------------------}-----------------------------4..........................
tblConstructionPhase NumDdys 5.00 22.00
-----------------------------{-----------------------------
}--------------
5.__00-------------------------1--0.00------------.
tblConstructionPhase NumDaye
.............................i-----------------------------}-----------------------------4..........................
tblConstructionPhase NumDdys 2.00 1.00
-------tblConstructionPhase----------------------4-----------------------------t-----------1Y27Y2021 ----------?---------11/30/-------------
PhaseEndDatei
tblConstructionPhase -----------PhaseEndDate r ---- -- --------
r
12/2812020
-------tblConstructionPhase ------ ---------PhaseStanDate --------------------
12/292020----------?--------- 11/12021 --- - -
.............................i-----------------------------------------------------------4..........................
tblConstructionPhase PhaseStartDate 1/2/2018 1VI512020
-----------------------------4-----------------------------4------------------------------ --------------------------
tblEnergyUse NT24NG 6.86 0.00
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tblEnergyUse T24NG 14.78 0.00
................q.P......._.. ----------.........----------¢------------ ------------4..........................
t i&iRoatlE ui ment Horse Power i 205.00 500.00
..............................-----------------------------------------------------------4..........................
1b106RoadEquipmenl OflRoadEquipmentType i Bore/Drill Rigs
.............................4-----------------------------------------------------------4--------------------------
tbIOlfRoatlEquipment OflRoadEquipmenlType i Genemlor Sets
..............................-----------------------------------------------------------4..........................
1b106RoadEquipmenl OffRoadEquipmentUnitAmount i 1.00 0.00
.............................4-----------------------------------------------------------4--------------------------
tbIOlfRoatlEquipment OffRoadEquipmenlUnit ount i 1.00 0.00
..............................-----------------------------------------------------------4..........................
1b106RoadEquipmenl OffRoadEquipmentUnitAmount i 2.00 0.00
..................-----------4-----------------------------------------------------------4..........................
IblProjectOharactenstics N20intensilyFactor i 0.006 0.00617
......................-------4-----------------------------------------------------------4..........................
iblProjedCharacteristics OperetionalVear i 2014 2022
.............................i-----------------------------}_____________________________4..........................
tblsolidWaste Solid WasteGenerationRate 1 1.86 0]0
...................---------- -----------------------------------------------------------4..........................
1blTripsMdVMT WorkerTripNumber i 3.00 0.00
..................P......._..4-----------------------------}_____________________________4..........................
tblVehicleTri s CC_TTP i 28.00 0.00
.............................4-----------........----------}_____________________________4..........................
tbNehicleTrips CNW_TTP i 13.00 0.00
---------
.........P......._..4---------------_H------------------------------------------4..........................
tbNehicleTri s CW_TTP 1 59.00 100.00
...........................................................+_____________________________4..........................
1blVehicleTripa DV_TP i 5.00 0.00
..................P......._..4-----------------------------}_____________________________4..........................
tbNehicleTri s PB_TP i 3.00 0.00
.............................4................-------------------------------------------4..........................
tbNehicleTrips PR_TP i 92.00 100.00
..................P......._..i-----------------------------}_____________ _____________4..........................
tbNehi.... s ST_TR i 1.50 1.33
............................. ------------.................}_____________________________4..........................
tbNehicleTrips SU_TR i 1.50 1.33
..................P......._..4-----------------------------}_____________ _____________4..........................
tblVehicleTri s WD_TR i 1.50 1.33
------------.....------------4-----------------------------------------------------------4..........................
tblWater AerobicPeroent r 87.46 97.54
.............................%n.e bimndF--------goonsP----}________________-------------4------------..............
tblWaler •AnaerobicantlFacultativeLagoonsPercenl+ 2.21 2.46
------------.....------------4-----------------------------------------------------------4..........................
tblWater IndoorWaterUseRate i 346,875.00 260,156.00
.............................4-----------------------------4------------------------------k..........................
tblWaler SepticTankPercent 10.33 0.00
2.0 Emissions Summary
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2.1 Overall Construction
Unmitigated Construction
ROG I NO. I 00 I 502 I Fugitive Exhaun PM10 Fugitive ExM1ausl PM2.5 BIo-COF NBia-002 ToWICO2 CH4 N20 002.
PM10 PM10 Total PM2.5 PM2.5 Total
Veer bnelyi 64r/yr
2018 n 4WOO, ; 4,8000, 2 e000e- ; 0.0000 ' 00000 LOOOOe ; 1 WOO, ; 00000 1,0000, ; 1 WOO, • 00000 I 0.1214 ' 0.1214 ' 4.0000, 1 0.0000 1 0.1222
005 I 006 ON I i 005 I 005 I 005 005 ' 005 i I
•I I I I I I . I
2020 0.0186 ' 8.4200e- 1 9.1800e- 1 1.000Oe- I 0.0000 ' S.5000e- 1 5.5000e- 1 0.0000 ' S.5000e- ; 5.S000e- • 0.0000 I 1.2]88 ' 1.2786 ' 1.0000. 1 0.0000 1 1.2787
.I
I 003 I 003 I 005 I 004 I ON I 006 ON
•I I I I I I I � '
2021 0.8429 ' 0.0429 0.0504 ' 9.000Oe- I O.00DD ' 2.4200e- 1 2.4200e- 1 0.0000 ' 2.4200e- ; 2.4200e- • 0.0000 I ].4]15 ' 7.4715 ' 4.3000e- ,--0.0000 1 TABOO
I 1 I 005 I 1 003 I 003 I 003 003 i i 006 1 I
I
Tobl 0.6615 ' 0.0518 0.0598 ' 1.0No* ' 0.00D0 2.98000. ' 2.98000. ' 0.000D 2.9800. 2.98000- • 0.0000 ' 8.8696 ' 8.86% 1 5.7000. 0.0000 8.8815
004 003 003 003 003 ON
Mitigated Construction
ROG NO. CO 502 Fugitive ExM1ausl PM10 Fugitive ExM1auM PM2.5 Bio-CO2 NBia-0O2 T.WICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Vear We , MTIYr
2018 •1 4DDDDe- ' 46000e- z 8000, ' 0 0000 1 0 OODO 1 0000, ' 1 0009e- ' D OOOD 1 0000e- ; 1 0000e- • 0 0000 1 0.1214 ' 01214 ' 40000e- ' 0 0000 1 01222
:1 005 i ON ON 1 005 005 005 005 i 1 005
.._........,1------------____------- _______ -------_-------_-------_-------_----------------.......I_______._______._______.......... .......
2020 •I 0.0188 i 54200e- i 9.1600e- i 1 OODOe- 1 00000 i 5.5000e- i 5.WOOe- i 00000 i 5.5000e- ; 5.5000e- 00000 I 1.2766 i 12766 i 1.0000e- i 0.0000 1 127e7
:1 003 I 003 I 005 I ON I ON I 00 ON
I I I I I I I I 'I
.._........•' ______1_______ _______'_______x_______ -------a-------a-------a----------------... ______a_I ______x_______a_I ______r......
0.6 2021 629 ' 0.0629 ' 0.0500 ' 9.000Oe- 1 0.0000 ' 2.4200tr i 2.6200e- i 0.0000 1 24200e- ; 2.6200e- • 0.0000000 i ).4]15 i 7.6715 i 4.3000 1 0.0000 1 ]4806
005 I 1 003 I 003 I i 003 003 1 I I 0e-04 1
Tool 0.6615 1 0.0518 0.0598 ' 1.000Oo- 1 0.0000 2.9800a. ' 2.9000e. ' 0.0000 2.9800a 2.9800e. , 0.0000 8.8690 ' 8.86% 1 5.7000a 0.0000 1 8.8815
11 0" 003 003 03 003 004
CaIEEMod Version: CalEEMod.2013.2.2 Page 5 of 22 Date: 7/16/2016 11:30 PM
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive ExM1aua[ PM2.5 Bio-0O2 NBio-COY Total CO2 CH4 N20 CO2
PM10 PM10 Total PM2.5 PM" Total
P.,..m 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 1 0.00 1 0.00 0.00 0.00
Reduction
2.2 Overall Operational
Unmitigated Operational
ROG NO 00 S02 Fugitve Exhaust PM10 Fugigve Exhaust PM2.5 Bio-0O2 NBio-002 Total CO2 CH4 N20 CO2a
PM10 PM10 Total PM2.5 PM2.5 Total
Category tone, W/yr
Area n 542OOe- 1 00000 2.0000e- I 0.0000 I 00000 I 0.0000 I 0woo ; 0.0000 r 00000 14.0000e- 14.0000e- 1 0OOOO 0.0000 i 40000e-
.I 003 I 005 . 005 I 005 005
.._........a_------i______i______i______i______i______i______i______i______________ I_______._______._______._______------.
Energy 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 I 0.0000 I 3.9663 3.9863 1.8000 - 1 4.00OOo- 3.9821
.._.MOM1.e.... I 004 1 005
_ ._______ _____:_______------.
1.00 - 3.3200e 0o155 6.00O - 4.5600 - 5gaaao- 4.8200 - 1.20e- 50000e 127oge- 0.0000 I 4.2125 4.2125 1.4000 0.0000 4.2155
.I 003 003 005 003 005 003 003 1 005003
Waste ________._--- ..
i I I 0py I ii
0.0000 0.0000 OOo0 0.0000 0.1421 0.0000 0.1421 0.4000e- 1 0.0000
0.3184
Lb3 I
I I I I I I I I
.._.W.a.te.r....•�I�_______I________I________I________I________1-------_-------_--------___________ . I_______
00000 0.0000 0000 0_0000 0.0920
I 0.9894 1.0814 2.6900o- 12.1 OOOo- 1.1829
003 004
i
Total O.S000e- 13.32007 0.0165 18.0000e- 14.580oe- e.o999e- 14.0200e- 11.2200e- 9.0.0., 1.2700e- , 0.2341 9.1482 I 9.= I 0.0114 2.6000e- 9.6989
11 OOJ 003 005 003 005 OOJ 003 005 003 ON
CaIEEMod Version: CalEEMod.2013.2.2 Page 6 of 22 Date: 7/16/2016 11:30 PM
2.2 Overall Operational
Mitigated Operational
ROG I Nor I CO I 502 I Fugitve Exhaun PM10 Fugitive Exhaust PM2.5 BIo-COF Mrry
NBio-002 ToWICO2 CMN20 002.
PM10 PM10 Total PM2.5 PM2.5 Total
cereeory loearyT r
Area n 542o0e- 1 00000 20000e- 1 0.0000 I 00000 I 0.0000 I 00000 0.0000 • 00000 140000e. 1 4.0000e- l 00000 0.0000 14.000Oe-
.I
003 I 005 I i i i I 005 I 005 I 1 005
•I I I I I I I
__ •I ---------------�--------
I I
En_ergy 0.0000 I o.W00 10.0000 10.0000 I 10.0000 10.0000 I 10.0000 0.0000 • 0.0000 13.9883 13.9883 I1.8000e- 14.00 1 3.9821
[u 0 I 0055 I
•I I I I I I I Moblle _
I
I
-------i------- ------- ------- ------- ------- __ ____ _______-________ -------- ______a-------a_I
______i_______r______
1.OBOOe- i 3.3200e- i 0.0155 i 6.WOOo- i 4.SBOOe- i B.000Oa i 4.8200e- i 1.2200e- i 3.000Oe- 1 1.270Oe- • 0.0000 I 4.2125 i 4.2125 i 1.4000e- i 0.0000 I 4.2155
.I
003 I o03 I I 005 I 003 1 WS I 003 I 003 1 005 --- I I I ON_______ __ I 1
•I I I I I I I •
___________•I _ __�_______
Waste I I I I I 0.0000 I 0.0000 I I 0.0000 1 O.00oO • 0.1421 I 0.0000 I 0.1421 184000e- I 0.0000 1 03184
.I
003 1 I
•I I I I I I I
___________•I _______i_______ _______ _______i_______ _______ _______i_______________ _______
Water I I I 0.0000 I 0.0000 I 0.0000 1 OoOoO • 0.0920 I 0.9694 I 1.0614 12.6900e- 2.10OW- 1 1.1827
i i i i i i 003 1 004 I
Total 6.5 0 e- 13.3200e- 0.0155 16.0000e-005 14.5600e-003 6.000U005e- 14.6200e-003 11.2200003e- 6.000005 50, 1.2 0]03 00 004.- • 0.2341 I 9.14 S000e 82 I 9.3823 I 0.0114 2. - 9.6988
000 03 003
ROG NOx CO S02 FugHlve ExM1aust PM1Y Fugltive Exhaust PM25 810-L03 NBIo-L02 Total CO2 LH4 N30 L03e
PM10 PM10 Total PM2.5 PM2.5 Total
Percent 000 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 1 0.00 0.00 0.00 0.00 0.00 0.00
Reduction
3.0 Construction Detail
Construction Phase
Phase Phase Name Phase Type Stall Dale End Date Num Days Num Days Phase Description
Number I Week
1 •Dnll Rig Emissions Estimate 1Graning 11/1/2018 11/1/2018 51 11
I
.._....:..............9_........;.........Coating ......1____________a____________ _____; ..............
2 •Amhit-----Coatin for-- IArchi------Coatin 172I15/2020 172I28/2020 51 101
.._....:. .............or Tank ..1..........._..........1-'-2021 1_--"'-_�_______�__-___�-------------------------
:Architectural
3 Coating For Tank •Architectural Coating •11/1/2021 •11/302021 5 22•
CalEEMod Version: CalEEMod.2013.2.2 Page 7 of 22 Date: 7/16/2016 11:30 PM
Acres of Grading (Site Preparation Phase): 0
Acres of Grading(Grading Phase): 0
Acres of Paving: 0
Residential Indoor: 0; Residential Outdoor: 0; Non-Residential Indoor: 70,720; Non-Residential Outdoor: 39,320(Architectural Coating—sgft)
OffRoad Eauioment
Phase Name Jffj Of roatl Equipment Type Amount Usage Hours Horse Power Load Factor
Architectural Coating For Tank )Air Compressors 11 6.001 78' 0.48
Drill Rig Emissions Estimate (Bore/Drill Rigs 1 1.00l 500• 0.50
Architectural Coating For Tank )Generator Sets 11 B.00i 84' 0]4
Drill Rig Emissions Estimate (Concrete.... .. Saws 01 8.001 81• 0.73
Architectural Coating for Ps )Air Compressors 1! 6.00 78' 0.48
....... ..................................... ______..__.._..{_.__________._____________ ...._.........
Drill Rig Emissions Estimate (Rubber Tired 0� 1.00- 25S 0.40
t ----- r
Drill Rig Emissions Estimate •TractorslLoatlerslBackhoes 0: 8.00• 97• 0.37
Trios and VMT
Phase Name Offroad Equipment I Worker Trip Ventlor Trip Hauling Trip Worker Trip Ventlor Trip Hauling Trip Worker Vehicle Vendor Hauling
Count Number Number Number LengM Length Length Class VehiGe Class Vehicle Class
Architectural Coaling ) 1; 0.00• 0.00i 0,00: 14.70' 6.90; 20.00;LD_Mix iHDT_Mix ;HHDT
t___ 1_______
Drill Rig Emissions ) 1; 0.00• 0.001 0.001 14.70' 6.90; 20.00:LD_Mix iHDT—Mix JHHDT
&....
Architectural Coaling ; 2• 0.00' 0.00' 0.00' 14.70' 6.90' 20.00'LD_Mix •HDT_Mix •HHDT
3.1 Mitigation Measures Construction
Clean Paved Roads
CaIEEMod Version: CalEEMod.2013.2.2 Page 8 of 22 Date: 7/16/2016 11:30 PM
3.2 Drill Rig Emissions Estimate - 2018
Unmitigated Construction On-Site
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM2.5 Blo-CO2 NBio-CO2 TOISICO2 CM N20 I CO2e
PM10 PM10 Total Phi PM2.5 TWaI
Category WOW, MT/p
Fugitive Oust i I 1 00000 0.0000 I Omoo 1 00000 0.0000 ; 00000 0.0000 I Omoo 1 00000 1 00000 I 0.0000 1 00000
•I I I •
Ott •
-Rod • I 4800 1I 2. OII 00000 I I I I •�_______ •• I__ _ _ _ _ __ _I _
4.0000e- i W e OO _
0.1214 I 0.1214 14.000Oe- I 0.0000 i 0.1222
005 i 004 I 004 I I i 005 I 005 I i 005 005 i i 005 I I
I
Total 4.00000- 4.8000e- 12.B000e. I 0.0000 I 0.0000 11.=. 11.00000- I 0.0000 1.0000s. 1.0000e. • 0.0000 I 0.1214 I 0.1214 4.0000a. I 0.0000 0.1222
11 005 ON ON 005 005 005 005 005
Unmitigated Construction Off-Site
ROG NO CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM25 Blo-CO2 NBio-CO2 TOtaICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category toresyr Mrly
Heulilg •I 0.0000 0.0000 I 0.0000 I 0.0000 I 0.0000 0.0000 I 0.0000 I 0.0000 0.0000 ; 0.0000 • 0.0000 I 0.0000 I 0.0000 OD000 I 0.0000 I 0.0000
•I I I I I I I I • I
•I I I I I I I veeaod•I aI aI aI aI aI aI a
i
gBao 0000 000g oggo aoo 0000 ooga . __o_____ I
r go 0000 ggo 0.0000 0.0000 g.gaoo 0.000 1
0.0000 i o.gaao
I
•I I I I I I I I ; i I i
-----------•I _-------_-------_-------_-------_-------_-------_-------_--------------- _____I
Worker 0.0000 i 0.0000 j 0.0000 j 0.0000 j 0.0000 j 0.0000 j 0.0000 j 0.0000 j 0.0000 ; 0.0000 • 0.0000 I 0.0000 j 0.0000 i 0.0000 j 0.0000 i 0.0000
I i i i i i I i I
Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 I 0.0000 0.0000 0.0000 0.0000 I 0.0000
CaIEEMod Version: CalEEMod.2013.2.2 Page 9 of 22 Date: 7/16/2016 11:30 PM
3.2 Drill Rig Emissions Estimate - 2018
Mitigated Construction On-Site
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM2.5 Blo-CO2 NBio-CO2 TOISICO2 CM N20 I CO2e
PM10 PM10 Total Phi PM2.5 TWaI
Category WOW, MT/p
Fugitive Oust i I 1 00000 0.0000 I Omoo 1 00000 0.0000 ; 00000 • 0.0000 I Omoo 1 00000 1 00000 I 0.0000 1 00000
•I I I •
Ott •
-Rod • I 4800 1I 2. OII 00000 I I I I •�_______ •• I__ _ _ _ _ __ _I _
4.0000e- i W 0 O _
0.1214 I 0.1214 14.000Oe- I 0.0000 i 0.1222
005 i 004 I 004 I I i 005 I 005 I i 005 005 i i 005 I I
I
Total 4.00000- 4.8000e- 12.B000e. I 0.0000 I 0.0000 11.=. 11.00000- I 0.0000 1.0000s. 1.0000e. • 0.0000 I 0.1214 I 0.1214 4.0000a. I 0.0000 0.1222
11 0a5 ON ON 005 005 005 005 005
Mitigated Construction Off-Site
ROG NO CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM25 Blo-CO2 NBio-CO2 TOtaICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category tonsi Mrly
Heulilg •I 0.0000 0.0000 I 0.0000 I 0.0000 I 0.0000 0.0000 I 0.0000 I 0.0000 0.0000 ; 0.0000 • 0.0000 I 0.0000 I 0.0000 OD000 I 0.0000 I 0.0000
•I I I I I I I I • I
•I I I I I I I veeaod•I aI aI aI aI aI aI a
i
gBao 0000 000g oggo aoo 0000 ooga . __o_____ I
r go 0000 ggo 0.0000 0.0000 g.gaoo 0.000 1
0.0000 i o.gaao
I
•I I I I I I I I ; i I i
-----------•I _-------_-------_-------_-------_-------_-------_-------_--------------- _____I
Worker 0.0000 i 0.0000 j 0.0000 j 0.0000 j 0.0000 j 0.0000 j 0.0000 j 0.0000 j 0.0000 ; 0.0000 • 0.0000 I 0.0000 j 0.0000 i 0.0000 j 0.0000 i 0.0000
I i i i i i I i I
Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 I 0.0000 0.0M 0.0000 0.0000 I 0.0000
CaIEEMod Version: CalEEMod.2013.2.2 Page 10 of 22 Date: 7/16/2016 11:30 PM
3.3 Architectural Coating for PS - 2020
Unmitigated Construction On-Site
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM2.5 Blo-CO2 NBio-CO2 TeISICO2 CM N20 I CO2e
PM10 PM10 Total Phi PM2.5 Total
Category Who, MT/p
A¢hit.Coating �I 00174 I I 0.0000 I 0.0000 I 0.0000 ; 00000 0.0000 I 0.0000 1 00000 00000 I 0.0000 1 00000
•I I I I I I I I I I I
---
__ _ _______ _______ _______ _______ _______ _______ _______ _______-___ ---
•I
Ott-Road 1.2100e- 10.4200e- 19.i800e- 11.000Oe- I 15.5000e- 15.SWOe- 155000e- ; 5.S000e- 0.0000 I 1.2706 I 1.2766 11.0000e- I 0.0000 i 1987
003 003 I 003 I 005 I i 004 I 000 I i 004 000 � i 004 I I
I
Total 0.0106 SA200a I metes,- 11.000Oe- I S.S000e- 15.5000e- I 5.5000e- 5.5000e- • 0.0000 I 1.2780 I 1.3700 1.0000a. I 0.0000 1.2787
11 009 003 005 004 006 ON004 004
Unmitigated Construction Off-Site
ROG NO CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM25 Bo-CO2 NBio-CO2 TotaICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category tons/Yr Mrly
Heulilg •I 0.0000 0.0000 I 0.0000 I 0.0000 I 0.0000 0.0000 I 0.0000 I 0.0000 0.0000 ; 0.0000 • 0.0000 I 0.0000 I 0.0000 oD000 I 0.0000 I 0.0000
•I I I I I I I I • I
•I I I I I I I veeaod•I aI aI aI aI aI aI a
i
BBao 0000 000g oBBo aoo 0000 ooga . __o_____ I
r go 0000 BBo 0.0000 0.0000 B.gaoo 0.000 1
0.0000 1 o.Baao
I
•I I I I I I I I ; i I i
-----------•I _-------_-------_-------_-------_-------_-------_-------_--------------- _____I
Worker 0.0000 i 0.0000 j 0.0000 j 0.0000 j 0.0000 j 0.0000 j 0.0000 j 0.0000 j 0.0000 ; 0.0000 • 0.0000 I 0.0000 j 0.0000 i o.0000 j 0.0000 0.0000
I i i i i i I i I
Total 0.0000 0.000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 I 0.0000 0.0000 0.000 0.0000 I 0.0000
CaIEEMod Version: CalEEMod.2013.2.2 Page 11 of 22 Date: 7/16/2016 11:30 PM
3.3 Architectural Coating for PS -2020
Mitigated Construction On-Site
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM2.5 Blo-CO2 NBio-CO2 TOISICO2 CM N20 I CO2e
PM10 PM10 Total Phi PM2.5 Total
Category Who, MT/p
A¢hit.Coating �I 00174 I I 0.0000 I 0.0000 I 0.0000 ; 00000 • 0.0000 I 0.0000 1 00000 00000 I 0.0000 1 00000
-I I I I I I I I I I I
---
__ _ _______ _______ _______ _______ _______ _______ _______ ___________ ---
•I
Ott-Road 1.2100e- 10.4200e- 19.i800e- 11.000Oe- I 15.500oe- 15.SWOe- 155000e- ; 5.S000e- • 0.0000 I 1.2706 I 1.2766 11.0000e- I 0.0000 i 1987
003 i 003 I 003 I 005 I i 004 I 000 I i 004 000 i i 004 I I
I
Total 0.0106 SA200a I mattes. 11.000Oe- I S.S000e- 15.5000e- I 5.5000e- 5.5000e- • 0.0000 I 1.2785 I 1.3708 1.000Ue- I 0.0000 1.2787
11 009 003 005 004 006 ON 004 004
Mitigated Construction Off-Site
ROG NO CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM25 Bo-CO2 NBio-CO2 TotaICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category tons/Yr Mrly
Heulilg •I 0.0000 0.0000 I 0.0000 I 0.0000 I 0.0000 0.0000 I 0.0000 I 0.0000 0.0000 ; 0.0000 • 0.0000 I 0.0000 I 0.0000 ODo00 I 0.0000 I 0.0000
•I I I I I I I I • I
•I I I I I I I vendod•I I I I I I I a
i
j 0000 00O 0.0000 0.0000 O.O000 0.000 1
0.0000 O.O000 a a a a a _ O _ I
r 0.0000 0.000 O.000O O00O O.W00 o.000O O.000O OOWO
I
•I I I I I I I I : ; i I i
----------- _-------_-------_-------_-------_-------_-------_-------_--------------- _____I
Worker •I 0.0000 i 0.000 j 0.0000 j 0.0000 j O.W00 j 0.0000 j 0.0000 j O.OWO j 0.0000 ; O.000O • 0.0000 I 0.0000 j 0.000o i O.0000 j 0.0000 i 0.0000
I i i i i i I i I
Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 I 0.0000 0.0m 0.0000 0.0000 I 0.00W
CaIEEMod Version: CalEEMod.2013.2.2 Page 12 of 22 Date: 7/16/2016 11:30 PM
3.4 Architectural Coating For Tank-2021
Unmitigated Construction On-Site
ROG NOx CO S02 Fugitive Exhaust Polo Fugitive Exhaust PM2.5 Blo-CO2 NBio-CO2 TeISICO2 CM N20 I CO2e
PM10 PM10 Total Phi PM2.5 Total
Category tonal, MT/p
A¢ht Coating ,�II 06375 I 1I 'i i i 0.0000 i 0000i 0.0000 00000
0.0000
I 0000i 00wit 00000 i 0.0000 i
00000
___O_tt _
-Ro_ad _ -------_-------_-------_____________--- -------
I.I 5.3600e- O.W2_ 0.0504 9.00Oe- 2.420 2.42We- 2420 2.4200e- 0.0000 ].4715 I 7.4715 4.3000e- I 0.0000 i 7,4806
003 005 I i 003 I 003 I i 003 003 � i 004 I I
I
Total 0.11WI29 0.W29 I 0.0504 19.0000e- I 12.=. 12.4200e- I 2.4200e- 2.4200e- • 0.0000 I 7A715 I 7.4715 4.3000a. I 0.0000 7."06
11 005 009 003 003 003 004
Unmitigated Construction Off-Site
ROG NO CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM25 Bo-CO2 NBio-CO2 TotaICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category tons Whir
Heulilg •I 0.0000 0.0000 I 0.0000 I 0.0000 I 0.O000 0.0000 I 0.0000 I 0.0000 0.0000 ; 0.0000 • 0.0000 I 0.0000 I 0.0000 o0000 I 0.0000 I 0.0000
•I I I I I I I I • I
•I I I I I I I venaod•I aI aI aI aI aI aI a
i
96ao 0000 0009 o96o aoo 0000 oo9a . __o_____ I
r go 0000 990 0.0000 0.0900 9.0aoo 0.000 1
0.0090 1 0.9aao
I
•I I I I I I I I ; i I i
----
------- I ___________________________________________________________________________ _____I
a____ I______________________________________
Worker 0.0000 i 0.0000 j 0.0000 j 0.0000 j O.WOo j 0.0000 j 0.0000 j O.OWO j 0.0000 ; 0.0000 • 0.0000 I 0.0000 j 0.000o i o.0000 j 0.0000 0.0000
I i i i i i I i I
Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 I 0.0000 0.0m 0.0000 0.0000 I 0.00M
CaIEEMod Version: CalEEMod.2013.2.2 Page 13 of 22 Date: 7/16/2016 11:30 PM
3.4 Architectural Coating For Tank-2021
Mitigated Construction On-Site
ROG NOx CO 502 Fugitive Exhaust Polo Fugitive Exhaust PM2.5 Blo-CO2 NBio-CO2 TeISICO2 01-14 N20 I CO2e
PM10 PM10 Total Phi PM2.5 Total
Category tonal, MT/p
A¢ht Coating ,�II 06375 I 1I 'i i i 0.0000 i 0000i 0.0000 00000
0.0000
I 0000i 00wit 00000 i 0.0000 i
00000
___O_tt _
-Ro_ad _ -------_-------_-------_____________--- _______.I 5.3600e- O.OB_ 0.0504 9.00Oe- 2.420 2.4200e- 2420 2.4200e- 0.0000 I ].4715 I 7.4]15 4.3000e- I 0.0000 I 7,4806
003 I I I 005 I i 003 I 003 I i 003 003 I i 004 I I
I
Total 0.6429 O.W29 I 0.0504 19.0000e- I 12.42 . 12.4200e- I 2.4200e- 2.4200e- • 0.0000 I 7A715 I 7.4715 4.3000a. I 0.0000 7."06
11 005 009 003 003 003 004
Mitigated Construction Off-Site
ROG NO CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM25 Bo-CO2 NBio-CO2 TotaICO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
Category tons Whir
Heulilg •I 0.0000 0.0000 I 0.0000 I 0.0000 I 0.000o 0.0000 I 0.0000 I 0.0000 0.0000 ; 0.0000 • 0.0000 I 0.0000 I 0.0000 00000 I 0.0000 I 0.0000
•I I I I I I I---venao- •d••III I aIII aIII aIII aII I aII I aII I a
o �_______ •i; I
r 9.6aao o.000 0.0099 0.96o a.0000 0.0009 0.0900 9.goo .0000 0.990 0.0000 III
0.0900 Ii 9.gaooI 0.000 1i 0.0090 I o.9aao
Wo-ke -------_-------_-------_-------_-------_-------_-------_-------_--------------- _____
r- I 0.0000 j 0.0000 I 0.0000 I 0.0000 I O.WOo I 0.0000 I 0.0000 I O.OWO j 0.0000 ; 0.0000 • 0.0000 I 0.0000 I 0.000o i 0.0000 I 0.0000 I 0.0000
i i i i i I i I
Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 I 0.0000 0.0m 0.0000 0.0000 I 0.00m
4.0 Operational Detail - Mobile
CalEEMod Version: CalEEMod.2013.2.2 Page 14 of 22 Date: 7/16/2016 11:30 PM
4.1 Mitigation Measures Mobile
ROG NOx CO 502 Fugitive ExM1aust PM10 Fugitve ExM1auR PM2.5 Blo-CO2 NBio-CO2 T.tal CO2 CM N20 CO2s
PM10 PM10 Total PM2.5 PM2.5 TWaI
Category mnsryr W/yr
Miligatetl v 10B00e- 3.3200e- I 0,0155 60000s- 14.5600e- 80000s- i 46200e- 112200s- 80000e- 12700e- • 0.0000 i 4.2125 42125 1 14000, I 0.0000 1 42155
•. 003 003 i 005 003 1 005 003 003 005 003 i i 004 i
i I
Unmltlgaled •• 1.0800e- 3.3200e- 0.0155 6.0000e- 4.5600e- 6.0000e- 4.6200e- 1.2200e- BOOOOe- 1.2700e- 0.0000 4.2125 4.2125 14000e- 0.0000 4.2155
003 003 005 003 005 003 003 005 003 004
4.2 Trip Summary Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
General Heavy Industry 2,00 2.00 2.00 12,055 12,055
Total 2,00 2.00 2.00 12,055 12,055
4.3 Trip Type Information
Miles Trip% Trip Purpose%
Land Use H-Wor C-W H-S or C-C IH-Oor C-NW H-W or C-W H-S or C-C I H-O or C-NW Pool Diverted Pass-by
General Heavy Industry 1660 8,40 6.90 100,00 0,00 0,00 100 0 0
L50 0,056653•LDTi LDT2 MDV LHD7 LHD2 MHD HHD OBUS UBUS MCV SBUS MH
0. 05043• 0.194832• 0.151784• 0,042126• 0005989• 0.016072• 0.016505• 0.001461• 0.002178: 0.004464: 0.000494: 0.002401
§.Q AV7fr&y,Detail
Historical Energy Use: N
CalEEMod Version: CalEEMod.2013.2.2 Page 15 of 22 Date: 7/16/2016 11:30 PM
5.1 Mitigation Measures Energy
ROG NO CO S02 Fugitive I Exhaust P1,110 Fugitive Exhaust PM2.5 Bo-CO2 NBio-CO2 To•sICO2 CH4 N20 CO2a
PM10 P1.110 Total PM2.5 PM2.5 Total
Category tonelyr W/yr
Eledncily ' ' ' 0.0000 ' 0.0000 ' 0.0000 ; 0.0000 • 0.0000 i 3.9663 ' 3.9663 1.8000tr 14.0000e. 1 3.9821
Mitigated Mt i i i i i ' i Mt i 005
__________-____ ---
0 O.00Iq 0.0000 3.8663 3.9663 1.8000e- 4.00o0e- '
3.8821
uElenaatoa oo- oos
_____ _ ______1 _____ _____ '
NawalGas 00000 0.0000 ' o.0000 ' 00000 ' ' o.0000 ' o.0000 ' ' o.0000 o.0000 o0000 � o.0000 ' 00000 ' o.0000 ' 0.0000 00000
MNgatetl :' i i i ' i i
NalualGas •• 0.000D 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 O1 0.0000 0.0000 0.0000
unmitigated
5.2 Energy by Land Use - NaturalGas
Unmitigated
NaturalGa ROG NOx CO S02 Fugave Exhaust PM10 Fugitive Exhaust PM2.5 Bio-0O2 NBio-0O2 Total 002 CH4 N20 CO2e
s Use PM10 Palo Total PM2.5 PM2.5 Tatel
Land Use FBTUlyr tonalyr MTlyr
Geneal Heavy 0 n 0.0000 0.0000 11 0.0000 00000 0.0000 0.0000 ; 0.0000 • 0.0000 0.0000 0.0000 0.0000 ti 0.0000
Intlusby
Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 • 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
CaIEEMod Version: CalEEMod.2013.2.2 Page 16 of 22 Date: 7/16/2016 11:30 PM
5.2 Energy by Land Use - NaturalGas
Miticated
Netu.IGa ROG NOx CO S02 Fughive Exhaust PM10 Fugifve Exhaust PM2.5 Bio-0O2 I NBIo-0O2 Total CO2 CHd N20 CO2e
s Use PM10 PM10 Total PM2.5 PM2.5 Total
Lane uae karuNr mnayr MrNr
General Has o n 0.0000 ; 0.0000 ; 00000 i 0.0000 1 ; 00000 l 00000 ; 0.0000 o0000 o.0000 773 i 0.0oun ; 0.0000 ' 00000 0.0000
Industry i
l
Total • 0.0000 ' 0.0000 ' 0.0000 0.0000 ' 0.0000 0.0000 ' 0.0000 0.0000 • 0.0000 0.0000 0.0000 ' 0.0000 ' 0.0000 0.0000
5.3 Energy by Land Use - Electricity
Unmitigated
qkWh/y,
TotaICO2 CHd N20 CO2e
Land Use MTNr
General Has 13860 n 3.9663 1.8000e- 4.0000e- 3.9821
Indust, l 006 005 l
Total 3.9663 1 1.8000e- ' 4.0000e- 3.9821
004 OOs
CaIEEMod Version: CalEEMod.2013.2.2 Page 17 of 22 Date: 7/16/2016 11:30 PM
5.3 Energy by Land Use - Electricity
Mitlaated
Electncky Totel 002 CH4 N20 CO2e
uae
Land Uee kWMyr MTNr
Geneml Heavy 13860 n 3.9663 l 1 8000e- l 4.0000e- i 3.9821
ln&g, 0" 005
I
Total • 3.9663 ' MOW- 4.0000e- 3.9821
11 904 66s
6.0 Area Detail
6.1 Mitigation Measures Area
ROG NO. I CO 502 FugiW. Exhaust PM10 Fugitive Exhaust PM2.5 BIo-CO2 NBic-0O2 T.WCO2 CMN20 002e
PM10 PM10 Tolal PM25 PM2.5 TM2
Category tonWW W),
Mlligate 5.420oe- j 0.0000 j 20000� j 0.0000 l 0.0000 l 0.0000 l j 0.0000 0.0000 • 0.0000 4.0000e- j 4.000W l 0.0000 j 0.0000 4.WOOe-
•� 003 005 005 005 i 005
UnmiBgetetl •• 5.4200e- 0.W00 20000e- 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 4.0OWe- 4.000Oe- 0.0000 0.0000 4.0000e-
003 005 005 005 005
CaIEEMod Version: CalEEMod.2013.2.2 Page 18 of 22 Date: 7/16/2016 11:30 PM
6.2 Area by SubCategory
Unmitigated
ROG NO. 00 S02 Fugitive Exhaua PM- Fugitive Exhaust PM2.5 BIo-COF NBia-G02 T.WICO2 CMN20 002.
PM10 PM10 Total PM2.5 PM2.5 Total
subcategory tonw/ Mrlyr
nmhnecmai •, o.0000 ; 00000 ' o.0000 ' 0woo 0.00e0 0.0000 , 0.0000 ' 00000 ' 000oo 0.0000 00000
Coating •' ' ' ' ' ' ,
__ •' -------___.00----- __ 000_____ '
Consumer 5.42 ; ' ' ' ' 0.0000 ' 000 ' ' 0.0000 ; 000 • 0.0000 , 0.0000 ' 0.0 ' O.OD00 ' 0.0000 i 0.0000
Protlucls •' 003 0.0
I i
___________•' -------_------- _______
0.0 '
Lantluaping 000 ' O.MO ' 2000e-0 I 0.0000 ' ' 0.0000 ' 0.0000 ' ' O.OD00 ; 0.0000 • 0.0000 14.0000e- 14.0000e- ; O.OD00 ' 0.0000 i 4.ODOOe-
I 005 I I i i 005 I 005 I , 005
I
Total 5.d200e- 1 0.0000 2.0000a- ' 0.0000 ' 0.0000 ' 0.0000 ' 0.0000 0.0000 • 0.0000 ' d.0000e- 4.0000e- 0.0000 0.0000 d.0000e-
003 005 005 005 003
Mitiaated
ROG NOx CO S02 Fugitive Exhaust PM10 Fugitive Exhaust PM2.5 E
NBia-0O2 Tofal CO2 CH4 N20 CO2e
PM10 PM10 Total PM2.5 PM2.5 Total
SubCategory Wn , MTlyr
Conaurtrer •, 5.4200e- ' ' 0 0000 ' 0 0000 ' a 0000 0 0000 0 0000 ; 0 000D ' a 0000 0 0000 1 0 0000
Pmtluuls •� 003 I ' ' ' ' '
.._........,I_______ _______________ I_______._______._______._______------.
Lantlacaping , 0.0000 0.0000 2000Oo- 0.0000 f 0.0000 0.0000 f 0.0000 0.0000 00000 , 4Oee0e- , 4.0000e- 0.0000 0.0000 aOooOe-
I I 005 I I I I I I ; ' 005 , 005 I I i 005
'
.._........,I_______ I_______i_______ _______a_______ .00000
Nd tingal •, 0.0000 i i 00000 0.0000 ' 0.0000 0.0000 00000 , 00000 , 00000 0.0000 0.0000 i 00000
Coating q
Total 5.4200e- 1 0.0000 2.0000e- ' 0.0000 1 O.D000 ' 0.0000 ' 0.0000 0.0000 , 0.0000 4.0000e- 1 4.DODDe- 1 0.0000 0.0000 1 e.D000e-
11
003 005 005 005 005
7.0 Water Detail
CaIEEMod Version: CaIEEMod.2013.2.2 Page 19 of 22 Date: 7/16/2016 11:30 PM
7.1 Mitigation Measures Water
Total CO2 CM I N20 I CO2e
Category MT/yr
Mitigated i 1.0614 j 2.6900a- j 2.1000, I 1.1827
003 004 i
UnmiOgatetl 1.0614 2.6900e- 2.1000e- 1.1829
003 000
7.2 Water by Land Use
Unmitigated
In]Mgal
Talel CO2 CH4 N20 CO2e
dU.
Land Use MT/yr
General Heavy 1)2601661•1 1M4 I26900e- I21000e- ' 11829
Industry 0 003 004 '
i
Total 1.0514 , 2.6900e- 2.1000e- 1.1329
003 004
CaIEEMod Version: CalEEMod.2013.2.2 Page 20 of 22 Date: 7/16/2016 11:30 PM
7.2 Water by Land Use
Mitigated
Ind.tsi T.WICO2 CH4 N20 CO2e
door Use
Land Use I Mgal MTNr
General Heavy 1)2601561•1 1D614 126900e- ; 2 1000e- 1 11827
mdastry 0 003 004
i
Total 1.0614 12.691 12.1000e- I 1.1827
003 004
8.0 Waste Detail
8.1 Mitigation Measures Waste
Category/Year
Thal Cot I CH4 N20 COL
Ttyr
-:J
Mitigated 0.1421 840001 0.0000 1 0.3184
003
--------
Unmitigated •• 0.1421 840001 0.0000 0.3184
003
CaIEEMod Version: CalEEMod.2013.2.2 Page 21 of 22 Date: 7/16/2016 11:30 PM
8.2 Waste by Land Use
Unmitigated
West. Tote)CO2 CH4 N20 CO2e
Disposed
Land Use tans MTlyr
Genersl Heary 07 v 01421 18E000e- I 0.0000 0.3184
Industry 003
i
Total • 0.1421 8.4000e- ' 0.0000 0.3184
003
Mitigated
Waste TaMI CO2 CH4 N20 CO2e
Disposed
Land Use we Mi
Generel Heavy 0.7 n 0.1421 8.4000e- 0.0000 I 0.3184
Industry 003
I
Total 0.1421 8.4000.- 1 0.0000 0.3184
003
9.0 Operational Offroad
Equipment Type Number HouWDay DaysNear Horse Power Load Factor Fuel Type
CaIEEMod Version: CaIEEMod.2013.2.2 Page 22 of 22 Date: 7/16/2016 11:30 PM
10.0 Vegetation
Appendix B
Biological Assessment
Orange County Water District
Water Production Enhancement
Project
Biological Assessment
Prepared By
Orange County Water District
18700 Ward Street
Fountain Valley, CA 92708
Contact: Daniel Bott U
S INCE 1933
August2016
Table of Contents
Section Page
SECTION 1.0 INTRODUCTION................................................................................... ill
SECTION 2.0 REGULATORY FRAMEWORK.............................................................211
2.1 Federal Regulations........................................................................................211
2.2 State Regulations............................................................................................2[2
SECTION 3.0 PROEECT DESCRIPTION ....................................................................3E1
3.1 Study Area ......................................................................................................3E1
3.2 Proposed Project Actidties..............................................................................311
3.3 Proposed Project.............................................................................................3E1
SECTION 4.0 BIOLOGICAL RESOURCES.................................................................411
4.1 Biological Resource Setting ............................................................................411
4.2 Special Status Plant Species ..........................................................................411
4.3 Special Status Wildlife Species.......................................................................4E3
4.4 Critical Habitat.................................................................................................4E5
4.5 Federal and State ELrisdictional Aoaatic Resources.......................................4E5
SECTION 5.0 PROEECT IMPACTS.............................................................................511
5.1 Threshold of Significance................................................................................511
5.2 Project Impacts ...............................................................................................5E1
SECTION 6.0 REFERENCES......................................................................................611
Tables
Table 1: SensitiEB Plant List.........................................................................................4[2
Table 2: Special Status Wildlife....................................................................................4A
Figures
Figure 1: Regional Location Map .................................................................................3EP
Figure 2: OCSD Plant 2 Wastewater Treatment Site ...................................................33
Appendices
Appendix A: United States Fish and Wildlife Information, Planning and ConserEbtion
System Database Search
Orange County Water District Water Production Enhancement Project i
Section 1
Introduction
SECTION 1.0 INTRODUCTION
Purpose
The Orange County Water District EOCWDdocated at 18700 Ward Street, Fountain
Valley, California, 92708 is proposing Water Production Enhancement Project. The
Biological Assessment eEbluates potential impacts to biological resources associated
with implementation of Water Production Enhancement Project. The biological
assessment was prepared by the OCWD Natural Resource Department in the spring of
2016. The assessment identifies applicable laws and regulations that apply to biological
resources within the project area, documents existing biological resources and the
potential for sensitiEL species to occur within the project area, eEsluates potential
project impacts and where reELired identifies mitigation measures to aEbid and
minimiLb potential impacts to sensitiCb biological resources.
Methodology
Literature Review
A literature search and resew was conducted in conjunction with biological surEbys to
document the presence and potential for biological resources to exist within the project
area. To identify the potential for special status species to occur within the project area,
database searches were conducted with the use of United States Fish and Wildlife
EUSFWS Ell nformation, Planning, and ConserEation System Database and the California
Department of Fish and Wildlife [CDFWONatural DiEbrsity Database.
Onsite Field Survey
A Field surCby was conducted by Dadd McMichael, OCWD biologist, in spring of 2014
to determine if sensitilb Cegetation communities, special status plant species and
special status wildlife species were present and if the project area contained suitable
habitat conditions to support special status plant species and special wildlife species.
The surlby was conducted by walking areas of the project area utilidng recognllbd
techninies. Based on the results of the surE,ey, sensitiEb Ebgetation communities,
special status plants and special status wildlife species were determined to ha-a either
a low, moderate or high potential to occur within the project area.
Orange County Water District Water Production Enhancement Project 1-1
Section 2
Regulatory Framework
SECTION 2.0 REGULATORY FRAMEWORK
The following federal, state and regional regulatory programs are applicable to the
GWRS Final Expansion Project.
2.1 Federal Regulations
Federal Clean Water Act
The Clean Water Act is intended to restore and maintain the Duality and biological
integrity of Waters of the United States [U.S.[]According to Section 404 of the Clean
Water Act, any actidty that inml[es the discharge of dredged or fill material into Waters
of the U.S. is subject to approlial of a 404 Permit from the U.S. Army Corps of
Engineers [Corpsli Depending on the le[IDI of impacts occurring, an actidty affecting
waters of the U.S. could OJalify for a Nationwide Permit or reOJires appro[13I of an
Indiddual404 Permit.
Section 401 of the Clean Water Act re0uires that an applicant for a federal license or
permit to discharge into nadgable waters must pro[ide the federal agency with a water
iluality certification, declaring that the discharge would comply with water olality
standards reDtirements of the Clean Water Act. The issuance of a 404 permit triggers
the reDiirement that a Section 401 Water Quality Certification must also be obtained
from the Regional Water Quality Control Board IRWQCB[i
Federal Endangered Species Act
The Federal Endangered Species Act IFESADdesignates threatened and endangered
animals and plants and proddes measures for their protection and reco[Bry. The Take
of listed animal and plant species in areas under the federal jurisdiction is prohibited
without obtaining a federal permit. A Take is defined as to harass, harm, pursue, hunt,
shot, wound, kill, trap, capture or collect or attempt to engage in any such conduct.
Harm includes any act which kills or injures fish or wildlife, including significant habitat
modification or degradation that significantly impairs essential behaUoral patterns of fish
or wildlife. ActiUties that damage the habitat of listed species re0uire approC.81 from U.S.
Fish and Wildlife Serdce [USFWSDforterrestrial species or from National Marine
Fisheries Serdce 1NMFS11for marine species. FESA also reouires determination of
critical habitat for listed species and impacts to the critical habitat is prohibited. ESA
contains two pathways for obtaining permission to take listed species.
Under Section 7 of FESA, a federal agency that authoriEbs, funds or carries out a
project that may affect a listed species or its critical habitat must consult with USFWS or
NMFS, to ensure that their actions do not jeopardiDa the continued existence of
endangered or threatened species or result in the destruction or modification of the
critical habitat of these species. A Biological Opinion i$ODwould be prepared by
USFWS and NMFS to determine if the actidty would jeopardilb the continued existence
C'''gggOrange County Water District Water Production Enhancement Project 2-1
Section 2
Regulatory Framework
of the listed species. If the BO determines that the actidty would not threaten the
existence of the listed species and a no jeopardy opinion is prodded, then the project
may proceed. If the BO finds that the project would result in jeopardy to the listed
species [jeopardy opinionQ then reasonable and prudent measures would need to be
incorporated into the project to reduce potential effects to a lelel that would not be likely
to jeopardio; the continued existence of the species.
Under Section 10 of FESA pri ate parties with no federal nexus may obtain an
Incidental Take Permit to harm listed wildlife species incidental to the lawful operation of
a project. To obtain an Incidental Take Permit, the applicant must delblop a habitat
management plan that specifies impacts to listed species, proddes conseroation
measures and alternatiles to minimise impacts. If USFWS finds that the habitat
conseroation measures would not appreciably reduce the likelihood of the surdml and
reco[l;ry of the species, USFWS would issue an incidental take permit.
Migratory Bird Treaty Act
The Migratory Bird Treaty Act implements international treaties between the United
States and other nations that protect migratory birds, including their nests and eggs,
from killing, hunting, pursuing, capturing, selling and shipping unless expressly
authori[lad or permitted.
2.2 State Regulations
California Environmental Quality Act
The California Envronmental Quality Act ECEQADwas enacted in 1970 to prodde for full
disclosure of envronmental impacts before issuance of a permit by a state or local
public agency. In addition to state and federally listed species, sensitiDo plants and
animals receii,s consideration under CEQA. SensitiDq species include wildlife Species
of Special Concern listed by California Department of Fish and Wildlife [CDFWoand
plant species on the California Nati[I Plant Society list 1A, 1 B or 2.
California Endangered Species Act
The California Endangered Species Act ICESAoproddes protection and prohibits the
take of plant, fish and wildlife species listed by the State of California. Unlike FESA,
stater fisted plants haQo the same degree of protection as wildlife. A Take is defined
similarly to FESA and it is prohibited for both listed and candidate species. A Take
authorioation may be obtained from the California Department of Fish and Wildlife
1CDFW11under Section 2091 and 2081 of CESA. Section 2091 of CESA, similar to
Section 7 of FESA proddes for consultation between a state lead agency under the
California Environmental Quality Act and CDFW, with issuance of take authoriLation if
the project does not jeopardiDa the listed species. Section 2081 of CESA allows take of
a listed species for educational, scientific or management purposes.
r: Orange County Water District Water Production Enhancement Project 2-2
Section 2
Regulatory Framework
California Fish and Game Code Section 1600
The State of California defines Waters of the State as any surface water or
groundwater, including saline waters within the boundaries of the State. In accordance
with Section 1600 of the Fish and Game Code, CDFW must be notified prior to
beginning any actidty that would obstruct or dilbrt the natural Flow of, use material from
or deposit or dispose of material into a ricer, stream, or lake, whether permanent,
intermittent or ephemeral water bodies. The notification occurs through the issuance of
a Streambed Alteration Agreement. CDFW has 60 days to redew the proposed actions
and propose measures to protect affected fish and wildlife resources. The final proposal
that is mutually agreed upon by CDFW and the Applicant is the Streambed Alteration
Agreement.
California Fish and Game Code Fully Protected Species
The legislature of the State of California designated species as fully protected prior to
the creation of the California Endangered Species Act. Lists of fully protected species
were initially deleloped to prodde protection to those animals that were rare or faced
possible extinction and included fish, mammals, amphibians, reptiles and birds. Most
fully protected species haEb since been listed as threatened or endangered under
California Endangered Species Act and/or the Federal Endangered Species Act. These
species may not be taken or possessed at any time, with the only exception being
permits issued for limited scientific study.
California Fish and Game Code Sections 3503, 3513, 3800, 3801
These California Fish and Game Code Sections protect all birds, birds of prey and all
nonlgame birds, as well as their eggs and nests, for species that are not already listed
as fully protected and that occur naturally within the State. Specifically, it is unlawful to
take any raptors or their nests and eggs.
Orange County Water District Water Production Enhancement Project 2-3
Section 3
Project Description
SECTION 3.0 PROJECT DESCRIPTION
3.1 Study Area
The OCSD Plant No. 2 Site is located at 22212 Brookhurst Street within the City of
Huntington Beach. As shown in Figure 1, the site is bounded by Hamilton ACenue to the
north, Brookhurst Street to the west, Talbert Marsh and Talbert Marsh Bike Trail to the
south and the Santa Ana Ricer and the Santa Ana Ricer Trail to the east. Primary
regional access to Plant No. 2 would from Interstate 405 from the Brookhurst Street exit.
Primary local access would be from Brookhurst Street and Pacific Coast Highway.
3.2 Proposed Project Activities
The OCWD Water Production Enhancement Project consists of a Secondary Effluent
Flow EDjali-ation Tank proposed at OCSDIS Plant No. 2 Site in order to race!lb
maximum water production at the OCWD GWRS water treatment facility. OCSD® Plant
No. 2 is a wastewater treatment facility which has Elarying influent land effluentoflows of
secondary effluent. During the day, wastewater flows into OCSD® Plant No. 2 can peak
abo[>: 140 million gallons per day EMGDD These peak flows cannot be pumped to the
GWRS facility due to the limits of the conElayance facilities, i.e. effluent pump station
and pipeline; that deli[Br the secondary effluent to GWRS. Therefore, a secondary
effluent flow eoualiEation tank has been proposed at OCSDEs Plant No. 2 Site to capture
these peak flows during the day and store them in the 6Efnillion gallon tank until
nighttime. During low flows at night, the flow eDualiDstion tank would drain into the
effluent pump station to supplement the low secondary effluent inflows and allow the
GWRS to treat these peak flows which would hale otherwise been discharged to the
ocean. This secondary effluent flow eDualiDation tank would be expected to deliCer an
additional 6,000 acreJeet of secondary effluent for treatment at the GWRS facility.
3.3 Proposed Project
The Water Production Enhancement Project in[bl[Bs three construction actidties: 1❑
construction of flow eDualilation tank, 2Dconstruction of a pump station, and 3❑
construction of conCeyance piping and flow meter Eault. The improCements proposed in
the Water Production Enhancement Project are shown in Figure 2.
A 6Efnillion gallon -MG-flow eDualiEation tank would be constructed at the north end of
OCSD Plant No. 2 Site. The 6EMG tank would be a circular welded steel tank
approximately 200EPeeet in diameter and 30EBeeet tall from existing grade. The flow
eoualiElation tank would haDB a 4Epump E3 duty D 1 standby0pump deep4 approximately
500dinear feet of 36Ghch diameter connection piping with a meter Ebult 115Eft x 201 x
101 deepDconnected to the operations of the tank. The pump station would be housed
in a 301t x 402 x 201 block wall building.
Orange County Water District Water Production Enhancement Project 3-1
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Figure 1
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Figure 2
S
Section 3
Project Description
The site preparation work for the flow ellualiCation tank, pump station, and pipeline/leult
would inmlie excaleting and hauling approximately 1000 cubic yards tCYoof soil. In
addition to dirt remolial, an existing concrete parking lot would need to be demolished
for the tank pad. For this dirt excalation work, four dump trucks would be doing fi[D
round trips each oar a period of 4 days to haul the dirt off site. For the demo work, four
dump trucks would be doing three round trips each oler a period of 14 days to haul the
concrete/asphalt off site.
The flow elliali[btion tank would be constructed on concrete piles. Approximately 3011
piles would be reDuired for supporting the ellialiCation tank. To construct the pilings, 12❑
inch diameter holes would be drilled into the ground with an auger drill rig.
Approximately 40 CY of dirt from pile drilling actidty would be remoled. Once the pile
drilling is completed, the rebar support cages for the piles would be installed into the
drilled holes with a crane. Approximately 40 CY of concrete would be filled into the
holes with the rebar and cured. The piles would be supporting a 2[foot thick concrete
pad matching the diameter of the tank. This eEbates to 2,330 CY of concrete for the
tank pad. The pump station and meter moult would also reDuire approximately 100 CY of
concrete to construct these structural facilities.
Once the piles and concrete pad halle been constructed, the steel tank would be
assembled. A crane and welding laborers would be reouired to weld the steel
components of the tank together. Once the tank is welded, the surface would be
prepped for a base coat and finally painted.
While the tank is being assembled, the contractor would be edipping the pump station
and meter [bult with the use of laborers, fork lifts and cranes. The construction
eDuipment for the tank, meter Cault, flow di ersion box and pump station would include;
an excaCator, crane, pile driller, bull doer, backhoe, compactor, dump trucks, concrete
trucks, water truck, man lifts and fork lifts.
Orange County Water District Water Production Enhancement Project 3-4
Section 4
Biological Resources
SECTION 4.0 BIOLOGICAL RESOURCES
4.1 Biological Resource Setting
The study area is included in USGS Newport beach Quadrangle, Township 6 South,
Range 10 West, Section 20. OCSD Plant No. 2 site is composed of 110 acres, and is
delbloped with wastewater treatment structures, offices, and paced parking areas and
roadways. The site is bounded by Hamilton ACenue to the north, Brookhurst Street to
the west, the Santa Ana RICer and the Santa Ana Ricer Trail to the east and the Talbert
Marsh and Talbert Marsh Bike Trail to the south. A surrey conducted on OCSD Plant
No. 2 did not identify any sensible biological resources. South of the study area is the
Talbert Marsh and the California Least tern Colony.
Talbert Marsh is a tidal marsh that has been restored to full tidal action. The water
within Talbert Marsh is seawater from the ocean inlet located south of the marsh
property that fluctuates in height up to 8 feet from tidal flows. Talbert Marsh proddes
habitat for both migratory and resident bird species.
South of Pacific Coast Highway is the location the California Least Tern Natural
Preserie Area. The California Least Tern Natural Preserle Area was first established
under the Huntington State Beach General DeCelopment Plan in 1976. It was originally
dedicated on 2.5 acres and was fenced off with a cyclone fence [A heaDjLduty, chain❑
link fence topped with barbed wiredto pre Cent predators from harassing the birds. OCer
the years, the California least ternB nesting area has expanded beyond the fenced
area, State Parks has erected additional picket fencing to protect the birds. Currently,
the cyclone fence area cogs approximately 8.9 acres and the picket fence lfrontlyard❑
area is 3.8 acres. California State Parks protects the nesting area by limiting access,
conducting trash remo al, grooming the sand periodically, and conducting predator
management.
4.2 Special Status Plant Species
To determine the potential for special status plant species to be present within the study
area, the OCWD Natural Resources Department conducted a search for special status
plant species with the use of USFWS Information, Planning, and Conseristion System
Database and the CDFW Natural DiCersity Database for the Newport Beach USGS
Quadrangle. A summary of USFWS and CDFW database searches is prodded in
Appendix A.
A listing of special status plant species within potential to occur within the Newport
Beach USGS Quadrangle is shown in Table 1. The determination on the potential for
the special status plant species to occur within the study area was based on the
following criteria:
• Present: Species was obserled within the study area within the last year.
Orange County Water District Water Production Enhancement Project 4-1
Section 4
Biological Resources
• High: The study area supports suitable habitat and the species has been
obserCed within the last year.
• Moderate: The study area supports suitable and the species has not been
obserced within last two years.
• Low: The study area lacks suitable habitat for the species.
Table 1: Sensitive Plant List
Species Federal State CNPS General Potential for
HabitaVRecent Occurrence Study
Occurrence Area
Chaparral sand NL NL IBA Coast Scrub Low
Verbena Chaparral. Species presumed
(Abronia Villosa extirpated
var. aunts
Aphanisma NL NL 1B.2 Coastal Scrub, Low
(Aphanisma Coastal Bluff Scrub, Study Area lacks
blitoides) Coastal Dunes suitable habitat
Venture Marsh E NL Marshes,Swamps, Low
Milkletch Coastal Dunes, Study Area lacks
EAstragalus Coastal Scrub suitable habitat
pycnostachy
lar.
Lanosissimus
Coulter® NL NL 1B.2 Coastal Scrub, Low
Saltsbush Coastal Bluff Scrub, Study Area lacks
(Atriplex Coastal Dunes suitable habitat
coulter
South Coast NL NL 1B.2 Coastal Scrub, Low
Saltscale Coastal Bluff Scrub Study Area lacks
suitable habitat
DaEidsona NL NL 1B.2 Coastal Scrub, Low
Saltscale Coastal Bluff Scrub Study Area lacks
(Atnplex suitable habitat
serenana var.
davidsonii
Southern NL NL 1B.1 Marshes and swamps Low
Tarplant Study Area lacks
(centromadia suitable habitat.
panyi ssp.
Australis
Salt Marsh E E 1B.2 Coastal Salt marsh, Low
BirdsEbeak Coastal Dunes Study Area lacks
(Chloropyron suitable habitat.
maritimum ssp.
Mantimum
Many Stemmed NL NL 1B.2 Chaparral, Coastal Low
Dudleya Scrub Study Area lacks
(Dudlaya suitable habitat
Multicaulis
San Diego E E IBA Vernal pools, Coastal Low
Button J'elery Scrub,Valley and Study Area lacks
EEryngium Foothill Grasslands suitable habitat
aristulatum car.
arrishiiE
vOrange County Water District Water Production Enhancement Project 4-2
Section 4
Biological Resources
Los Angeles NL NL 1A Marshes and Swamps Low
Sunflower Study Area lacks
(Helianthus suitable habitat
nuttallii ssp.
Parishii
Coulter® NL NL 1B.1 Coastal Salt marshes Low
Goldfield Study Area lacks
masthenia suitable habitat
glabrata ssp.
Coulter
Mud name NL NL 2.2 Marshes and swamps Low
(Name Project area lacks
steraccarfai suitable habitat
Gambels Water E T 1B.1 Marshes and swamps Low
Cress Study Area lacks
(Nasturtium suitable habitat
ana lfi
Prostrate NL NL 1B.1 Vernal pools, coastal Low
Vernal Pool scrub Study Area lacks
NaEarretia suitable habitat
(Navarrefia
Prostrate)
Coast NL NL 1B.2 Coastal Dunes Low
woollyheads Study Area lacks
(Nemacaulis suitable habitat
denudate par.
denudate
Estuary NL NL 1B.2 Marshes and swamps Low
Seablite Study Area lacks
(Sueede suitable habitat
Esteroa
San Bernardino NL NL 18.2 Marshes and swamps, Low
Aster coastal scrub Study Area lacks
(Symphyofrchu suitable habitat
in defoliatum
Federal State Listing Eelifornia Endangered California Nati®P=Soi CNPS
ECEndangered Species Act CDFG 1APlants presumed distinct in California
TSnnotened FPTully Protected isrPlants pure,threatened or endangered In California
SSC-Spacial Species of Concern EEndangamd and elsewfiere
C Candidate for Listing TThreatened 2Plants pure,threatened or endangered in California
NL 1Nol Listed SSensitia but mare common Worsham
SSC Special Species of Concern 3Plants about Mich we need more renew
WL Watch List 4 Plants of limited distribution
NL Not Listed CNPS Threat Rank
.1 Seriously Endangered
.2 Fairly Endangered
.3 Not Very Endangered
4.3 Special Status Wildlife Species
To determine the potential for special status wildlife species to be present within the
project area, the OCWD Natural Resources Department conducted a search for special
status wildlife species with the USFWS Information, Planning, and Conserilation System
Database and the California Department of Fish and Wildlife Natural DiDersity
Database. A summary of USFWS and CDFW database searches is prodded in
Appendix A.
Orange County Water District Water Production Enhancement Project 4-3
Section 4
Biological Resources
A listing of special wildlife species within potential to occur within the Newport Beach
USGS Quadrangle is shown in Table 2. The determination on the potential for the
special status wildlife species to occur at the project area was based on the following
criteria:
• Present: Species was obserIJA within the study area within the last year.
• High: The study area supports suitable habitat and the species has been
obser[Jad within the last year.
• Moderate: The study area supports suitable and the species has not been
obserled within last two years.
• Low: The study area lacks suitable habitat for the species.
Table 2: Special Status Wildlife
Species Federal State General Habitat/Recent Potential Occurrence
Occurrence Study Area
Orange throat NL SSC Low leC l coastal scrub, Low
Whiptail sandy areas with patches Study Area lacks
As idoscelis h e hra of scrub suitable habitat
Burrowing owl NL SSC Open growing low Low
(Athens cuniculana) grasslands Study Area lacks
suitable habitat
San Diego Fairy Shrimp E SSC Vernal pools Low
(Branchinecfa Study Area lacks
sandie onensis) suitable habitat
Western Snowy Plover T SSC Sandy Beaches Low
(Charaddus alexandrines Study Area lacks
nivosus) suitable habitat
Southwestern Willow E E Riparian woodlands Low
Flycatcher Study Area lacks
Em idonax trailli extimus suitable habitat
Western Mastiff Bat NL SSC Roosts in cliffs,tall Low
(Eumops perotis buildings,trees and Study Area lacks
califomicus) tunnels suitable habitat
Big free Bat NL SSC Roosts in cliffs,tall Low
(Nycfinomops macrons) buildings,trees and Study Area lacks
tunnels suitable habitat
Pacific Pocket Mouse E SSC Coastal Plains Low
(perognathus Study Area lacks
lon imembds pacifujs suitable habitat
Coast Horned LiEard NL SSC Low lands along sandy Low
(Phrynosoma blainvillii) washes with scattered Study Area lacks
brush suitable habitat
Coastal California T SSC Coastal sage scrub Low
Gnatcatcher Study Area lacks
(Poltophla califomica suitable habitat
califomica
Lightlffooted Clapper Rail E E Salt marshes Low
(Rallus longirostris levipes) Study Area lacks
suitable habitat
Southern California NL SSC Coastal Marshes Low
S'alltmarsh Shrew Studv Area lacks
Orange County Water District Water Production Enhancement Project 4-4
Section 4
Biological Resources
Sorex oratus suitable habitat
California Least Tern E E Sandy Beaches Low
(Sterna antillari Study Area lacks
suitable habitat
Least Bells dreo E E Low growing riparian Low
(Vireo bellil pusillus) habitats Study Area lacks
suitable habitat
Legend
Federal Endangered Species And
El Endangered
T Threaten.
SSG Special Spedes of Concern
Cl Candidate for Listing
California Endangered Species ActlCali(omia OagarMerd Fish Game
Flo Fully Protected
EfEndangered
TThreatenad
SISansiti a
SSG Special Species of Concern
WLroi Llal
4.4 Critical Habitat
The Federal Endangered Species Act reDjires the federal goCernment to designate
Critical Habitat for any species it lists under the Federal Endangered Species Act.
Critical Habitat is defined as 1 -specific areas within the geographical area occupied by
the specie at the time of listing, if they contain physical or biological features essential to
conserllation, and those features may relyire special management considerations or
protection and 2Dspecific areas outside the geographical area occupied by the species
if the agency determines that the area itself is essential for conseriation. According to
the of USFWS Information, Planning, and Conseriation System Database and the
California Department of Fish and Wildlife Natural DiCersity Database, the study area is
not located on lands that are designated as Critical Habitat.
4.5 Federal and State Jurisdictional Aquatic Resources
Waters of the United States
A water body is considered Waters of the U.S. if it is: L7 Ltraditional nadgable water
ITNWq [20wetlands adjacent to a TNW; 1311norilhadgable tributaries of TNW that ha[B
perennial or seasonal Flow of water; and 14Dvvetlands that are adjacent to non[thadgable
tributaries of TNW that hallb perennial or seasonal flow of water.
There are no Waters of the U.S. on the OCSD Plant No. 2 Site. The closest surface
water body within the ❑cinity of the study area is the Santa Ana Ricer. The Santa Ana
Ricer drains into the Pacific Ocean. The Pacific Ocean is nadgable water and therefore
Santa Ana Ricer is classified as a tributary to a nadgable water and Waters of the U.S.
The Federal jurisdiction along the Santa Ana Rimer extends to the ordinary high water
mark and to any adjacent wetland Cegetation.
Orange County Water District Water Production Enhancement Project 4-5
Section 4
Biological Resources
Waters of the State of California
According to the State Water Code, Waters of the State are defined as any surface
water, groundwater or wetlands within the boundary of the state. There are no waters of
the State on the OCSD Plant No. 2 Site. The Santa Ana Ricer is classified as Waters of
the State. The State jurisdiction along the Santa Ana Ricer extends to the top of the
slope to adjacent wetland Cegetation.
Wetland Waters of the United States and State California
Wetland Waters are a subset of jurisdictional Waters of the U.S. and the State.
Generally, wetlands are lands where saturation with water is the dominant factor
determining the nature of soil delelopment and the types of plant and animal
communities lidng in the soil and on its surface. Wetlands generally include swamps,
freshwater marshes, brackish water and saltwater marshes, bogs, lernal pools,
periodically inundated salt flats, intertidal mudflats, wet meadows, wet pastures, springs
and seeps, portions of lakes, ponds, riD3rs and streams and all areas which are
periodically or permanently colared by shallow water, or dominated by hydrophilic
�egetation, or in which the soils are predominantly hydric in nature.
Presently, there is no single definition for wetlands. Howelbr, all resource agencies
recognile that wetlands must demonstrate the following three essential elements: []❑
the site periodically supports hydrophytic Degetation, 2rthe site contains hydric soil and
13Ethe site periodically contains water or the soil is saturated with water at some time
during the growing season of each year.
Orange County Water District Water Production Enhancement Project 4-6
Section 5
Project Impacts
SECTION 5.0 PROJECT IMPACTS
5.1 Threshold of Significance
The following threshold of significance was used to elaluate potential impacts to
biological resources associated with implementation of the GWRS Final Expansion
Project.
• Would the project haD3 a substantial adverse effect, either directly or through
habitat modifications on any species identified as a candidate, sensitille or
special status species in local or regional plans, policies, or regulations or by the
California Department of Fish and Wildlife or U.S. Fish and Wildlife Serdce❑
• Would the project ham a substantial adverse effect on any riparian habitat or
other sensitive natural community identified in local regional plans, policies and
regulations or by the California Department of Fish and Wildlife or U.S. Fish and
Wildlife Serdce❑
• Would the project hale a substantially ad[brse effect on federally protected
wetlands as defined by Section 404 of the Clean Water Act through direct
remolial, filling hydrological interruption, or other means❑
• Would the project interfere substantially with the moCement of any nati[19 resident
or migratory fish or wildlife species or with established nati[E resident or
migratory wildlife corridors, or impede the use of natiCe wildlife nursery sites❑
• Would the project conflict with any local policies or ordinances protecting
biological resources, such as a tree preserlation policy or ordinance[]
• Would the Project be in conflict with the prodsions of an adopted Habitat
Conservation Plan, Natural Community Conservation Plan, or other approved
local, regional, or state habitat consermtion plan❑
5.2 Project Impacts
A: Would the project have a substantial adverse impact, either directly or through
habitat modifications, on any species identified as a candidate, sensitive or
special status species in local or regional plans, policies or regulations or by the
California Department of Fish and Game or U.S. Fish and wildlife Services?
Onsite Impacts
Based on a redew of databases from United State Fish and Wildlife Serdce and
California Department of Fish and Wildlife and biological surCeys conducted within the
study area, it has been determined that there would be low potential for special status
plant species or special status wildlife species to be present on OCSD Plant No. 2. As
shown in Table 1 and Table 2, Plant No. 2 lacks suitable habitat to support special
status plant species or special status wildlife species that were identified in the
V Orange County Water District Water Production Enhancement Project 5-1
Section 5
Project Impacts
database search. Additionally, no indications were found that any special status species
were eler present. Therefore, implementation of the proposed project would not result
in ad[arse impacts to any special status plant species or special status wildlife species.
Offshe Impacts
Located south of OCSD Plant No. 2 is the Talbert Marsh and south of Pacific Coast
Highway is the California Least Tern Colony. Both of these biological resources could
prodde suitable nesting habitat for special status bird species. The construction
operations for the proposed project would be confined to OCSD Plant No. 2. No
construction actidties would occur at the Talbert Marsh or at the California Least Tern
Colony. Therefore, no direct impacts to special status plant or wildlife species would
occur.
The construction actidties for the proposed project would in IIbIE13 the operation of heaDJ
construction emipment that could operate during nesting season. If the construction
actidty was to occur in close proximity to nesting birds there would be the potential that
breeding patterns could be disturbed. The United States Fish and Wildlife Serdce as
established a noise impact threshold of 60 dBA to identify potential ad[Erse impacts to
nesting birds. The Talbert Marsh is located approximately 3,300 feet from where the
construction actidties would occur and the California Least Tern Colony is located
approximately 4,200 feet from the construction would occur. Based on the nosiest
piece of construction eLuipment that would be used, the noise estimated IeCel at the
Talbert Marsh and at the California Least Tern Colony would be below 49 dBA.
Additionally, with the presence of the block wall around Plant No. 2 and the traffic noise
along Pacific Coast Highway, it would be Eery unlikely that construction noise would
herd at either location. Potential indirect noise impacts to special status wildlife species
would be less than significant. No mitigation measures are re0uired.
B: Would the project have a substantial adverse impact on any riparian habitat or
natural community identified in local or regional plans, policies, and regulations
or by the California Department of Fish and Game or U.S. Fish and Wildlife
Service?
The location where the proposed Flow enialiEation tank and pump station structure
would be constructed is currently paled or in a disturbed condition. A suriby conducted
at the location where the flow eElualilation tank and pump station structure would be
constructed did not identify any sensiti[L Eegetation communities. Therefore,
implementation of the proposed project would not result in ad[t:rse impacts to sensitilb
natural communities.
C: Would the project adversely impact federally protected wetlands either
individually or in combination with the known or probable impacts of other
Orange County Water District Water Production Enhancement Project 5-2
Section 5
Project Impacts
activities through direct removal, filling hydrological interruption, or other
means?
The location where the proposed flow eaaliLation tank and pump station structure
would be constructed is paced or in a disturbed condition. A preliminary site surCey
conducted on the study area did not identify any reDuired parameters that define
Wetland Waters of the U.S. or State. Therefore, the implementation of the proposed
project would not ad[brsely impact Wetland Waters of the U.S or State.
D: Would the project interfere substantially with the movement of any native
resident or migratory fish or wildlife species or with established native resident or
migratory wildlife corridors, or impede the use of native wildlife nursery sites?
The OCSD Plant No. 2 Site is currently improled with buildings, wastewater treatment
facilities, roadways and parking areas. The site does not contain suitable habitat or
prodde linkages to suitable habitat to support wildlife moibment. Along the perimeter of
Plant No.2 are a row of eucalyptus trees that could prodde potential nesting
opportunities for migratory birds. Therefore, construction actidties for the proposed
project would not in[bl[e the remollal of any trees. Therefore, potential direct impacts to
nesting migratory birds would be abided. Additionally, sound attenuation measures
would be incorporated into the project to minimiCe noise impacts in the study area.
The Talbert Marsh is located approximately 3,600 feet from the construction actidties
and the California Least Tern Colony is located approximately 4,500 feet from where the
construction would occur. At the distance the construction noise lelels would be
minimal and would not pose a potential disruption to nesting birds. The implementation
of the proposed project would not result in significant adil�rse impacts to migratory birds
or result in significant adEerse impacts to wildlife movement. No mitigation measures
are reDuired.
E: Would the project conflict with any local policies or ordinances protecting
biological resources, such as tree preservation policy or ordinance?
The City of Huntington Beach does not haDa any local policies or ordinances that
prodde for the protection of management of biological resources that would apply to the
study area. Therefore, implementation of the proposed Water Production Enhancement
Project would not be in conflict with local polices or ordinances that prodde for the
protection of biological resources.
F: Would the project be in conflict with provisions of an adopted Habitat
Conservation Plan, Natural Community Conservation Plan, or other approved
local regional or state habitat conservation plan.
The OCSD Plant No. 2 Site is not included within adopted Habitat Conserlation Plan.
Therefore, implementation of the proposed project would not be in conflict with any
app@@@@roled Habitat Management Plan or Natural Community Conseriation Plan.
v' Orange County Water District Water Production Enhancement Project 5-3
Section 6
References
SECTION 6.o REFERENCES
California Department Fish and Game Natural Diij�rsity Database, Accessed March
2016.
California NatiCe Plant Society InCentory of Rare and Endangered Plants Database,
Accessed March 2016.
City of Fountain Valley General Plan, Web Site Accessed ane 2016
City of Huntington Beach General Plan, Accessed one 2016.
Orange County Water District Groundwater Management Plan, 2009.
U.S. Army Corps of Engineers List of Wetland Plants, 2008.
U.S. Army Corps of Engineers Regional Supplement to the Corps of Engineers Wetland
Delineation Manual Arid West Region, September 2008.
United States Fish and Wildlife Information, Planning, and Conserlation System
Database, Accessed Lune 2016.
Orange County Water District Water Production Enhancement Project 6-1
Appendix C
Phase I Cultural Resources Study
[Click here and enter Draft phase]
Groundwater Replenishment System Final Expansion Project
and Water Production Enhancement Project
Phase I Cultural Resources Study
Prepared for August 2016
Orange County Water District
r ESA
J
[Draft phase here]
Groundwater Replenishment System Final Expansion Project
and Water Production Enhancement Project
Phase I Cultural Resources Study
Prepared for August 2016
Orange County Water Distdot
2121 N Parkway ESA
sutte 1 W
Irvine.CA 92606
969➢M.7M
NM1WI.pCmet.COm
IMie Sacramento
Les Angeles San De o
OaMand San Fmnci.
Od"o Santa M.I.
Pasadena S. M.
Petaluma Tampa
Pord.d Woa Wd Hllls
1& 8].01
Table of Contents
Groundwater Replenishment System Final Expansion Project
and Water Production Enhancement Project Phase I Cultural
Resources Study
Pace
1. Introduction..................................................................................................................1
1.1 Project Location....................................................................................................2
1.2 Project Description................................................................................................2
2. Area of Potential Effects...........................................................................................10
3. Setting ........................................................................................................................13
3.1 Endronmental Setting.........................................................................................13
3.2 Prehistoric Setting...............................................................................................13
3.3 Ethnographic Setting ..........................................................................................14
3.4 Historic Setting....................................................................................................16
4. Regulatory Framework..............................................................................................19
4.1 Federal ...............................................................................................................19
4.2 State...................................................................................................................20
5. Archival Research .....................................................................................................25
5.1 South Central Coastal Information Center Records Search ...............................25
5.2 Historic Map and Aerial Redew..........................................................................27
5.3 NatlID American Heritage Commission..............................................................28
5.4 Geoarchaeological Redew.................................................................................32
6. Paleontological Records Search..............................................................................35
7. Cultural Resources Survey and Results..................................................................36
8. Conclusions and Recommendations.......................................................................37
8.1 Archaeological Resources..................................................................................37
8.2 Historic Built Resources......................................................................................39
8.3 Paleontological Resources.................................................................................39
9. References.................................................................................................................41
G.adweler Repleni0msnl syelem Firth Espenaian Prgea ene E8 1160W 01
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Phase I Cultural Resmrres S dy
Table of Contents
Pace
Appendices
A. Resumes
B. SCCIC Records Search Results
C. Natilb American Correspondence
D. Photographs of the Project APE
List of Figures
Figure 1 Local Vicinity Map Topographic Base......................................................................3
Figure 2 Project Location Topographic Base.........................................................................4
Figure3 Site Plan..................................................................................................................5
Figure 4 Area of Potential Effects........................................................................................11
List of Tables
Tablet Predous Cultural Resources Iniestigations including the Project APE.................25
Table 2 Predously Recorded Cultural Resources within o[mile of the Project APE..........26
Table 3 NatiCe American Outreach.....................................................................................29
G.adweler Wenis6manl syelem Firth Espenaian Prgea ene ES 116036].01
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Phase I CUIWnl Resmrres S dy
Groundwater Replenishment System Final Expansion Project
and Water Production Enhancement Project
Phase I Cultural Resources Study
1 . Introduction
Environmental Science Associates(ESA)has been retained by the Orange County Water District
(OCWD)to prepare a Cultural Resources Study for the proposed Groundwater Replenishment
System(GWRS)Final Expansion Project and the Water Production Enhancement Project
(referred below as the project)located in the cities of Huntington Beach and Fountain Valley,
California. The GWRS is an existing advanced water treatment facility constructed by the OCWD
and the Orange County Sanitation District(OCSD)that supplements local water supplies by
providing reliable,high-quality source of treated water to recharge the Orange County
Groundwater Basin,and to protect the Orange County Groundwater Basin from seawater
intrusion.The project would provide facilities that would allow an increase in the amount of
water to be conveyed to the GWRS and further supplement the local water supplies.The GWRS
Final Expansion Project involves eight components: (1)increasing microfiltration(MF)capacity;
(2)increasing reverse osmosis(RO)treatment capacity; (3)increasing ultraviolet(UV)treatment
capacity;(4)increasing final product water capacity;(5)construction of an effluent pump station:
(6)conversion of existing gravity pipeline to a pressurized pipeline;and(7)construction of a
separate headworks and bypass pipeline.The Water Production Enhancement Project involves the
proposed flow equalization tank with a pump station,and conveyance piping and flow meter
vault.
The project is eligible for funding from the State Revolving Fund(SRF)Loan Program,which is
administered by the California State Water Resources Control Board(SWRCB). Since the SRF
Loan Program is partially funded by the U.S.Environmental Protection Agency(EPA),it is
subject to federal environmental regulations including Section 106 of the National Historic
Preservation Act(NHPA)of 1966,as amended.This Phase I cultural resources study has been
prepared in support of the environmental documentation being prepared for the GWRS Final
Expansion Project and the environmental documentation being prepared for the Water Production
Enhancement Project in compliance with CEQA and Section 106 of the NHPA. The OCWD is
the lead agency responsible for compliance with CEQA.
ESA personnel involved in the preparation of this study include: Candace Ehringer,M.A.,R.P.A.,
Principal Investigator;Arabesque Said-Abdelwahed,MPP,report author and surveyor;Vanessa
Ortiz,M.A.,R.P.A, literature review analyst.Resumes of key personnel me provided in
Appendix A.
Gmadwater Wenla6manl syelem Final EVerson P,gea and E8 1160387.01
Wader P,otluom Enhanosmmr Progd t Auaua12016
Phase I Cultural Reamrres S dy
Groundwater Replenishment System Final Eglansloo Proleot and Water Pmdudlon Enhharh a nk Proled.Phase I Cultural Resource.Study
1. InO dudion
1 .1 Project Location
The project is located within the cities of Fountain Valley and Huntington Beach(Figure 1).
A portion of the project is located at the existing OCWD GWRS Facility in Fountain Valley.
The project is also located at the southern portion of OCSD Treatment Plant No. I and OCSD
Treatment Plant No. 2 in Huntington Beach.In addition,the project includes the renovation of an
existing waste water pipeline located along the west side of the Santa Ana River that extends
from Treatment Plant No.2 to the OCWD GWRS Facility. The project is located within section
32 of Township 5 South/Range 10 West and it is located in sections 5, 17,20, of Township 6
South/Range 10 West as shown on the Newport Beach, California 7.5-minute U.S.Geological
Survey topographic map(Figure 2).
1 .2 Project Description
The project evaluated in this report comprises of two separate projects. The first is the GWRS
Final Expansion Project.The second is the Water Production Enhancement Project.The
components of each project are illustrated in Figure 3 as well as the potential staging area.
1.2.1 GWRS Final Expansion Project
This project includes conversion of an existing gravity pipeline to a pressurized pipeline,
increasing MF capacity,increasing RO Treatment Capacity,increasing UV treatment capacity at
the OCWD GWRS Facility, final product water and construction of a pump station at the OCSD
Plant No. 2. The GWRS takes highly treated wastewater that would have been previously
discharged into the Pacific Ocean and purifies it using a three-step advanced treatment process
consisting of MF, RO and UV light with hydrogen peroxide. Specifically,the project will include
the following seven improvements,as well as potential staging areas:
1.2.1.1 Microfiltration Capacity
The project would increase the MF treatment capacity by approximately 45 million gallons per
day(MGD). The expansion of the MF facility at the OCWD water treatment site involves
construction of 12 new treatment basins increasing the overall number of treatment basins from
36 to 48. The construction of the 12 new basins would occur by increasing the size of the MF
building and basement,which houses most of the actual MF equipment. The MF basement
includes all piping,valves,pumps,instruments, and control panels. The basement would be
expanded by excavating an area of approximately 88-feet long by 165-feet wide by 25-feet deep
from finished grade. The depth of disturbed soils is unknown;therefore,excavations may extend
to native and undisturbed soils.
Gmadv eler Paremanmenl syelem Final EVanslan Prgea and E8 116OW.01
Wader P,otludim Enhanosmeni Pmeo 2 Auaus12016
Phase I Cultural Resmrres SWdy
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Project Location Topographic Base
OCSD Plant No. 1 and OCSD Plant No.2
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Figure 3
Site Plan
Groundwater ReelenlshmeM System Final Eq nslon Project and Water Pmdudlon Enhanc MProfed.Phase I Cullum)Resources aWdy
1. InOrodudion
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Ph—ICUllwel ReSwrcas SWd,
Groundwater ReplenlshmeM System Final apansbn Pmled and Waler ProduMon Enha memeM Prolml.Phase I Cultural Resources,SWdy
1. Introduetion
In the excavated area,a foundation would be built including installation of foundation piles. The
12 new concrete treatment basins would be constructed on this foundation. Each basin would be
installed with a centrifugal pump,associated piping,and other appurtenances. These 12 new
treatment basins would make up a one and a half new treatment trains that would be added to the
existing two trains within the MF West building.In addition,most of the electrical equipment
associated with the new treatment basins would be added to the new expanded MF West
electrical building.
The MF product water or effluent discharges into an existing 2 million gallon underground
concrete reservoir commonly referred to as a break tank. This reservoir contains two sets of
vertical turbine pumps.One set(six existing pumps)is used for pumping MF product water back
to the MF facility for a backwashing process. The other set of pumps(six existing pumps)is used
to transfer the MF product water from the reservoir to the RO Facility.As part of the final
expansion,two new 200-horsepower vertical turbine pumps would be installed in the existing
break tank facility to pump MF product water back to the MF facility for the backwash process.
The break tank facility already has pump slots constructed for these two new pumps, and
therefore,the construction work for these pumps only involves lifting the pumps into the slots and
connecting up the piping and electrical.
1.2.1.2 Reverse Osmosis Treatment Capacity
The project would increase the RO treatment capacity by approximately 30 MGD. The project
would include the installation of up to six additional treatment trains at the OCWD water
treatment site.The treatment train includes pressure vessels,RO membranes,RO feed pumps,
and associated piping for each train.The new equipment for the six new trains would be tied into
the existing piping for the expansion.No excavation would be required.
1.2.1.3 Ultraviolet Treatment Capacity
The project would increase the UV Treatment capacity at the OCWD water treatment site by
approximately 30 MGD.The project would install three additional treatment trains.Each train
would consist of three steel vessels containing 432 total UV light lamps. Each vessel would be
equipped with two electrical panels,feed and product piping,valves and instruments. The
existing concrete pad and canopy would be sized to house the three new trains.Therefore,only
the equipment for each of the three trains would need to be installed in their designated areas.
Equipment required for this phase includes one crane,one fork lift and two man lifts.No
excavation would be required.
1.2.1.4 Final Product Water
The project would also expand the chemical and final product water facilities at the OCWD water
treatment site.As part of the project,one additional decarbonation tower would be added to the
existing decarbonation area. The concrete pad for the decarbonation tower is already constructed.
An additional pump would also be added to the existing product water pump station. The pump
would be a 2,000-horsepower vertical turbine pump installed within an existing pump station
building with a slot already in place.No excavation is required.
Gmadwater Wenlahmanl S d an Final Espansan Prgea and ESP MiS7.01
Wader Pmtludim Enhanosmem Pmed 7 Auaua12016
Phase I Cultural Resmrres SWdy
Groundwater Replenlshmert S)stem Final Eglanslm Proled and Water Pmdudlon Enhhanc saat Profed.Pha.e I CUIWml Resource..lady
1. Int'odudion
1.2.1.5 Construction of OCSD Plant No. 2 Effluent Pump Station
A new pump station(Effluent Pump Station)would be constructed at the OCSD Plant No. 2 to
convey water flows within the existing OCSD pipeline to the OCWD water treatment facility site.
The pump station would include four pumps(three duty and one standby)with the capacity to
pump 30 MGD each. The pumps would be housed in a new concrete pump house,approximately
100-feet long by 50-feet wide by 20-feet high with a 25-foot deep wet well.
In addition to the Effluent Pump Station,a second smaller Plant Water Pump Station would be
constructed at OCSD's Plant No. 2. The Plant Water Pump Station serves OCSD's Plant No.2
with hose bib and washdown water for plant operations. The Plant Water Pump Station would
have four plant water pumps housed in a 48-feet long by 58-feet wide by 20-feet high concrete
building.The concrete wet well for the pumps is estimated to be 25-feet deep.The depth of
disturbed soils is unkra wn;therefore,excavations may extend to native and undisturbed soils.
1.2.1.6 Pipeline Re-Lining
The source water for the project would come from both of the treatment plants owned and
operated by the OCSD. Facilities are already in place to receive source water,secondary effluent,
from OCSD's Plant No. 1 wastewater treatment facility.However,to provide an additional
60 MGD of source water for the project,OCWD would need to receive additional wastewater
flows from OCSD Plant No.2 wastewater treatment site.To convey the wastewater flows to the
GWRS water treatment site,an existing 3.5-mile long,66-inch diameter gravity concrete
reinforced pipe(CRP)would be relined to become a 54-inch diameter pressure pipeline. The
existing pipeline is located along an OCSD easement corridor that extends west of the Santa Ana
River levee. The OCSD easement corridor is located on approximately 5 feet of fill material
(OCWD,pers.comm.and SRI,2007).The re-lining of the pipeline will be completed either by
utilizing existing manholes(approximately spaced 2,000 feet from each one)for access into the
pipeline or by excavating a 10-feet wide by 10-feet long by 5-feet deep area to expose the
pipeline to allow entry into the pipe to re-line the existing pipeline.For each option,construction
equipment would be staged at each pipeline opening.As shown in Figure 3,eight entry locations
are proposed.All excavations along the eight entry locations would be within fill and recently
disturbed soils. To connect the pipeline to the new Effluent Pump Station on the OCSD facility,
approximately 100 feet of 54-inch diameter steel pipe would be constructed.Additionally,to
connect the pipeline to OCWD facilities, approximately 100 feet of 54-inch diameter steel pipe
would be installed by trenching and backing filling on OCWD property. The depth of fill material
is unknown at this location in OCSD Plant No. 1.
1.2.1.7 OCSD Plant No. 2 Separate Headworks and Bypass Pipeline
The majority of the wastewater flows from OCSD Plant No. 2 are needed as source water to meet
the demands of the project. Currently,OCSD Plant No. 2 receives reject concentrated brine
waters from treatment processes from the Inland Water Agencies. These concentrated reject
flows,i.e.brines,are currently not allowed to be recycled through the existing GWRS per the
Division of Drinking Water permit for GWRS.Therefore,a separate headworks facility and a
bypass pipeline would be constructed on OCSD's Plant No.2 that would segregate the brine
flows from the typical influent domestic wastewater flows to Plant No. 2. The bypass pipeline
cFUna rite,RB ..iAmN1 syalem Flydl P".aIN Pr .O era E8 I WWI 01
Wa er Pmtludim Enhancement Propel 8 Auaus12016
Phase I Cultural Reamrres S dy
Groundwater ReplenlshmeM System Final E pansbn Pmled antl WMer ProduMon Enha memeM Protect Phase I Cultural Resources Shady
1. Introduction
would be a 66-inch diameter CRP with an alignment that runs approximately 200 feet around the
existing headworks for Plant No.2. Connected to the bypass pipeline would be a new separate
headworks facility,including a screenings building(65-feet long by 55-feet wide by 20-feet deep)
and a grit basin building(65-feet long by 40-feet wide by 20-feet deep). Also along the bypass
pipeline alignment would be a 20-feet deep concrete metering vault with vault dimensions of 100-
feet wide by 100-feet long by 14-feet deep.Excavation would be required for this component of
the project.This project component location is underlain by disturbed soils from previous
placement of several pipelines(OCSD,pers.comm.).The depth of disturbed soils is unknown;
therefore,excavations may extend to native and undisturbed soils.
1.2.2 Water Production Enhancement Project
The Water Production Enhancement Project involves three construction activities: (1)construction
of flow equalization tank,(2)construction of a pump station, and(3)construction of conveyance
piping and flow meter vault.
A 6-million-gallon(MG)flow equalization storage tank would be constructed at the north end of
OCSD Plant 2.The location of the flow equalization storage tank is shown in Figure 3. The
storage tank would be a circular-welded steel tank approximately 200-feet in diameter and 30-feet
tall from existing grade,with a 4-pump(3 duty+ 1 standby),pump station,and approximately
500-linear feet of 36-inch diameter connection piping with a meter vault(15-x 20-x 10-ft deep)
connected to the operations of the tank.The pump station would be housed in a 30-x 40-x 20-ft
block wall building.
Excavation would be required for construction of the flow equalization tank,pump station,and
pipeline/vault. In addition to excavation,an existing concrete puking lot would be demolished
for the tank pad.
1.2.3 Potential Staging Areas
During construction of the project,construction equipment,vehicles,and materials could be
stored at up to two staging areas: the OCSD Plant No. 2 and along the existing pipeline at each
pipeline opening.No excavations would occur at the potential staging areas.
cmundwner Parenlahment syelem Final Espensan Prgea and ESP 116OW 01
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Phase I Cultural Resmrres Shady
Groundwater Recienlshmenl System Final Egmnslm Proled and Water Pmdudlon Enhanc M Profed.Pha.e I Culluml Resource.Study
2.Area M Pdendel Effects
2. Area of Potential Effects
An Area of Potential Effects(APE)was established for the project according to Section 106 of
the NHPA in coordination with the OCWD(Figure 4). An APE is defined as:
...the geographic area or areas within which an undertaking may directly or indirectly
cause alterations in the character or use of historic properties,if any such properties exist.
The APE is influenced by the scale and nature of an undertaking and may be different for
different kinds of effects caused by the undertaking(36 Code of Federal Regulations
[CFR] 800.16[d]).
The horizontal APE encompasses the ME Building Expansion(about 0.50-acre), 3.5-mile long
existing pipeline,the excavation area for OCSD pipeline(about 650 square feet),the contractor
laydown area(about 0.70-acre),the area encompassing the Flow Equalization Pump Station and
Flow Equalization Control/Meter(about 3.70-acres),the area encompassing the OCSD pump
station(about 0.28 acre), and the area encompassing the headgates and bypass pipeline(about
0.5 acre).The vertical APE includes the anticipated maximum depth of ground disturbance of
25 feet below ground surface and the maximum height of the flow equalization tank of 30 feet
above ground surface.
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3. Sefting
3. Setting
3.1 Environmental Setting
The project is located in the cities of Huntington Beach and Fountain Valley,Orange County, in
southern California. The topography of Orange County includes a combination of mountains,
hills, flatlands,and shorelines. Urbanized Orange County is predominantly within an alluvial
plain,semi-enclosed by the Puente and Chino Hills to the north,the San Joaquin Hills to the
south,and the Santiago Foothills and the Santa Ana Mountains to the east. The Puente and Chino
Hills,which identify the northern limit of the plains,extend for 22 miles and reach a peak height
of 7,780 feet.To the east and southeast of the plains are the Santa Ana Mountains,which have a
peak height of 5,691-feet.The Santa Ana River is located adjacent to and just east of the project
APE.
The City of Huntington Beach is located near the coastal margin of the Los Angeles Basin,which
includes Orange County,and is underlain by more than 15,000 feet of stratified sedimentary
rocks of marine origin(Oakeshott, 1978). Soils in the project APE are composed of younger
alluvium that is divided into river floodplam deposits(washed in from the northeast as sand,
gravel and silt), and tidal flat/lagoonal type deposits lie in the gaps(finer-grained silts and clays)
(City of Huntington Beach, 1996).
3.2 Prehistoric Setting
The prehistory of the region has been summarized within four major horizons or cultural periods:
Early[10,000 to 8,000 before present(B.P.)],Millingstone(8,000 to 3,000 B.P.),Intermediate
(3,000 to 1,500 B.P.),and Late Prehistoric(1,500 BY to A.D. 1769)(Wallace, 1955;Warren,
1968).
3.2.1 Early Period (10,000 to 8,000 B.P.)
The southern California coast may have been settled as early as 10,000 years ago(Jones, 1992).
These early inhabitants were likely maritime adapted groups exploiting shellfish and other marine
resources found along the coastline(Dixon, 1999; Erlandson, 1994;Vellanoweth and Altschul,
2002).One site located in Newport Bay,Orange County(CA-ORA-64)dates to approximately
9,500 years B.P.and suggests early intensive utilization of shellfish,fish,and bird resources
(Drover et at., 1993;Macko, 1998).
3.2.2 Millingstone Period (8,000 to 3,000 B.P.)
The Millingstone Period dates to about 8,000 to 3,000 B.P. The transition from the Early Period
to the Millingstone Period is marked by an increased emphasis on the processing of seeds and
edible plants.The increased utilization of seeds is evident by the high frequencies of handstones
(mans)and milling slabs(natures).Around 5,000 B.P.,mortar and pestles appear in the
archaeological record. Mortars and pestles suggest the exploitation of acoms(Vellanoweth and
Altschul,2002).
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Millingstone Period sites in Orange County generally date to between 8,000 and 4,000 B.P.
Archaeological evidence suggests a low,stable population centered around semi-permanent
residential bases. These sites me located along coastal marine terraces,near the shoreline,bays,or
estuaries. Satellite camps were used to take advantage of seasonally available resources.Marine
resources were supplemented by seeds and small terrestrial mammals.Later Millingstone Period
sites indicate a growing reliance on shellfish(Cleland et al., 2007).
3.2.3 Intermediate Period (3,000 to 1,500 B.P.)
The Intermediate Period dates to between 3,000 to 1,500 B.P. Archaeological sites indicate a
broader economic base,with increased reliance on hunting and marine resources.An expanded
inventory of milling equipment is found at sites dated to this period. Intermediate Period sites are
characterized by the rise of the mortar and pestle and small projectile points(Cleland et al.,
2007).
The number of Intermediate Period sites in Orange County declined over time,particularly
around Newport Bay.Climate changes and drier conditions led to the congregation of populations
near freshwater sources. Settlement patterns indicate greater sedentism,with reduced exploitation
of seasonal resources and a lack of satellite camps.Coastal terrace sites are not reoccupied during
this time period. These shifts in settlement and subsistence strategies led to growing population
densities,resource intensification,higher reliance on labor-intensive technologies, such as the
circular fishhook,and more abundant and diverse hunting equipment. Rises in disease and inter-
personal violence,visible in the archaeological record,may be due to the increased population
densities(Cleland et al.,2007;Raab et al., 1995).
3.2.4 Late Prehistoric Period (1,500 B.P. to A.D. 1769)
The Late Prehistoric Period began around 1,500 B.P. and lasted until Spanish contact in 1769.
The Late Prehistoric Period resulted in concentration of larger populations in settlements and
communities,greater utilization of the available food resources,and the development of regional
subcultures(Cleland et al.,2007). Artifacts from this period include milling implements,as well
as bone and shell tools and ornaments.
Newport Bay and San Joaquin Hills,abandoned during the Intermediate Period,were reoccupied
during the Late Prehistoric Period.These settlements were smaller than in the Intermediate.
Village sites were located in areas with a multitude of resources. Small collector groups moved
between a small number of these permanent settlements(Cleland et al.,2007).
3.3 Ethnographic Setting
The project is located at the southern extent of Gabrielino-Tongva territory,near the boundary
with the Jumeno,or more properly Acjachemen,to the south. Traditionally,the boundary
between the two is identified as either Aliso Creek or the drainage divide to the north of the
creek,roughly 20 miles south of the project APE,respectively.Both are included here.
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3. Seaing
3.3.1 Gabriel ino-Tongva
Prior to European colonization,the Gabrielino-Tongva,a Takic-speaking group,occupied a
diverse area that included:the watersheds of the Los Angeles, San Gabriel,and Santa Ana rivers;
the Los Angeles basin; and the islands of San Clemente,San Nicolas, and Santa Catalina
(Kroeber, 1925). The Gabrielino-Tongva are reported to have been second only to the Chumash
in terms of population size and regional influence(Bean and Smith, 1978).
The Gabrielino-Tongva were hunter-gatherers and lived in permanent communities located near
the presence of a stable food supply. Community populations generally ranged from 50-100
inhabitants,although larger settlements may have existed. The Gabrielino-Tongva are estimated
to have had a population numbering around 5,000 in the pre-contact period,with many recorded
villages along the drainages mentioned above and in the Los Angeles basin proper(Kroeber,
1925).
Beginning with the Spanish Period and the establishment of Mission San Gabriel Arcangel,
Native Americans throughout the Los Angeles area suffered severe depopulation and their
traditional culture was radically altered.Nonetheless, Gabrielino-Tongva descendants still reside
in the greater Los Angeles and Orange County areas and maintain an active interest in their
heritage.
3.3.2 Juaneno-Acjachemen
The Juaneno or Acjachemen, also Takic-speaking,occupied a more restricted area extending
across southern Orange County and northern San Diego County. Juaneno territory extended along
the Pacific coast from midway between Arroyo San Onofre and Las Pulgas Canyon in the south
to Aliso Creek in the north,and continued east into the Santa Ana Mountains from Santiago Peak
in the northwest to the headwaters of Arroyo San Mateo in the southeast(Kroeber 1925). The
Juaneno were bounded by the Gabrielino-Tongva to the north,and the Luiseno to the east and
south.
The Juaneno-Acjachemen,like the Gabrielino-Tongva,subsisted on small game, coastal marine
resources, and a wide variety of plant foods such as gross seeds and acorns. Their houses were
conical thatched reed,brush,or bark structures. The Juaneno inhabited permanent villages
centered around patrilineal clans,with each village headed by a chief,known as a nu(Kroeber
1925; Sparkman 1908). Seasonal camps associated with villages were also used.Each village or
clan had an associated territory and hunting,collecting, and fishing areas.Villages were typically
located in proximity to a food or water source,or in defensive locations,often near valley
bottoms,streams,sheltered coves or canyons,or coastal strands(Bean and Shipek 1978).
The Juaneno-Acllachemen population was estimated to have numbered approximately 1,000 at the
time of European contact.Beginning with the Spanish Period and the establishment of Mission
San Juan Capistrano,the Juaneno-Acjachemen suffered severe depopulation and their traditional
culture was radically altered.Nonetheless,descendants still reside in the Orange County area and
maintain an active interest in their heritage.
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3. Salting
3.4 Historic Setting
The historic setting for the project is divided into three primary periods: the Spanish Period
(A.D. 1769-1821), the Mexican Period(A.D. 1821-1846), and the American Period(A.D. 1846 to
present).
3.4.1 Spanish Period (A.D. 1769-1821)
The first European exploration of Orange County began in 1769 when the Gaspar de Portola
expedition passed through on its way from Mexico to Monterey. A permanent Spanish presence
was established with the founding of Mission San Juan Capistrano in 1776(Hoover et al.,2002).
The mission was founded to break the long journey from Mission San Diego to Mission San
Gabriel(near Los Angeles).A large,ornate church was constructed at the mission from 1797 to
1806,but was destroyed only six years later in an earthquake.The church was not rebuilt.
In an effort to promote Spanish settlement of Alta California,Spain granted several large land
concessions from 1784 to 1821.At this time, Spain retained title to the land; individual ownership
of lands in Alta California was not granted.The parts of Orange County that would become the
City of Huntington Beach and the City of Fountain Valley began as a Spanish land concession,
known as Rancho Los Nietos.A grant of 300,000 acres was given to Manuel Nieto in 1784 in
consideration of his military service(City of Huntington Beach,2000;Logan, 1990).
3.4.2 Mexican Period (A.D. 1821-1846)
In 1821,Mexico won its independence from Spain.Mexico continued to promote settlement of
California with the issuance of land grants.In 1833,Mexico secularized the missions,reclaiming
the majority of mission lands and redistributing them as land grants. During this time,Rancho
Los Nietos was divided into five smaller ranchos. The area of Huntington Beach became part of
Rancho Las Bolsas,a 33,460-acre rancho granted to Maria Catarina Ruiz in 1834(County of
Orange,20I1).Maria was the widow of Jose Antonio Nieto,Manuel Nieto's son.
Many ranchos continued to be used for cattle grazing by settlers during the Mexican Period.
Hides and tallow from cattle became a major export for Califomios(Hispanic Californians),
many of whom became wealthy and prominent members of society. These Califomios led
generally easy lives,leaving the hard work to vaqueros(Hispanic cowhands)and Indian laborers.
Californios lives centered primarily around enjoying the fruits of their labors,throwing parties
and feasting on Catholic holidays(Pitt, 1994; Starr,2007).
3.4.3 American Period (A.D. 1846 to present)
Mexico ceded California to the United States as part of the Treaty of Guadalupe Hildalgo,which
ended the Mexican-American War(1846-1848). The treaty also recognized right of Mexican
citizens to retain ownership of land granted to them by Spanish or Mexican authorities.However,
the claimant was required to prove their right to the land before a patent was given. The process
was lengthy and costly, and generally resulted in the claimant losing at least a portion of their
land to attorney's fees and other costs associated with proving ownership(Starr,2007).
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The Gold Rush(1849-I855)saw the first big influx of American settlers to California.Most of
these settlers were men hoping to strike it rich in the gold fields.The increasing population
provided an additional outlet for Califomios' cattle(Bancroft, 1890).As demand increased,the
price of beef skyrocketed and Califomios reaped the benefits.
The culmination of the Gold Rush,followed by devastating floods in 1861 and 1862 and droughts
in 1863 and 1864,led to the rapid decline of the cattle industry (Bancroft, 1890).Many
Califomios lost their lands during this period, and former ranchos were subsequently divided and
sold for agriculture and residential settlement.
Following the admission of California into the United States in 1850,the region of modem day
Orange County was originally part of Los Angeles County.Orange County was established in
1889,with the City of Santa Ana as County Seat(Armor, 1921).
3.4.4 History of the Project Vicinity
The project vicinity was once part of a 300,000-acre Spanish land grant,Rancho Los Metes,a
part of which became Rancho Las Balsas during the Mexican Period. Abel Stearns later acquired
the land for ranching and cultivation of barley. During the land boom of the 1880s,the area was
subdivided for agricultural and residential development(County of Orange,2011;Milkovich,
1986).
Previously called Shell Beach and later Pacific City,the town changed its time to Huntington
Beach in 1904 when Henry E.Huntington extended Pacific Electric Railway service to the little
community(Carlberg and Epting,2009;Mitcovich, 1986).Discovery of oil in the 1920s led to a
population explosion in the town. In one month,the population of Huntington Beach went from
1,500 to 6,000.
3.4.4.1 History of OCSD Plant No. 1 and No. 2 and OCWD GWRS
OCSD
In 1921,the cities of Santa Ana and Anaheim agreed to construct a sewer outfall extending into
the Pacific Ocean,thus forming the Orange County Joint Outfall Sewer(JOS),and marking the
beginning of the OCSD. In 1924,JOS construction was completed and the first sewage from
member cities was discharged into the system. Three years later,the outfall was extended to a
distance of 3,000 feet from shore,and a new screening plant and pumping station was
constructed. In 1941,the first units of the Primary Treatment Plant,now referred to as Plant
No. 1)were constructed. In 1954,OCSD assumed the duties of JOS and officially commenced
operations. Over the next 50 years, additional services and facilities were constructed at OCSD
Plant No. 1. The portion of the existing facility where the proposed OCSD pipe connection would
connect was constructed within the last 10 years.In 1954,Plant No.2 was constructed near the
ocean and adjoining Santa Ana River and the second ocean outfall was constructed. OCSD is
currently a public agency that provides wastewater collection,treatment,and disposal services for
approximately 2.5 million people in central and northwest Orange County. OCSD is a special
district that is governed by a Board of Directors consisting of 25 board members appointed from
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3. Selgng
21 cities,sanitary districts, and one representative from the Orange County Board of Supervisors.
OCSD has two operating facilities(Plants 1 and 2)that treat wastewater from residential,
commercial and industrial sources(ocsd.com).
OCWD GWRS
In the 1950s,traces of salt water were detected in the Orange County Groundwater Basin as far as
5 miles inland,although the area of intrusion was focused primarily across a 3-mile stretch
between the cities of Newport Beach and Huntington Beach.
In order to protect the basin from further seawater intrusion,the OCWD constructed the Water
Factory 21 (AT-21)in 1978. This facility treated wastewater utilizing a purification process
including RO,and injected it into 23 multi-casing injection wells along the Talbert Gap forming a
hydraulic barrier to seawater intrusion. (gwrsystem.com).
In 2004,WF-21 discontinued production and was demolished in February 2007 to provide space
for the construction of GWRS.GWRS provides new technology and is a larger water purification
plant compared to the previous WR-21. Construction of the GWRS broke ground in September
2004 and was completed in late 2007.The GWRS consists primarily of membrane processes,
replacing the physical-chemical processes of WF-21.Unlike WF-21,the GWRS utilizes MF as
pre-treatment prior to RO and UV light with hydrogen peroxide. The GWRS product water not
only supplies water to an expanded seawater barrier,but is also pumped to two of OCWD's
recharge basins where it blends with Santa Ana River and imported waters and naturally filters
into the groundwater basin,ultimately becoming part of north and central Orange County's
drinking water supply(gwrsystem.com).
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4. Regulatory Framework
4. Regulatory Framework
4.1 Federal
4.1.1 Section 106 of the National Historic Preservation Act
Archaeological resources we protected through the NHPA of 1966,as amended(54 United States
Code of Laws [USCI 300101 et seq.),and its implementing regulation,Protection of Historic
Properties(36 CFR Part 800),the Archaeological and Historic Preservation Act of 1974,and the
Archaeological Resources Protection Act of 1979. Prior to implementing an"undertaking"
(e.g.,issuing a federal permit),Section 106 of the NHPA requires federal agencies to consider the
effects of the undertaking on historic properties and to afford the Advisory Council on Historic
Preservation and the State Historic Preservation Officer(SHPO) a reasonable opportunity to
comment on any undertaking that would adversely affect properties eligible for listing in the
National Register of Historic Places(National Register).As indicated in Section 101(d)(6)(A)of
the NHPA,properties of traditional religious and cultural importance to a tribe me eligible for
inclusion in the National Register.Under the NHPA, a resource is considered significant if it
meets the National Register listing criteria at 36 CFR 60.4.
4.1.2 National Register of Historic Places
The National Register was established by the NHPA of 1966,as"an authoritative guide to be
used by federal, State, and local governments,private groups and citizens to identify the Nation's
historic resources and to indicate what properties should be considered for protection from
destruction or impairment"(36 CFR 60.2). The National Register recognizes both historic-period
and prehistoric archaeological properties that are significant at the national, state,and local levels.
To be eligible for listing in the National Register,a resource must be significant in American
history,architecture, archaeology,engineering,or culture.Districts, sites,buildings, structures,
and objects of potential significance must meet one or more of the following four established
criteria(U.S.Department of the Interior,2002):
A. Are associated with events that have made a significant contribution to the broad patterns
of our history;
B. Are associated with the lives of persons significant in our past;
C. Embody the distinctive characteristics of a type,period, or method of construction or that
represent the work of a master,or that possess high artistic values,or that represent a
significant and distinguishable entity whose components may lack individual distinction; or,
D. Have yielded,or may be likely to yield,information important in prehistory or history.
Unless the property possesses exceptional significance,it must be at least 50 years old to be
eligible for National Register listing(U.S.Department of the Interior,2002). In addition to
meeting the criteria of significance, a property must have integrity.Integrity is defined as"the
ability of a property to convey its significance"(U.S.Department of the Interior,2002).The
National Register recognizes seven qualities that,in various combinations,defrte integrity.The
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4. Regulatory Framework
seven factors that define integrity are location,design, setting,materials,workmanship,feeling,
and association. To retain historic integrity a property most possess several,and usually most,of
these seven aspects. Thus,the retention of the specific aspects of integrity is paramount for a
property to convey its significance.
4.2 State
4.2.1 California Environmental Quality Act
CEQA is the principal statute governing environmental review of projects occurring in the state
and is codified at Public Resources Code(PRC) Section 21000 et seq. CEQA requires lead
agencies to determine if a proposed project would have a significant effect on the environment,
including significant effects on historical or unique archaeological resources.
Under CEQA(Section 21084.1), a project that may cause a substantial adverse change in the
significance of an historical resource is a project that may have a significant effect on the
environment.An archaeological resource may qualify as an"historical resource"under CEQA.
The CEQA Guidelines(Title 14 California Code of Regulations [CCR] Section 15064.5)
recognize that an historical resource includes: (1)a resource listed in,or determined to be eligible
by the State Historical Resources Commission,for listing in the California Register of Historical
Resources(California Register);(2)a resource included in a local register of historical resources,
as defined in PRC Section 5020.l(k)or identified as significant in a historical resource survey
meeting the requirements of PRC Section 5024.1(g);and(3)any object,building,structure, site,
area,place,record,or manuscript which a lead agency determines to be historically significant or
significant in the architectural,engineering,scientific,economic,agricultural,educational,social,
political, military,or cultural annals of California by the lead agency,provided the lead agency's
determination is supported by substantial evidence in light of the whole record. The fact that a
resource does not meet the three criteria outlined above does not preclude the lead agency from
determining that the resource may be an historical resource as defined in PRC Sections 5020.10)
or 5024.1.
If a lead agency determines that an archaeological site is a historical resource,the provisions of
Section 21084.1 of CEQA and Section 15064.5 of the CEQA Guidelines apply. If a project may
cause a substantial adverse change(defined as physical demolition,destruction,relocation,or
alteration of the resource or its immediate surroundings such that the significance of an historical
resource would be materially impaired)in the significance of an historical resource,the lead
agency must identify potentially feasible measures to mitigate these effects(CEQA Guidelines
Sections 15064.5(b)(1), 15064.5(b)(4)).
If an archaeological site does not meet the criteria for a historical resource contained in the CEQA
Guidelines,then the site may be treated in accordance with the provisions of Section 21083,
which is as a unique archaeological resource.As defined in Section 21083.2 of CEQA a"unique"
archaeological resource is an archaeological artifact,object,or site,about which it can be clearly
demonstrated that without merely adding to the current body of knowledge,there is a high
probability that it meets any of the following criteria:
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• Contains information needed to answer important scientific research questions and there
is a demonstrable public interest in that information;
• Has a special and particular quality such as being the oldest of its type or the best
available example of its type;or,
• Is directly associated with a scientifically recognized important prehistoric or historic
event or person.
If an archaeological site meets the criteria for a unique archaeological resource as defined in
Section 21083.2,then the site is to be treated in accordance with the provisions of Section
21083.2,which state that if the lead agency determines that a project would have a significant
effect on unique archaeological resources,the lead agency may require reasonable efforts be
made to permit any or all of these resources to be preserved in place(Section 21083.Ila)). If
preservation in place is not feasible,mitigation measures shall be required.
The CEQA Guidelines note that if an archaeological resource is neither a unique archaeological
nor a historical resource,the effects of the project on those resources shall not be considered a
significant effect on the environment(CEQA Guidelines Section 15064.5(c)(4)).
4.2.2 CEQA-Plus
The EPA sponsors the SRF Loan Program to provide funding for construction of publicly-owned
treatment facilities and water reclamation projects. This funding for capital improvements to
wastewater treatment and water recycling facilities is authorized under the federal Clean Water
Act. In order to comply with requirements of the SRF Loan Program,which is administered by
the SWRCB in California,a CEQA document must fulfill additional requirements(mown as
CEQA-Plus. The CEQA-Plus requirements have been established by the EPA and are intended to
supplement the CEQA Guidelines with specific requirements for environmental documents
acceptable to the SWRCB when reviewing applications for wastewater treatment facility loans.
They me not intended to supersede or replace CEQA Guidelines. The EPA's CEQA-Plus
requirements have been incorporated into the SWRCB's Environmental Review Process
Guidelines for SRFLoan Applicants(2004).The SWRCB's SRF Guidelines require that a
proposed project comply with Section 106 of the NHPA.
4.2.3 California Register of Historical Resources
The California Register is"an authoritative listing and guide to be used by State and local
agencies,private groups,and citizens in identifying the existing historical resources of the State
and to indicate which resources deserve to be protected,to the extent prudent and feasible,from
Register are based upon National Register criteria(PRC Section 5024.1[b]). Certain resources are
determined by the statute to be automatically included in the California Register,including
California properties formally determined eligible for,or listed in,the National Register.
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To be eligible For the California Register,a prehistoric or historic-period property must be
significant at the local,state, and/or federal level under one or more of the following four criteria:
1. Is associated with events that have made a significant contribution to the broad patterns
of California's history and cultural heritage;
2. Is associated with the lives of persons important in our past;
3. Embodies the distinctive characteristics of a type,period,region,or method of
construction,or represents the work of an important creative individual,or possesses high
artistic values;or
4. Has yielded,or may be likely to yield,information important in prehistory or history.
A resource eligible for the California Register must meet one of the criteria of significance
described above, and retain enough of its historic character or appearance(integrity)to be
recognizable as a historical resource and to convey the reason for its significance.It is possible
that a historic resource may not retain sufficient integrity to meet the criteria for listing in the
National Register,but it may still be eligible for listing in the California Register.
Additionally,the California Register consists of resources that are listed automatically and those
that must be nominated through an application and public hearing process.The California
Register automatically includes the following:
• California properties listed on the National Register and those formally determined
• eligible for the National Register;
• California Registered Historical Landmarks from No. 770 onward; and,
• Those California Points of Historical Interest that have been evaluated by the OHP and
have been recommended to the State Historical Commission for inclusion on the
California Register.
Other resources that may be nominated to the California Register include:
• Historical resources with a significance rating of Category 3 through 5 (those properties
identified as eligible for listing in the National Register,the California Register,and/or a
local jurisdiction register);
• Individual historical resources;
• Historical resources contributing to historic districts;and,
• Historical resources designated or listed as local landmarks,or designated under any local
ordinance, such as a historic preservation overlay zone.
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4.2.4 California Health and Safety Code Section 7050.5
California Health and Safety Code Section 7050.5 requires that in the event human remains are
discovered,the County Coroner be contacted to determine the nature of the remains. In the event
the remains are determined to be Native American in origin,the Coroner is required to contact the
California Native American Heritage Commission(NAHC)within 24 hours to relinquish
jurisdiction.
4.2.5 California Public Resources Code Section 5097.98
California PRC Section 5097.98,as amended by Assembly Bill 2641,provides procedures in the
event human remains of Native American origin are discovered during project implementation.
PRC Section 5097.98 requires that no further disturbances occur in the immediate vicinity of the
discovery,that the discovery is adequately protected according to generally accepted cultural and
archaeological standards,and that further activities take into account the possibility of multiple
burials.PRC Section 5097.98 further requires the NAHC,upon notification by a County Coroner,
designate and notify a Most Likely Descendant(MLD)regarding the discovery of Native
American human remains. Once the MLD has been granted access to the site by the landowner
and inspected the discovery,the MLD then has 48 hours to provide recommendations to the
landowner for the treatment of the human remains and any associated grave goods.
In the event that no descendant is identified,or the descendant fails to make a recommendation
for disposition,or if the land owner rejects the recommendation of the descendant,the landowner
may,with appropriate dignity,reinter the remains and burial items on the property in a location
that will not be subject to further disturbance.
4.2.6 California Public Resources Code Section 21080.3.1
California PRC Section 21080.3.1, as amended by Assembly Bill (AB) 52,requires lead agencies
to consider the effects of projects on tribal cultural resources and to conduct consultation with
federally and non-federally recognized Native American Tribes early in the environmental
planning process and applies specifically to projects for which a Notice of Preparation(NOP)or a
notice of Negative Declaration or Mitigated Negative Declaration(MND)will be filed on or after
July 1,2015.The goal is to include California Tribes in determining whether a project may result
in a significant impact to tribal cultural resources that may be undocumented or known only to the
Tribe and its members and specifies that a project that may cause a substantial adverse change in
the significance of a tribal cultural resource is a project that may have a significant effect on the
environment. Tribal cultural resources are defined as"sites,features,places,cultural landscapes,
sacred places, and objects with cultural value to a California Native American Tribe"that are
either included or determined to be eligible for inclusion in the California Register or included in
a local register of historical resources(PRC Section 21074(a)(1)).
Prior to determining whether a Negative Declaration,MND,or Environmental Impact Report
(EIR)is prepared for a project,the lead agency must consult with California Native American
Tribes, defined as those identified on the contact list maintained by the California Native
American Heritage Commission(NAHC),who are traditionally and culturally affiliated with the
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geographic area of the proposed project, and who have requested such consultation in writing.
Consultation may include:
• The type of environmental review necessary
• The significance of tribal cultural resources
• The significance of the project's impacts on the tribal cultural resources
• Project alternatives or the appropriate measures for preservation
• Recommended mitigation measures
Consultation should be initiated by a lead agency within 14 days of determining that an
application for a project is complete or that a decision by a public agency to undertake a project
(PRC Section 21080.3.1(d)and(e)). The lead agency shall provide formal notification to the
designated contact of,or a tribal representative of,traditionally and culturally affiliated California
Native American Tribes that have requested notice. At minimum,notice should consist of at least
one written notification that includes a brief description of the proposed project and its location,
the lead agency contact information,and a notification that the California Native American Tribe
has 30 days to request consultation pursuant to this section. The lead agency shall begin the
consultation process within 30 days of receiving a California Native American Tribe's request for
consultation.According to PRC Section 21080.3.2(b),consultation is considered concluded when
either the parties agree to measures to mitigate or avoid a significant effect, if a significant effect
exists,on a tribal cultural resource,or a party,acting in good faith and after reasonable effort,
concludes that mutual agreement cannot be reached.
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5. Archival Research
5.1 South Central Coastal Information Center Records Search
A records search for the APE and a 1/,mile radius was conducted on June 21,2016 at the South
Central Coastal Information Center(SCCIC),located at California State University,Fullerton.
The records search included a review of all recorded cultural resources within a %-mile radius of
the project APE, as well as a review of cultural resource reports on file.The Historic Properties
Directory was also examined for any documented historic-period built resources within or
adjacent to the project APE. The results of the SCCIC records search are included in
Appendix B.
5.1.1 Previous Cultural Resources Investigations
A total of 61 cultural resources studies have been conducted within a%-mile radius of the project
APE.Of the 61 previous studies, five studies included a pedestrian survey of portions of the APE,
and four included archival research for the APE(Table 1).A complete list of the 61 studies
located within Y/-mile of the project APE is located in Appendix B.Less than 50 percent of the
project APE has been included in previous cultural resources surveys.
TABLE 1
PREVIOUS CULTURAL RESOURCES INVESTIGATIONS INCLUDING THE PROJECT APE
SCIC#
Author (OR-) Title Year
Mason,Roger D.Ph.D., 36070 Cultural Resources Survey Report for the Le Said Park Edension 2005
RPA Prated,Huntington Beach, Orange County,California
Padon,Beth 18360 Cultural Resources Review for Groundwater Replenishment System 1998
Program EIR?er 110S, Orange County Water Dishlct and County
Sanitation Districts of Orange County
POD Consultants,Inc. 4087- Final Program EIR for the Groundwater Replenishment System 1999
Historic Resource 4256� The Cultural Resources Study of the SCE—Monica Pacific Nursery 2012
Associates protect Metropcs California,LLC Site no.MLAX04188,20462
Raisenwood Lane,Huntington Beach, Orange County, California 92646
Ewa Management 801❑ Phase II Archaeological Studies Plado Basin and the Lower Santa Ana 1985
Criteria,Inc River
Michael Brendman 3682 Direct APE Historic Architectural Assessment for Royal Street 2007
Associates Communications,LLC Candidate LA2812A(SCE tabard Park),SCE
Tower M2 T5 EIIiVHB Number 2 South of Rayenwood,Huntington
Beach,Orange County, California
Mason,Roger D. 2033o Research Design for Evaluation of Coastal Archaeological Sites In 1987
northern Orange County, California
Statistical Research,Inc 4259D Cultural Resources Monitodng Report, Orenge County Water District 2007
Groundwater Replenishment System,Orange County, Callfonda
Leonard,III,N.Nelson 2700 Description and Evaluation of Cultural Resources within the U.S.Army 1975
Corps
Unknown 43130 The City of Huntington Beach General Plan 2013
City of Huntington Beach
nlndicdes study o-adaps the Archaeological APE
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5.1.2 Previously Recorded Cultural Resources
The records search indicated that nine cultural resources have been previously recorded within a
9/,mile radius of the project APE(Table 2).No cultural resources have been previously recorded
within the project APE.However,two historic-age Souther California Edison(SCE)
transmission towers(30-177464 and 30-177612)are located adjacent to the pipeline alignment.
Several prehistoric sites have been recorded within the search radius along the east bluffs of the
Santa Ana River.
TABLE 2
PREVIOUSLY RECORDED CULTURAL RESOURCES WITHIN%-MILE OF THE PROJECT APE
Primary Trinomial(CA- Date
p(P30) ORA-) Other Designation Description Recorded
000058 CA[DRAf58 ORG3 Prehistoric Habitation Site 2003;
1975;and
1949
000076 CA[DRA176 ORES Prehistoric Habitation Site with shell 1949
midden
000163 CADDRAE163 Grand Site Prehistoric archaeological site consisting 1966
of shell ridden with associated firepits,
burials,stone tools,pottery,and
charmstones
000165 CADDRAE165 Banning Erect,Potion A Prehistoric archaeological she consisting 1960
of stone bowl fragments,lithic fragments,
and pastels
000576 CAMRA576 ❑ Prehistoric feature consisting of a single 1974
human burial
000645 CADDRAT145 ACEESARIS Prehistoric archaeological site consisting 1998;
of a single shell midden 1979
000906 CAUDRA306 ❑ Prehistoric archaeological she consisting 1998;
of a single shell midden 1979
001740 CAUDRA❑ SRS1759EI Two historiclperiod trash scatters 2014
1740H
177464 L SCE Transmission Tower M20 Historicltherlod steel transmission tower 2012
T6,Ellis Huntington Beach
No.2
177467 L William Lamb Elementary HisuricEperiod architectural resource 2013
School consisting of an Educational Building
177612 L SCE Transmission Tower M20 Historic1therlod steel transmission tower 2007
T5,Ellis Huntington Beach
No.2
5.1.2.1 Resource 30-177464
SCE Transmission Tower M2-T6(30-177464),consists of one of a pair of SCE high-lead
electrical transmission towers that rum general north-south tying into the SCE power plant located
along the Pacific Coast Highway(PCH)neat Brookhurst Street.The riveted steel,truncated pair
of towers were built in 1964 and each stand approximately 121 feet tall,resting on concrete piers,
and having three arms with porcelain insulators conducting electricity along wires affixed to each
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arm. The tower parallels the Santa Ana River flood control channel immediately to the east. This
resource was previously evaluated for its historical significance.While the tower appeared to
retain very good integrity of design,materials, location,setting, association,and feeling,this
resource was Found to be a ubiquitous property type constructed in 1964 to provide additional
electrical power to the expanding suburban communities of west Orange County,including
Huntington Beach.This resource was not associated with any significant events(Criterion A),nor
did it appear to embody distinctive construction techniques or represent the work of a master
(Criterion C),and it was recommended not eligible for listing in the National Register
(Supemowicz,2012).
5.1.Z2 Resource 30-177612
SCE Transmission Tower M2-T5 (30-177612)consists of a steel lattice type, 122-foot tall
transmission tower. The base of the tower measures 30 feet on each side.The footings are
rectangular shaped concrete bases.The transmission tower was constructed with bolted steel L-
shaped profiles.The tower was installed by SCE as part of its expansion of electrical service in
the Huntington Beach area. The center of the tower base contains a square,concrete block
building.The building has a hipped roof with Spanish tile.The transmission tower was
constructed as part of the overall development of electrical power in Southern California in the
1940s in the post-World War II period. This resource was previously evaluated for its historical
significance. While the tower appeared to retain integrity of design,materials,location, setting,
association,feeling,and workmanship,the tower was not associated with any significant events
or persons(Criterion A and B),it did not represent distinctive construction techniques or the work
of a master(Criterion C),and it was not the principal source of information about this property
type and did not have the potential to yield information important in prehistory or history
(Criterion D).Thus it was recommended not eligible for the National Register(Crawford,2007).
It has not been previously evaluated for listing in the California Register.
5.2 Historic Map and Aerial Review
Historic maps and aerial photographs were examined in order to provide historical information
about the APE and to contribute to an assessment of the APE's archaeological sensitivity.
Available maps include: the 1868 U.S. Surveyor General's survey plat map of Townships 5 and 6
South, Range 10 West the 1895 and 1901 Santa Ana 1:62,500 topographic quadrangles; the 1902
Corona 1:125,000 topographic quadrangle; and the 1935 Newport Beach 1:31,600 topographic
quadrangles; and 1965 and 1975 Newport Beach 7.5-minute topographic quadrangle.Historic
aerial photographs of the APE from 1938, 1953, 1963, 1972, 1994,2002,2003,2004,2005,
2009,and 2010 were also examined(historicaerials.com,2016).
The 1868 U.S. Surveyor General's survey plat map shows the APE as being located within
Rancho Las Bolsas. The plat map indicates salt marshes within the current location of OCSD
Plant No. 2. The available historic maps and aerial photographs indicate that the APE and
surrounding area was largely used for agricultural purposes throughout the 20th century,and did
not become urbanized until the latter half of the century.The Santa Ana River is shown confined
with artificial levees in the 1938 historic aerial photograph. The OCSD Plant No. 1 is visible on
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the 1953 aerial photograph.The southern portion of OCSD Plant No. 1 was undeveloped until
The OCWD GWRS and OCSD Plant No. 2 are not shown on the 1953 aerial. The OCSD Plant
No. 2 facility is shown on the 1965 Newport Beach 7.5-minute topographic quadrangle. The
OCWD GWRS facility is shown on the 1972 7.5-minute topographic quadrangle.Based on a
detailed review of the 1972 and 2016 aerials of the OCSD Plant No.2,there are structures shown
on the 1972 aerial that remain visible on the 2016 aerial photograph.
5.3 Native American Heritage Commission
In 2014,the project environmental documentation, including a cultural resources study,was
initiated,and it was put on hold shortly after.However,Native American outreach was
completed.The Native American outreach was restarted as part of the project and new project
features.The results of previous Native American outreach and current outreach are presented
below. Documentation related to Native American outreach is provided in Appendix C.
5.3.1 Native American Outreach —2014
On August 13,2014,a records search request letter was sent to the NAHC in an effort to
determine whether any sacred sites are listed on its Sacred Lands File(SLF)for the project APE.
A response was provided on August 22,2014 that indicated that no Native American cultural
resources were identified within a''/rmile radius of the project APE.The NAHC recommended
outreach to nine specific tribal authorities who may want to comment on the search request. A
letter to the NAHC-listed tribal authorities was mailed on August 26,2014. Phone calls were
made to each of the named tribal members on September 9,2014 and again on September 18,
2014. Fora Tribal representatives responded and provided input(Table 3).
5.3.2 Native American Outreach — 2016
On June 2,2016,a SLF search request letter was sent to the NAHC in an effort to determine
whether any sacred sites are listed on SLF for the APE.A response was provided on June 6,2016
indicating negative results for Native American cultural resources within the project APE.The
NAHC recommended outreach to 12 specific tribal authorities who may want to comment on our
search request.A letter to the NAHC-listed tribal authorities was mailed on June 20,2016. Phone
calls were made to each of the named tribal members on June 28,2016. Two Tribal
representatives responded and provided input(see Table 3).
5.3.3 AB 52
In August 2016, OCWD sent letters to two Native American representatives who have requested
to be informed on activities conducted by the OCWD,under PRC Section 21080.3.1. The OCWD
reached out to the Juaneno Band of Mission Indians Acjachemen Nation and Gabrichim Band of
Mission Indians—Kizh Nation. Consultation efforts are currently on-going.
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TABLE 3
NATIVE AMERICAN OUTREACH
Dale of Follow-up
Contact Tribe/Organization Date Letter Mailed Phone Call Response
2014
ohn Tommy Roses Tong.a Acenstral Territorial Tribal 8/27/2014 9/9/2014 mhn Tommy Roses was concerned about project
Nation because It Is located within a sensiti a archaeological
area.He recommended testing prior to exca[ation or
full time archaeological and Nati a American
monitoring.
Anthony Morales Gabnelenoi San Gabriel 8/28/2014 9/9/2014 Anthony Morales was concerned about the project
Band of Mission because of its location along the Santa Ana RiCar.He
suggested archaeological and paleontological
monitoring.
Sandonne Goad Gabrielino/rol Nation 8/29/2014 9/9/2014 Referred to Sam Dunlap
Robert F Domme Gatr ino Tong®Indians of 8/30/2014 9/9/2014 No Response
California Tribal Council
Gabrielino Tong®Indians of 8/31/2014 9/18/2014 No Response
California Tribal Council
Bernie Acuna Gabnelino.Tong aTribe 9/1/2014 9/10/2014 No Response
Linda Candelaria Gabneleno Band of Mission Indians 9/Z2014 9/9/2014 No Response
Andrew Sales GabnelinoJoni Tribe 9/W2014 9/10/2014 Mr.Sales expressed concerned about the project due
to its location in an archaeological sensiti a area.Mr.
Salas suggested archaeological and Nell a American
monitoring take place to protect and preseris any
cultural resources that may be discoC red during
exca anions.
Conrad Acura Gabnelino/rorri Nation 9/4/2014 N/A No number or email proDded.
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Date of Follow-up
Contact Tribe/Organization Date Letter Mailed Phone Call Response
Sam Dunlap GabnelinorrongDe Nation 9/5/2014 9/10/2014 In an email dated September 11,2014,Mr.Dunlap
expressed concems about construction and
recommended archaeological and Nat i a American
monitoring.
2016
Malias Balances uaneno Band of Mission Indians, 6/20/2016 6/28/2016 See response from[oyes Stanfield[Perry
Acjachemen Nation
Adolph Sepul ads uaneno Band of Mission Indians 6/20/2016 6/28/2016 A 331cemall was left;No response to date
Anthony Morales Gabrieleno/TongCa Band of Mission 6/20/2016 6/28/2016 Mr.Morales recommended NaUDo American and
Indians archaeological monitoring due to the cultural and
spiritual sensltilLy of the area
Sonia Duhnston Duaneno Band of Mission Indians 6/20/2016 6/28/2016 An email was sent on Dune 20,2016.No response to
date
Sandonne Goad Gabnelino/rong®Nation 6/20/2016 6/28/2016 See response from Sam Dunlap
Bernie Aeons GabnelinoQonga Tribe 6/20/2016 6/28/2016 A deem l was left;No response to date
Teresa Romero Duaneno Band of Mission Indians, 6/20/2016 6/28/2016 A�cicemail was left;No response to date
Acjachemen Nation
myce StanfieldElPemy Duaneno Band of Mission Indians, 6/20/2016 6/28/2016 Ms.StanfieldMerry recommended Natl�American and
Acjachemen Nation archaeological monitoring during all ground disturbing
acti ities and in the e0ant of a disco�ry,that the
project be stopped and the mitigation plan be re-
e[aluated.
Robert Dorame Gabnelino Tong a Indians of 6/20/2016 6/28/2016 Mr.Doreme re uested an emailed Dersion of the letter;
California Tribal Council No response to date
Linda Candelaria Gail Tong a Tribe 6/20/2016 6/28/2016 A Coicemail was left;No response to date
Sam Dunlap Gabnelinl Nation 6/20/2016 6/28/2016 Mr.Dunlap reWested a PDF copy of the letter be
smelled.The PDF copy was smelled on Dune 20,2016.
No response to date
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Date of Follow-up
Contact Tribe/Organization Date Letter Mailed Phone Call Response
Andy Sales Gabnelino Band of Mission Indianso 6/20/2016 6/28/2016 Mr.Salas recommended Nati]b American and
Ki h Nation archaeological monitoring during all ground disturbing
acti0des
Conrad Acura GabnelinoQongs Tribe 6/20/2016 N/A No contact information was listed on the NAHC contact
list
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5.4 Geoarchaeological Review
Chris Lockwood, Ph.D.,R.P.A.,conducted a desktop geoarchaeological review of the project
APE and vicinity in order to evaluate the potential for buried archaeological resources within the
APE.The following section presents the results of Dr.Lockwood's analysis.
5.4.1 Geology and Geomorphology
The APE is located in Fountain Valley and Huntington Beach on the Santa Ana coastal plain in
Orange County,California. It is immediately west of a stretch of the Santa Ana River that is
confined to a flood control channel.
5.4.1.1 OCSD Plant No. 1
The portion of the APE at OCSD Plant No. 1 is situated on a landform dominated by a low-
gradient, sandy alluvial fan that merges with marine deposits at the coast. During the late
Pleistocene, sea-level was approximately 120 meters below present level,leaving the vicinity of
the APE approximately 9.3 miles(15.0 km)inland. Sea level rose throughout the Holocene,
attaining near present conditions by approximately 2,000 to 4,000 years ago.Near surface
deposits within the portion of the APE where new piping would be installed between OCSD Plant
No. 1 and the existing pipeline are mapped as late Holocene to latest Pleistocene alluvial fan
deposits(Morton 2004;Morton and Miller 2006),and consist of gravel, sand,and silt transported
and deposited by the Santa Ana River. The APE is covered by a paved surface that likely is
underlain by fill and required grading prior to construction.
5.4.1.2 OCWD GWRS Facility
The portion of the APE at OCWD GWRS Facility APE is on the same landform as the portion of
the APE at OCSD Plant No. 1 and therefore shares similar geomorphological characteristics. The
OCWD GWRS Facility APE has been previously developed.
5.4.1.3 OCSD Plant No. 2
The portion of the APE at OCSD Plant No. 2 is on the distal portion of the alluvial fan that also
contains the portion of the APE at the OCSD Plant No. 1 and the portion of the APE at the
OCWD GWRS Facility. During the late Pleistocene,the portion of the APE at OCSD Plant No. 2
was approximately 5.5 miles(9.0 km)inland.Historically,the APE consisted largely of salt
marsh,which would have been at or just above sea level,and was divided by small channels. The
area was for celery agriculture in historic times.
The OCSD Plant No.2 was initially developed for sanitation in 1954,but the parcel,including
the APE,was progressively developed towards the north over the next five decades.The APE is
covered with a paved surface that is at elevation 34 meters above mean sea level(amsl),
suggesting the APE contains several meters of fill overlying the native salt marsh deposits. Some
of the fill material may have originated as dredge spoils from channelization of the Santa Ana
River.Near surface geology the APE is mapped as late Holocene to latest Pleistocene alluvial fan
deposits(Morton 2004;Morton and Miller 2006). These deposits consist of gravel,sand, and silt
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transported and deposited by the Santa Ana River.To the south of the APE,the OCSD Plant No.
2 site contains unconsolidated eolian dune deposits.
5.4.2 Soils
5.4.2.1 OCSD Plant No. 1
Soils within the portion of the APE at OCSD Plant No. 1 are mapped as Metz loamy sand(MRCS
2016).The Metz soil series consists of very deep,somewhat excessively drained soils.Metz soils
are formed in alluvial parent material on floodplains and alluvial fans with slopes of 0 to 15
percent. Since Metz soils are commonly cultivated,the typical soil pedon possesses a shallow
plowzone A-horizon(Ap)overlying multiple layers of sandy loam to sand parent material(Cl,
C2,C3,C4 horizons).The absence of a B-horizon is likely due to the short geological time that
has passed since deposition of the last unit of parent material(Cl),although agricultural activity
has the potential to have partially disrupted B-horizon development. The sequence of several
units of parent material(C-horizon)reflects changes over time in the behavior of the Santa Ana
River,including periodic overbank flooding.Because the C-horizons represent vertical accretion
(i.e.,building)on the floodplain,there is a potential that successive fluvial deposits covered and
preserved archaeological resources that had accumulated between depositional events.Therefore,
Metz soils are considered to have a high sensitivity for buried archaeological resources.
5.4.2.2 OCWD GWRS Facility
Soils within the portion of the APE at the OCWD GWRS Facility are mapped as Hueneme fine
sandy loam(MRCS 2016).The Hueneme soils series are formed on alluvial fans in stratified
alluvium derived from sedimentary rock.The typical soil pedon consists of a plowed A-horizon
(Apl,Apt)developed at the top of relatively unaltered alluvial parent material(CI through C5)
extending more than 70 inches deep.The absence of a B-horizon is likely due to the short
geological time that has passed since deposition of parent material,although agricultural activity
has the potential to have disrupted the development of a recognizable B-horizon as well. The
sequence of several units of parent material(C-horizon)reflects changes over time in the
behavior of the Santa Ana River,including periodic overbank flooding.Because the C-horizons
represent vertical accretion(i.e.,building)on the floodplain,there is a potential that successive
fluvial deposits covered and preserved archaeological resources that had accumulated between
depositional events.Therefore,Hueneme soils are considered to have a high sensitivity for buried
archaeological resources.
5.4.2.3 OCSD Plant No. 2
Soils within the portion of the APE at OCSD Plant No. 2 are mapped primarily as Bolan silt loam
(NRCS 2016).Bolas series soils are deep,somewhat poorly drained soils developed in mixed
alluvium parent material on flood plains and basins.The typical soil pedon consists of a plowed
A-horizon(Apl,Ap2)developed at the top of relatively unaltered alluvial parent material(Cl
through C6)extending more than 69 inches deep.The absence of a B-horizon is likely due to the
short geological time that has passed since deposition of the parent material,although agricultural
activity has the potential to have disrupted the development of a recognizable B-horizon as well.
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The A-horizon in Balsa soils ranges from sandy loam to silty clay loam,while the C-horizon is
mainly silt loam and silty clay loam but may contain thin strata of sandier material(USDA 1997).
Significantly,many Balsa soil pedons contain buried A-horizons(paleosols). These buried A-
horizons represent periods of time in the past during which landform conditions were relatively
stable, and during which deposition and erosion were sufficiently balanced to allow for
development and retention of a soil weathering profile.From an archaeological perspective,
periods of landform stability,such as those signified by buried A-horizons,should be correlated
with the accumulation and preservation of cultural remains.Therefore,Bolsa soils are considered
to have a high sensitivity for buried archaeological resources.
5.4.3 Archaeological Potential
Although paved and filled,the portion of the APE at the OCSD Plant No.2 appears to retain high
sensitivity for buried archeological resources.During the latest Pleistocene and Holocene,the
geomorphic setting of the portion of the APE at the OCSD Plant No. 2 changed from inland to
coastal, and rising sea level resulted in fluvial deposition capable of burying archaeological
resources.The portion of the APE at the OCSD Plant No.2 was largely salt marsh into the early
20th century,but this is an area that would have offered important resources. Owing to its marshy
environment, this area may not have been favored for any substantial occupation,but nonetheless
is likely to have been visited for resource procurement and could contain artifacts associated with
those activities.Additionally,the saturated conditions offered within this setting may have aided
in the preservation of relatively rare organic artifacts.
Although paved and filled,the portion of the APE where new piping would be installed between
OCSD Plant No. 1 and the existing pipeline appears to retain high sensitivity for buried
archaeological resources.During the latest Pleistocene and Holocene rising sea levels reduced
fluvial downcutting and increased deposition capable of burying archaeological resources.
Historically,the APE was north of a large salt marsh, an area that would have offered important
resources. Owing to its proximity to both the salt marsh and the Santa Ana River,the APE may
have been selected for occupation,and could contain buried artifacts and features associated with
such use.
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6. Paleontological Records Search
Dr. Samuel A.McLeod,Ph.D.,of the Natural History Museum of Los Angeles County,
Vertebrate Paleontology Section,conducted a thorough search on June 16,2016 of the
paleontology collection records for the locality and specimen data for the proposed project.No
vertebrate fossil localities lie within the project APE;however,there are localities nearby from
the same sedimentary units that may occur subsurface in the project APE. The closest vertebrate
fossil locality from Quaternary Terrace deposits is LACM 7366.LACM 7366 produced
specimens of marine, freshwater,and terrestrial specimens including leopark shark, Triakis,
three-spined stickleback, Gasterosteus,garter snake, Thamnophis,desert shrew,Notiosorex,and
most prominently,pocket gopher, Thomomys.A series of fossil localities, LACM 7422-7425,are
located north-northwest of LACM 7366.These localities produced fossil specimens of mammoth,
Mammuthus,bison,Bison,and horse,Equus,from Alluvium or dune deposits. The closest
vertebrate fossil locality from Quaternary deposits is LACM 6370 located approximately 1.6
miles southeast. LACM 6370 produced a specimen of a fossil horse,Equus.Fossil locality
LACM 3267 located northeast,produced a specimen of a fossil elephant,Proboscidea in
Quaternary deposits. Fossil locality LACM 4219 produced fossil specimens of turtle,Chelonia,
and camel, Camelidae.Vertebrate fossil locality LACM 1339,located north of the APE,
produced fossil specimens of mammoth,Mammuthus,and camel, Camelidae,bones from sands
approximately 15 feet below the top of the mesa that is overlain by shell bearing silts and sands.
The entire APE has surface deposits of younger Quaternary Alluvium, derived as fluvial deposits
from the Santa Ana River to the east of the project APE. No fossil vertebrate localities are located
nearby these deposits,and they are unlikely to contain significant vertebrate fossils,at least in the
uppermost layers. Small hills and bluffs both east and west of the project APE,however,define
the Santa Ana River floodplain drainage and are mapped as having exposures of marine
Quaternary Terrace deposits. These or other older Quaternary deposits may occur in the project
APE at unknown depth.There is a low potential to uncover significant vertebrate fossil remains
during surface grading or shallow excavations in the APE.However,excavations that extend
down into the older Quaternary deposits may encounter significant fossil vertebrate specimens.
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7. GUXureI Resources Surly and Results
7. Cultural Resources Survey and Results
A cultural resources pedestrian survey of the APE was conducted on June 16,2016 by Arabesque
Said-Abdelwahed to identify the presence of surface archaeological materials.Intensive-level
survey was conducted of areas with greater surface visibility with intervals spaced at 10 meter.
Survey of the OCWD GWRS Facility showed that the entire project APE has been previously
developed and is completely paved.The buildings that exist on the OCWD site were constructed
after 1972.No cultural resources were observed during the survey at the OCWD GWRS Facility.
A pedestrian survey was conducted on June 16,2016 of the existing pipeline alignment for
rehabilitation is located along an OCSD easement corridor that extends west of the Santa Ana
River levee. The pipe would connect to existing facilities at the OCSD Plant No. 1 and proposed
facilities in OCSD Plant No. 2. The soils were previously disturbed during placement of the
existing pipeline located 5 feet below the existing ground surface. The corridor consists of fill
material and is elevated approximately 2-4-feet above natural grade(OCWD,pers. comm.).No
cultural resources were observed during the survey of the existing pipeline route.Cultural
resources were not observed during the survey of the pipe connection locations to existing
facilities.
New facilities(Flow Equalization Control/Meter,Flow Equalization Pump Station,OCSD
Pipeline Connection,pump station,bypass pipeline,and headgates)would be constructed at the
OCSD Plant No. 2. The bypass pipeline,headgates,Flow Equalization Control/Meter,and
proposed pump station locations are currently paved and natural ground was not visible. The
OCSD Plant No. 2 consists of existing tanks and waste water treatment buildings. Portions of the
proposed location for the Flow Equalization Pump Station and OCSD Pipeline Connection are
unpaved and were surveyed in regular intervals.No archaeological or historic built resources
were observed within the APE. Potential historic-period buildings/structures were noted at the
OCSD Plant No. 2 outside of the APE.
A photographic narrative of the survey results can be found in the attached Appendix D.
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B. conclusions and Recommendations
8. Conclusions and Recommendations
8.1 Archaeological Resources
As a result of this study,no archaeological resources were identified within the APE. However,
based on the results of study,the project APE should be considered highly sensitive for
subsurface archaeological resources.Native American respondents indicated sensitivity for
archaeological resources in the APE and surrounding area given the proximity to the Santa Ana
River corridor. In addition,the geoarchaeological review indicates that the portion of the APE
within OCSD Plant No. 2 was largely salt marsh into the early 20th century and would have
offered important resources.Owing to its marshy environment,this area may not have been
favored for any substantial occupation,but nonetheless is likely to have been visited for resource
procurement and could contain artifacts associated with those activities. Additionally,the
saturated conditions offered within this setting may have aided in the preservation of relatively
rare organic artifacts. Since the project includes ground-disturbing activities,there is a potential
for discovery of subsurface archaeological deposits that could qualify as historic properties under
Section 106 of the NHPA and/or historical or unique archaeological resources under CEQA.This
potential impact to unknown archaeological resources is considered significant. The following
mitigation measures are recommended to ensure that the project would result in No Historic
Properties Affected under Section 106 of the NHPA and less than significant impacts to historical
or unique archaeological resources under CEQA.
1. Construction Worker Cultural Resources Sensitivity Training:Prior to earth moving
activities,a qualified archaeologist meeting the Secretary of the Interior's Professional
Qualifications Standards for archaeology(U.S.Department of the Interior,2008)shall
conduct cultural resources sensitivity training for all construction personnel. Construction
personnel shall be informed of the types of cultural resources that may be encountered,
and of the proper procedures to be enacted in the event of an inadvertent discovery of
archaeological resources or human remains.OCWD shall ensure that construction
personnel are made available for and attend the training and retain documentation
demonstrating attendance.
2. Archaeological Monitoring: Prior to the start of any ground-disturbing activities,
OCWD shall retain an archaeological monitor to observe all ground-disturbing activities.
Archaeological monitoring shall be conducted by a monitor familiar with the types of
archaeological resources that could be encountered and shall work under the direct
supervision of the qualified archaeologist.Monitoring may be reduced or discontinued by
the qualified archaeologist,in coordination with OCWD,based on observations of
subsurface soil stratigraphy and/or the presence of older C-horizon deposits.The monitor
shall be empowered to halt or redirect ground-disturbing activities away from the vicinity
of a discovery until the qualified archaeologist has evaluated the discovery and
determined appropriate treatment. The monitor shall keep daily logs detailing the types of
activities and soils observed,and any discoveries.After monitoring has been completed,
the qualified archaeologist shall prepare a monitoring report that details the results of
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9. Conclusions and Recommendations
monitoring. The report shall be submitted to OCWD, SCCIC,and any Native American
groups who request a copy.
3. Native American Monitoring: Prior to issuance of a grading permit and prior to start of
any ground-disturbing activities,OCWD shall retain a Native American monitor to
observe all ground-disturbing activities. The monitor shall be obtained from a Tribe that
is traditionally and culturally affiliated with the area,according the NAHC list. The
monitor shall be empowered to halt or redirect ground-disturbing activities away from the
vicinity of a discovery until the qualified archaeologist has evaluated the discovery and
determined appropriate treatment. Monitoring may be reduced or discontinued,in
coordination with OCWD and the qualified archaeologist,based on observations of
subsurface soil stratigraphy and/or the presence of older C-horizon deposits.
4. Archaeological Discoveries: In the event of the discovery of archaeological materials,
OCWD or its contractor shall immediately cease all work activities in the area(within
approximately 100 feet)of the discovery until it can be evaluated by the qualified
archaeologist Prehistoric archaeological materials might include obsidian and their
flaked-stone tools(e.g.,projectile points,knives, scrapers)or tool-making debris;
culturally darkened soil C midded')containing heat-affected rocks,artifacts,or shellfish
remains;and stone milling equipment(e.g.,mortars,pestles,handstones, or milling
slabs);and battered stone tools,such as hammerstones and pitted stones. Historic-period
materials might include stone or concrete footings and walls;filled wells or privies; and
deposits of metal, glass,and/or ceramic refuse. Construction shall not resume until the
qualified archaeologist has conferred with OCWD on the significance of the resource.
SWRCB shall be afforded the opportunity to determine whether the discovery requires
addressing under Section 106 Post-Review Discoveries provisions provided in 36 CFR
800.13.
If it is determined that the discovered archaeological resource constitutes a historic
property under Section 106 of the NHPA or a historical resource under CEQA,avoidance
and preservation in place shall be the preferred manner of mitigation.Preservation in
place maintains the important relationship between artifacts and their archaeological
context and also serves to avoid conflict with traditional and religious values of groups
who may ascribe meaning to the resource. Preservation in place may be accomplished by,
but is not limited to, avoidance,incorporating the resource into open space,capping,or
deeding the site into a permanent conservation easement. In the event that preservation in
place is demonstrated to be infeasible and data recovery through excavation is the only
feasible mitigation available,an Archaeological Resources Treatment Plan that provides
for the adequate recovery of the scientifically consequential information contained in the
archaeological resource shall be prepared and implemented by the qualified archaeologist
in consultation with OCWD. The appropriate Native American representatives shall be
consulted in determining treatment for prehistoric or Native American resources to
ensure cultural values ascribed to the resource,beyond that which is scientifically
important,are considered.
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5. Human Remains: If human remains are encountered,OCWD or its contractor shall halt
work in the vicinity(within 100 Feet)of the find and contact the Orange County Coroner
in accordance with PRC Section 5097.98 and Health and Safety Code Section 7050.5. If
the County Coroner determines that the remains are Native American,the NAHC will be
notified in accordance with Health and Safety Code Section 7050.5, subdivision(c),and
PRC Section 5097.98. The NAHC will designate an MLD for the remains per PRC
Section 5097.98. Until the landowner has conferred with the MLD,OCWD shall ensure
that the immediate vicinity where the discovery occurred is not disturbed by further
activity,is adequately protected according to generally accepted cultural or
archaeological standards or practices,and that further activities take into account the
possibility of multiple burials.
8.2 Historic Built Resources
As a result of this study,two historic built resources(30-177464—SCE Transmission Tower M2-
T6 Ellis-Huntington Beach No.2 and 30-177612—SCE Transmission Tower M2-T5 Ellis/HB
No. 2)were identified adjacent to the existing pipeline portion of the project APE.Both resources
were previously recommended not eligible for the National Register and therefore do not qualify
as historic properties under Section 106 of the NHPA.Neither resource has been previously
evaluated for listing in the California Register;however,for the same reasons outlined in Section
5.1.2,these resources do not appear to meet the criteria for listing in the California Register and
they do not qualify as historical resources under CEQA.No further work or treatment is
recommended for these two resources.
Two potential historic built resources,OCSD Plant No. 1 and OCSD Plant No. 2,were identified
as a result of this study.Both plants were initially constructed more than 45 years agol,although
none of the historic-age buildings/structures appear to be within the APEZ. Project-related
activities OCSD Plant No. I will be limited to installation of a below-ground piping to connect to
existing facilities.No above-ground facilities would be constructed at this location and existing
potential historic buildings/structures are not located new the pipeline. Therefore,the project does
not have the potential to result in a significant impact to any potential historic resources on OCSD
Plant No. 1. Since above-ground buildings/structures are proposed at OSCD Plant No. 2,a
historical evaluation should be prepared for OCSD Plant No.2.
8.3 Paleontological Resources
Based on the results of the paleontological database search,there are no known fossil localities in
the APE and there is a low potential to uncover significant vertebrate fossil remains during
surface grading or shallow excavations in the APE.However, excavations that extend down into
1 The California OHP recommends including all resources over 45 years of age in the planning process given the lag
time between environmental documentation and project implementation.Generally,resources more than 50 years
of age require evaluation for listing in the National Register and California Register to assess impacts to historic
Properties under Section 106 of the NHPA and historical resources under CEQA.
i The Project may require creation of a separate architectural APE in order W adequately address directlindirect
effects to historic built resources.
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B. Conclusions and Recommendations
the older Quaternary deposits may encounter significant fossil vertebrate specimens. Since the
project includes ground-disturbing activities,there is a potential for discovery of fossils that may
be considered significant paleontological resources.This potential impact to unknown
paleontological resources is considered significant. The Following mitigation measures are
recommended to ensure that the project would result in less than significant impacts to unique
paleontological resources under CEQA.
1. Retention of a Qualified Paleontologist: Prior to the start of any ground-disturbing
activities,OCWD shall retain a qualified paleontologist meeting the Society of Vertebrate
Paleontology(SVP) Standards(SVP,2010).The qualified paleontologist shall contribute
to any construction worker cultural resources sensitivity training either in person or via a
training module provided to the qualified archaeologist.The training session shall focus
on the recognition of the types of paleontological resources that could be encountered
within the project site and the procedures to be followed if they are found. The qualified
paleontologist shall also conduct periodic spot checks in order to ascertain when older
deposits are encountered and where monitoring shall be required.
2. Paleontological Monitoring: Prior to the start of any ground-disturbing activities,
OCWD shall retain a paleontological monitor to observe all ground-disturbing activities
within older Quaternary deposits. Paleontological resources monitoring shall be
performed by a qualified paleontological monitor, or cross-trained
archaeological/paleontological monitor,under the direction of the qualified
paleontologist. The monitor shall have the authority to temporarily halt or divert work
away from exposed fossils in order to recover the fossil specimens.Monitoring may be
reduced or discontinued by the qualified paleontologist,in coordination with OCWD,
based on observations of subsurface soil stmtigmphy and/or other factors and if the
qualified paleontologist determines that the possibility of encountering fnssiliferous
deposits is low.The monitor shall prepare daily logs detailing the types of activities and
soils observed, and any discoveries. The qualified paleontologist shall prepare a final
monitoring a report to be submitted to OCWD and filed with the local repository.Any
recovered significant fossils shall be curated at an accredited facility with retrievable
storage.
3. Paleontological Discoveries: If construction or other project personnel discover any
potential fossils during construction,regardless of the depth or presence of a monitor,
work in the vicinity(within 100 feet)of the find shall cease until the qualified
paleontologist has assessed the discovery and made recommendations as to the
appropriate treatment.
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9. References
9. References
Armor, Samuel,History of Orange County, California:with biographical sketches of the leading
men and women of the county who have been identified with its earliest growth and
development from the early days to the present, Los Angeles: Historic Record Co., 1921.
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Vol. VII, 1860-1890,The History Company Publishers, San Francisco,CA, 1890.
Bean,L.J.and C.R. Smith. 1978."Gabrieliiio." In Handbook of North American Indians,Vol. 8:
California,edited by R.F. Heizer, 538-549.Washington,DC: Smithsonian Institution.
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Carlberg,Marvin and Chris Epting,Postcard History Series:Huntington Beach,Arcadia
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City of Huntington Beach,General Plan,Environmental Hazards Element, 1996a.
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http://egov.ocgov.com/vgnfiles/ocgov/Clerk-
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Information Center,California State University Fullerton.
Dixon,Keith A.,Early Holocene Human Adaptation on the Southern California Coast: A
Summary Report of Investigations at the Irvine Site(CA-ORA-64),Newport Bay,Orange
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Drover,C.E.,H.C.Koerper,and P. Langenwalter II,Early Holocene Human Adaptation on the
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Erlandson,Jon M.,Early Hunter-Gatherers of the California Coast.Plenum Press,New York,
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Historicaerials.com,Aerial photographs for the years 1953, 1963, 1972, 1994, 1995,2002,2003,
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in July,2016.
Gmadweter Replenlahmanl sy9le,Final Espanslan Prgea and ESP 1160W.01
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Groundwater Replenlshmert S)stem Final Eglansloo Project and Water Pmdudbn Enhancemed Profed.Phase I Culbml Resources aludy
9. References
Kroeber,A.L. 1925.Handbook of the Indians of California.Bulletin 78: Bureau of American
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172/sanana2dmu.pdf,accessed July 26, 2016.
Morton,D.M., and Miller,F.K. 2006. Geologic map of the San Bernardino and Santa Ana 30'x
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Oakeshott,G.B.,California's Changing Landscapes,A guide to the Geology of the States,2nd
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Orange County Sanitation District. http://www.ocsd.com/about-ocs&general-information/history.
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Orange County Water District(OCWD). Scott-Roberts, Sandy.Principal Engineer,OCWD.
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Vellmoweth,R.L. and J.H.Altschul,Antiquarians,Culture Historians,and Scientists: The
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9. References
Southern California Bight, edited by J.H.Altschul and D.G. Grenda,pp. 85-111, SRI Press,
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Wallace,W.J. 1955."A Suggested Chronology for Southern California Coastal Archaeology."
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Gmadwater Paplenlahmant syelea Final Espansan Prgea and ESP 116OW.01
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Appendix A.Resumes
APPENDIX A
Resumes
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Wabr Pwdudim Enhan—t Pmgd AUO.2016
Ph—I CulWml Re—S dy
r ESA
J
'I'd
Candace R. Ehringer, RPA
Senior Cultural Resources Specialist
EDUCATION Candace is a cultural resources project manager with 18 years of experience
M.A.,Anthropology, working across California.Candace manages multi-disciplinary cultural resources
California State projects which include archaeological,historic architectural,and paleontological
University,Northridge resources components.She is adept at building teams of specialists from these
B.A.,Anthropology,East resource areas that are uniquely qualified for the particular project at hand and has
Carolina University brought hundreds of projects to successful completion for both public agency and
private development clients.Candace provides technical and compliance oversight
18 YEARS EXPERIENCE for projects involving archaeological survey,evaluation,and treatment;built
AREAS OF EXCELLENCE environment studies including the documentation and evaluation of buildings,
structures,and districts;and paleontological resources survey and sensitivity
CEQA,NEPA,and assessments.She is proficient in the areas of CECI NEPA,and Section 106 and
Section lob pro routinely provides planning and strategic guidance to clients within the larger
Managesmulti- scope of state and federal regulations.
dlsclpllnaryCRM
projects
Strong historic resources Relevant Experience
research skills Los Angeles Unified School District, Historic Resources Evaluation of Five
QUALIFICATIONS Campuses,Los Angeles,CA.Project Manager.ESA provided historic resources
Interior's Standards
the K.services in support of proposed improvements to George Washington Carver
Exceeds Secretary Middle School,Graham Elementary School,Morris Hamasaki Elementary School,
Van Nuys Elementary School,and West Vernon Elementary School.Candace
Ca state ELM Permitted managed the preparation of historic resources evaluations of the five campuses.
CONTINUING ESA identified Van Nuys Elementary School and West Vernon Elementary School as
EDUCATION eligible.
AEP Advanced CEQA
Workshop,2o11 California Department of Water Resources,California Aqueduct Bridges Seismic
ACHP Section 106 Retrofit,Kern and San Bernardino Counties,CA.Project Manager.Candace
Essentialstraining managed the completion of an Archaeological Survey Report,a Historical Resources
cour,e,2oto Evaluation Report,a Historic Properties Survey Report,and Finding of Effect
Riverside County document in coordination with the California Department of Transportation
certification course,tote (Caltrans)and the California Department of Water Resources(DWR). DWR proposes
and 2011 to remedy structural seismic deficiencies for six existing bridges spanning the
PROFESSIONAL California Aqueduct.The California Aqueduct was determined eligible for listing in
PAPERS& the National Register under Criteria A and C for its association with irrigation and
PRESENTATIONS agricultural development of California and water conveyance engineering and
Ettinger,C.2014 Dead design.The six bridges are considered contributors to the aqueduct system.
Men Do Wear Plaid:
Garments and notions Cooper Molera Adobe,Monterey County,CA.Project Manager.The National Trust
for City Cemetery,Los for Historic Preservation has spearheaded a shared use program that aims to create
Angeles,California.oral a revitalized Cooper Valera Adobe.The intent is to balance compelling historic
paper at
aped Society
for Histbonorical
ri interpretation and education programs with appropriate and complementary
Archaeietyfor Historical
ArcnaeologyaPth annual commercial uses.Candace co-authored the Archaeological Research Design and
Meeting,Quebec City,
Quebeq Canada.
Candace R.Ehnngen RPA
Page 2
Treatment Plan (ARDTP)and implemented archaeological resources testing and
data recovery at the adobe.
California Department of Water Resources,Cantua Creek Stream Group
Improvements Project,Fresno County,CA.Project Manager.The California
Department of Water Resources(DW R)proposes to implement the Cantua Creek
Stream Group(CCSG)Improvements Project(Project).The CCSG is composed of five
major creeks:Arroyo Hondo,Cantua,Salt, Martinez,and Domengine.The CCSG
drains a portion of the Coast Range, located west of the Project area.Presently,
floodwaters from the CCSG terminate at four locations(Basins 1-4)along an
approximately 13-mile stretch of the San Luis Canal; Martinez Creek flows into Salt
Creek about 3 miles upstream of the San Luis Canal.Candace managed the
preparation of a Cultural Resource Inventory and Evaluation Report, Finding of
Effect,and Paleontological Resources Report in compliance with Section 106 of the
National Historic Preservation Act and CEQA.The Bureau of Reclamation was the
lead federal agency.
Monterey Regional Desalinization Project,Monterey County,CA.Senior Cultural
Resources Specialist. In support of the NEPA phase of this project,Candace
compiled information on cultural resources located along the proposed alternative
routes and authored a technical memo providing recommendations for the route
that would pose the least impact to known resources.She has also conducted
several surveys of pipeline routes and potential staging areas.The Bureau of
Reclamation is the lead federal agency for the project.
Los Angeles Unified School District, Historic Architectural Review of Twelve
Campuses,Los Angeles,CA.Project Manager.ESA provided historic resources
services in support of proposed improvements to 12 campuses.Candace conducted
site visits and oversaw the preparation of letter reports assessing the improvements
for compliance with the Secretary of the Interior's Standards.
City of Santa Barbara,Mission Creek Lagoon and Laguna Channel Restoration
Project,Santa Barbara County,CA.Project Manager.Candace managed the
preparation of a technical memorandum documenting a preliminary cultural
resource study and conducted the field survey.The study identified several cultural
resources that could pose a regulatory constraint on the project,including 18
historic built resources.The area was also identified as sensitive for archaeological
resources. ESA is currently assisting the City of Santa Barbara identify a design
alternative within the Project area that is economically feasible and meets the
multiple objectives of flood control,water quality improvement,public safety and
access,and habitat restoration.
DWR,Hyatt River Outlet Facility Life Extension Study,Oroville,CA.Project
Manager.The Hyatt River Outlet Facility Life Extension Study Project involves the
construction of outlet tunnels at the Edward Hyatt Power Plant to replace/repair
the River outlet.The Edward Hyatt Power Plant(1963-1969)and the Oroville Dam
(1961-1967)have been evaluated and appear eligible for listing in the National
Register of Historic Places.Candace managed the preparation of a technical
reportdocument which analyzed the existing records/data,assessed potential
effects to historic resources by the proposed activities,and concluded with a finding
of effect.
r ESA
r Arabesque Said-
Abdelwahed , MPP
Senior Associate
EDUCATION Arabesque has professional experience specializing in CEQA and NEPA-level
Master of public Policy, environmental documentation processes with a technical background in cultural
University of California, resources management,hazards and hazardous materials.She has focused on
I'me management and preparation of cultural resources literature reviews,
B.A.,Anthmpology, archaeological surveys,archaeological site testing,and data collection.She has
University ofcalifornin, also authored cultural resources reports required for environmental analysis.
Riverside Arabesque also brings significant experience performing Phase I environmental
8YEARS EXPERIENCE site assessments/environmental site reports.As an ASTM-trained environmental
site assessment professional,she has conducted dozens of Phase I ESAs in
PROFESSIONAL California.She has managed the preparation of Initial Studies and assisted in the
AFFILIATIONS preparation of Environmental Impact Reports.
Association of
Environmental
Professionals Relevant Experience
Register of Professional Countyof Orange,Cerritos Avenue Single-family residential project Initial
Archaeologists Study Mitigated Negative Declaration,Deputy Project Manager.Arabesque was
California Department of the assistant project manager for the preparation of an Initial Study Mitigated
Tovcsubstances Negative Declaration for a proposed 40-unit single-family residential project in
Control Registered
Environmental Assessor unincorporated Orange County.Arabesque was responsible for analysis and
content editing.
City of Santa Ana,Heritage Mixed-Use Development project EIR,Senior
Associate.Arabesque conducted analysis and prepared the cultural resources and
hazards and hazardous materials sections of the Environmental Impact Report.
Indian Wells valley Land Use Management Plan,Kern County,CA,Senior
Associate. ESA prepared a Program Environmental Impact Report(PEIR)for the
Indian Wells Valley Land Use Management Plan.This plan would evaluate the
existing and potential General Plan land use designation changes to support a
water balanced approach to land use planning.Arabesque prepared the hazards
and hazardous materials section ofthe EIR.
Sweetwater Authority,Richard A.Reynolds Desalination Plant Phase 2
Expansion Solar Project MND,Chula Vista,CA,Deputy Project Manager.
Arabesque was responsible for analysis and preparation of the Initial Study
Mitigated Negative Declaration including content editing,schedule maintenance,
staff coordination,and budget tracking.The Mitigated Negative Declaration was
prepared to address impacts associated with the installation of a solar
photovoltaic project on an existing desalination facility.
City of Baldwin Park Specific Plan EIR,Baldwin Park,CA,Senior Associate.ESA
Arabesque Said-Abdelwahed
Page 2
will be providing CEQA documentation and environmental planning services
associated with the Baldwin Park Transit Oriented District(TOD)Specific Plan for
the Downtown Area of Baldwin Park.This project aims to encourage transit-
oriented development,promote active transportation,reduce vehicle miles
traveled,and streamline the environmental review process for future projects.
Department of Toxic Substances Control,Santa Susana Field Laboratory EIR,
Ventura County,CA,Deputy Project Manager.Arabesque conducted analysis and
prepared the utilities section of the PEIR for the Santa Susana Field Laboratory.
She also coordinated the preparation of figures for the EIR.
City of Corona Department of Water and Power,Water Facilities Project,
Riverside County,CA.Assistant Project Manager.Arabesque assisted in the
preparation of the Initial Study and technical reports for the proposed water
production wells,pump houses,linearwells water transmission main and water
treatment facility.
City of Santa Ana Planning and Building Agency,Park View at Town and
Country Manor Project,Orange County,CA.Assistant Project Manager.
Arabesque prepared the Final EIR,MM RP,and Findings of Fact for the proposed
multi-story building at the existing Town and Country Manor"Continuing Care
Residential Community."Arabesque also supported the Project Director at two
Planning Commission meetings and City Council hearing.
The Shopoff Group,L.P.333 North Prairie Avenue Project,City of Inglewood,
Los Angeles County,CA.Assistant Project Manager.Arabesque assisted in the
preparation of EIR sections.Arabesque managed the preparation of the Cultural
Resources Assessment for the project area.
City of Wildomar,Riverside County,CA.Assistant Project Manager.Arabesque
assisted in the preparation of the EIR for the proposed residential project on
approximately 9-acres in the City of W ildomar.Arabesque prepared the project
description and impact sections including cultural resources,geology and soils,
hazards,land use,population and housing.
County of Riverside,Cabazon II Outlet Expansion Project,Riverside County,
CA.Project Manager.Arabesque coordinated the preparation of an Initial Study
for the proposed outlet mall expansion project in the community of Cabazon,CA.
Arabesque also coordinated the preparation of technical studies including a
Biological Habitat Assessment and Phase I Cultural Resources Assessment.
r ESA
J
Vanessa N . Ortiz, MA, RPA
Cultural Resources Specialist
EDUCATION Vanessa is an arch aeologist with over seven years of documentation,records
searches,survey,excavation,and monitoring experience.She is cross trained in
Id.A.,Anthropology archaeology and paleontology.She has worked extensively throughout California,
emphasis Archaeology,
California State with particular experience in the context of the Mojave and California Great Basin,
University,Los Angeles prehistoric food processing sites,and historic artifacts.
BA.Anthropology,
CaOfnmlo State Relevant Experience
University,Los Angeles
TVEARS E%PERIENCE Cltyof Beverly Hills Metro Purple Line Extension,Beverly Hills,CA.
Compliance Coordinator.ESA is retained by the City of Beverly Hills to conduct
PROFESSIONAL general compliance monitoring during the advanced utilities relocation phaseof
AFFILIATIONS construction for the segment of the Metro Purple Line Extension Project located in
Registerof Professional the City of Beverly Hills.Vanessa oversees ESAmonitors,prepareweekly reports
Archaeologists and 3-week look-ahead projections based on estimated contractor planned
Society for American activities.As needed,she issues violations in the event a non-compliance issue is
Archaeology identified.ESA's primary objective isto assist contractors in avoidingnon-
California Cukural compliance issues through thorough observation and open communication.
Resources Preservation
Alliance Ballona Wetland Restoration,Playa Del Rey,CA.Archaeologist As part of the
Sedetyfor Califomis development of the restoration plan for the Ballona Wetlands,the ESA project
Archaeology team characterized existing conditions that included water and sediment
Lambda Alpha Honors sampling and analysis.The water and sediment quality sampling was performed
society to develop and evaluate potential restoration alternatives,and to develop
conceptual plan.The ESA project team compiled existing data on and conducted
additional sampling for water and sediment to assess potential effects on the
proposed wetland restoration habitat from the use of urban runoff and tidal in-
flow from Ballona Creek.These data were used to complete a baseline report and
restoration alternatives assessment.Vanessa assisted 1n survey,data recovery
and artifact analysis.
Los Angeles Department of Water and Power(LADWP),Path 46 Clearance
Surveys,San Bernardino,CA.Archaeologist. ESA has been tasked by LADWP to
conduct required surveys for the Path 46 Transmission Line Clearances Project.
The project's objective is to restore required code clearances to the transmission
conductors,which will be accomplished by grading the ground surface
underneath the transmission lines to achieve required height consistency.The
work is being conducted in compliance with BLM guidelines and federal laws and
statutes.Biological,archaeological,and paleontological resource surveys are
currently being conducted for the 77 proposed grading areas,staging areas,and
roads.Pending reports will document results of the surveys and provide
recommendations for minimally invasive access areas,staging areas,and soil
distribution. Vanessa provided field surveys and documentation of
archaeological sites for submission to the California State Parks.
Vanessa N.Ortiz,MA,RPA
Page 2
Los Angeles Department of Water and Power(LADWP),Scattergood Olympic
Transmission Line(SOTL)Cultural Resources Monitoring,Los Angeles,CA.
Archaeologist.LADWP is constructing and will operate approximately 11.4 miles of
new 230 kilovolt(kv)underground transmission line.LADWP installed 55 vaults
and underground conduit for the SOTL Project.ESA provided cultural resources
services,including archaeological,Native American,and paleontological
monitoring,to fulfill the requirements of the Project El R mitigation measures for
cultural resources. Reports documenting the monitoring findings were submitted
at the end of the project.Vanessa provided oversight and scheduling to monitors
and assisted in preparing the final report.
California High Speed Rail,Fresno,CA.Archaeological Monitor.ESA was
retained as a sub-consultant to the Tutor Perini Zachary Parsons Joint Venture.
The project consisted of pre-construction surveys for biological and cultural
resources,compliance monitoring during construction,and compliance tracking
and reporting.Approximately 29 miles in length,the project also included both
biological and cultural resources such as the historic Chinatown in downtown
Fresno,vernal pool and seasonal wetland habitat and crossings of the San
Joaquin and Fresno Rivers.Vanessa provided archaeological monitoring for the
Project during construction.
Los Angeles Department of Water and Power,La Kretz Innovation Campus
Project,Los Angeles,CA.Archaeological Monitor and Lab Technician. ESA
provided archaeological monitoring in connection with the La Kretz Innovation
Campus Project located in downtown Los Angeles.ESA conducted construction
worker cultural resources sensitivity training;archaeological monitoring;and
prepared a monitoring report.The Project involved the rehabilitation of the
61,000-sq u a re-foot building located at 518-524 Colyton Street,the demolition of
the building located at 537-551 Hewitt Street,and the construction of an open
space public plaza,and surface parking lot,and involved compliance with Section
106 of the National Historic Preservation Act and consultation with the California
State Historic Preservation Officer.Vanessa provided monitoring for the duration
of the Project as well as a lab technician during the cu ratio n of the artifacts
recovered from the Project and co-authored the final cultural report.
Los Angeles Department of Water and Power(LADWP),Silver Lake Reservoir
Complex(SLRC)Storage Replacement and River Supply Conduit 1A,Los
Angeles County,CA.Archaeological and Paleontological Monitor.ESA is providing
archaeological and paleontological monitoring for SLRC Storage Replacement
and River Supply Conduit lA Project.As part of this task,ESA conducted
construction worker cultural resources sensitivity training and archaeological and
paleontological monitoring.A final monitoring report will be prepared at the end
of construction. Vanessa was the field monitor on this project.
ApaeWx B.SCCICR rda Sea"Results
Zoefidential,Bound Separatelyll
APPENDIX B
SCCIC Records Search Results
( Confidential, Bound SeparatelA
Grcundweler W..iA—t Syelem li di Espenaian Prgea and ESP 11a036].01
Wabr Pwdudim Eehsemmee�P-g Au us12016
Ph—I CuIWmi Reawrres SWdy
ApeeMlx C.NW a eri nCorrespondence
APPENDIX C
Native American Correspondence
GrcunEweler RePleniA—t syelem F dl EspenalN PNjea ene E8 1 iQpW 01
Wabr Pwdudim Enhan—t P-g Au0.2016
Ph—I CulWnl Re—S dy
Sacred Lands File&Native American Contacts List Request
NATIVE AMERICAN HERITAGE COMMISSION
1550 Harbor Blvd, Suite 100
West Sacramento, CA 95691
(916) 373-3710
(916) 373-5471 —Fax
nahc@nahc.ca.gov
Information Below is Required for a Sacred Lands File Search
Project: Section 106 Cultural Resources Assessment for the Groundwater
Replenishment System Final Expansion
County: Orange
USGS Quadrangle Name: Newport Beach
Townships: 5 and 6 South---Range: 10 West Section(s): Multiple
Company: Environmental Science Associates
Contact Person: Arabesque Said, MPP
Street Address: 2121 Alton Parkway, Suite 100, Irvine, CA 92606
Cell 951.310.7031
Office Phone: 213.599.4300
Fax: 213.599.4301
Email as needed: aabdelwahedaesassoc.com
SEE ATTACHED MAP
The GWRS Final Expansion Project involves five construction activities; 1)
Increasing microfiltration capacity, 2) Increasing reverse osmosis treatment
capacity, 3)Increasing ultraviolet treatment capacity, 4)final product water
and 5) construction of a pump station, 6) construction of a flow equalization
tank and associated appurtenances, and 7) conversion of existing gravity
pipeline to a pressurized pipeline. The project is located in multiple sections
of Townships 5 and 6 South; Range 10 West of the Newport Beach,CA 7.5'
United States Geological Survey Topographic Quadrangle Map.
Lenard
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or-
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OCWD Groundwater Replenishment System Final Expansion Project.P160387.01
SOURCE:USGS Newport Beach,CA(1618)7.5'DRG; Figure I
Local Vicinty Map Topographic Base
Area of Potential Effects
{
MF II In Ex n I n n OCSD GWRS.
E l m n n II Ion Facility Sunflower Ave
M B In kwa 1 Ellis Ave
Pump II �-• 1• •' • • • •♦
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um E i � • �� �
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6' 1,
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SD Pipe uinne io
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fisting as in
1
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r for Rehabilitation
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' - • I w Ep ump to ion
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OCSD Plant No. 2 LSD Pump Station
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SOURCE:ESRI OCWD Groundwater Replenishment System Final Expansion Project.P160381.01
Figure 3
Area of Potential Effects
T TEO CALEQRN• Etl0W G.Blown Jr. Go yejI
NATIVE AMERICAN HERITAGE COMMISSION 11"
1%0 Hdrw'Swa,SWtA 100 ys
Went Sd..To,CA 95591
(916)n1n10
Fdi(916)n3iP)1
June 6, 2016
Arabesque Said, MPP
Environmental Science Associates
Sent by Email: aabdelwahed@esassoc.com
RE: Proposed Groundwater Replenishment System Final Expansion, Cultural Resources
Assessment Project, City of Huntington Beach; Newport Beach USGS Quadrangle,
Orange County, California
Dear M. Said:
A record search of the Native American Heritage Commission (NAHC) Sacred Lands
File was completed for the area of potential project effect(APE) referenced above with negative
results. Please note that the absence of specific site information in the Sacred Lands File does
not indicate the absence of Native American cultural resources in any APE.
I suggest you contact all of the listed Tribes. If they cannot supply information, they
might recommend others with specific knowledge. The list should provide a starting place to
locate areas of potential adverse impact within the APE. By contacting all those on the list, your
organization will be better able to respond to claims of failure to consult. If a response has not
been received within two weeks of notification, the NAHC requests that you follow-up with a
telephone call to ensure that the project information has been received.
If you receive notification of change of addresses and phone numbers from any of these
individuals or groups, please notify me. With your assistance we are able to assure that our
lists contain current information. If you have any questions or need additional information,
please contact via email: gayle.totton@nahc.ca.gov.
Sincerely,
a Totto ., PhD.
ssoc(ate Governmental Program Analyst
Native American Contact List
Orange County
June 3, 2016
Juaneno Band of Mission Indians Aciachemen Nation Juaneno Band of Mission Indians
Chairperson, Mallets Belardes Adolph 'Bud' Sepulveda, Vice Chairperson
32161 Avenida Los Amigos Juaneno P.O. Box 25828 Juaneno j
San Juan capiammno , CA 92675 Santa Ana CA 92799
(949)293-8522 bssepul@yahoo.net
(949)444-4340 (Cell) (714) 83"270
(714) 914-1812 Cell
Gabrieleno/Tongva San Gabriel Band of Mission Indians Juaneno Band of Mission Indians
Anthony Morales, Chairperson Sonia Johnston, Tribal Chairperson
P.O. Box 693 Gabrielino Tongva P.O. Box 25628 Juaneno
San Gabriel CA 91778 Santa Ana , CA 92799
GTTrlbelcouncil®aol.c m sonia.johnston0sbcglobal.net '..
(626) 483-3564 Cell
(626) 286-1262 Fax
Gabrielino/Tongue Nation Gabdelino-Tongve Tribe
Sandonne Goad, Chairperson Bemis Acuna, Co-Chairperson
10612 Judge John Also St., #231 Gabrielino Tongva 1999 Avenue of the Stars,Suite 1100 Gabrielino
Los Angeles , CA 90012 Los Angeles , CA 90067
agoad4gabrielino•lolgve.com
(951) 807-0479 (310)428-5690 Cell
I
Juaneno Band of Mission Indians Acjachemen Nation Juaneno 13ar,a of Mission Indians Agachemen Nation
Teresa Romero, Chairwoman Joyce Perry, Tribal Manager
31411-A La Matanza Street Juaneno 4955 Paseo Segovia Juaneno
San Juan Capistrano , CA 92675 Irvine CA 92612
tromero@juaneno.com kaamalam@gmail.com
(949) 488-3484 (949) 293-8522
(530)354-5876 Cell
(949) 488-3294 Fax
Gabrlelino Tongva Indians of Callrornla Tribal Council Gabrielino-Tongva Tribe
Robert F. Dorame, Tribal Chair/Cultural Resources Linda Candelaria, Co-Chairperson j
P.O. Box 490 Gabrielino Tongva 1999 Avenueaf the Stara suite 1100 Gabrielino
Bellflower CA 90707 Los Angeles , CA 90067
gtongva@verizon.net (626) 676-1184 Cell
(562) 761-6417 Voice/Fax
This little current only es Wine date of this documeni and is based on the Information available to the Commission on the data Itwas produced.
Distribution of this list does.1 relieve any person or agency of stautory responslbll try as deft ned In Public Resources Coca Sections 21 aeo.a.
Secton 7050.5 of the Health and Safety Code,Section 6097.94 of the Public Rmou rare Code and Section W97.W of me Public Resource.Code.
This Ifst Is only applicable far connoting loss,Native Americans with regard to cultural resources for the proposed Groundwater Replenishment
System Mae Espension,Section 105 Cultural Resources Assessment Prolwth City d Hach ngton Beath,Newport Seed,USGS Quadrangle,Orange
County,California.
Native American Contact List
Orange County
June 3, 2016
Gabrieleno Band of Mission Indians - Kizh Nation
Andrew Salas, Chairperson
P.O. Box393 Gabrielino
Covina r CA 91723
gabrielenoindians@yahoo.com
(626) 926-4131
I
Gabrielino-Tongva Tribe I
Conrad Acuna
'999 Avenue of the Stars,Sulte 1100 Gabrielino
Los Angeles , CA 90067
Gabrielino /Tongva Nation
Sam Dunlap, Cultural Resources Director
P.O. Box 80908 Gabrielino Tongva
Los Angeles . CA 90086
Bamdunlap @ earthlink.net
(909) 262-9351
I
i
I
i
i
I
This list is current only as of the date of lhls document and Is based on the Information available to the Commission on the date it was Produced.
Distribution of Mis list does not relieve any person or agency of statutory responsibility as defined In Public Resources Code Sections 21080.3.1
Seotgn 1050.5 of the Health and Safety Code,Section 5097.94 of the Public Resources;Code and Secton 5097.98 of the Public Resources Cade.
This Ilm le only appllcable for caniacting local Native Americans with regard to cultural resources for the poposed Groundweter Replenishment
System Final Fxpanslon,Section 10S Cultural Resources Asseesment Project,City of Huntington Beech,Newport Beach USGS Quadrangle,Orange
County,California.
I ESA 2121 Mon Pwr aY www.esassoc.com
Suite 100
JIrvine,CA 92606
213.599.6300 phone
213.599.6301 fan
June 20,2016
Chairperson Matias Belardes
luanefio Band of Mission Indians Acjachemen Nation
32161 Avenida Los Amigos
San Juan Capistrano,CA 92675
Subject: Groundwater Replenishment System Final Expansion Project—D160387.01
Dear Chairperson Belardes:
ESA is conducting a cultural resources assessment as part of CEQA-Plus documentation for the Groundwater
Replenishment System(GWRS)Final Expansion Project(project)located in the cities of Huntington Beach and
Fountain Valley,California.The GWRS is an advanced water treatment facility constructed by the Orange
County Water District(OCWD)and the Orange County Sanitation District(OCSD)that supplements local water
supplies by providing reliable,high quality source of treated water to recharge the Orange County Groundwater
Basin and to protect the Orange County Groundwater Basin from seawater intrusion.The GWRS consists of
three major components: an advanced water purification facility and pumping stations,a major pipeline
connecting the treatment facilities to existing recharge basins and an existing seawater intrusion barrier.The
proposed project would include the construction and operation of an expanded microfiltration treatment facility,
expanded Reverse Osmosis Treatment Capacity,expanded ultraviolet light treatment facility at the existing
OCWD GWRS Facility in Fountain Valley. The project would also include construction and operation of a new
PUMP station at the OCSD Treatment Plant No.2 in Huntington Beach and the renovation of an existing water
supply pipeline located on the west side of the Santa Ana River. A separate headworks facility and a bypass
pipeline would be constructed on OCSD's Plant No. 2 that will segregate the brine flows from the typical
influent domestic wastewater flows to Plant No. 2. As seen on the attached topographic map,the project area is
located within multiple sections of Townships 5 and 6 south;Range 10 West of the United States Geologic
Survey(USGS)Newport Beach,CA 7.5' topographic quadrangle.
Section 106 of the National Historic Preservation Act of 1966(NHPA)considers the effects a project may have
on historic properties.The definition of"historic properties"can include properties of traditional religious and
cultural significance to Native American groups.To determine whether the proposed project may impact any
historic properties,including traditional cultural properties,ESA has reviewed background information and
consulted with the Native American Heritage Commission(NAHC). Our records search at the South Central
Coastal Information Center(SCCIC), indicate that there are no known cultural resources in the Area of Potential
Effect(APE). A record search of the NAHC's Sacred Land File has failed to indicate the presence of Native
American cultural resources in the immediate APE. The NAHC has listed you as a tribal contact for this project.
r ESA
Chairperson Matins Belardes
June 20,2016
Page 2
We would appreciate your comments identifying any sensitive sites in or near the project area that you may be
aware of,any concerns or issues pertinent to this project,or the names of others who may be interested in this
project.Thank you for your cooperation on this matter. If you have any questions or comments,please contact me
at 949.870.1524(cell)or a abdelwahed@esmsoc.com.
Sincerely,
4
Arabesque Said-Abdelwahed, MPP
Community Development
I ESA 2121 Mon Parkway .www.eeeeeoc.cnnn
Suite 100
JIrvine,CA 92606
213.599.6300 phone
213.599.6301 fax
June 20,2016
Chairperson Anthony Morales
Gabrieleno/Tongva San Gabriel Band of Mission Indians
P.O.Box 693
San Gabriel, CA 91778
Subject: Groundwater Replenishment System Final Expansion Project—D160387.01
Dear Chairperson Morales, :
ESA is conducting a cultural resources assessment as part of CEQA-Plus documentation for the Groundwater
Replenishment System(GWRS)Final Expansion Project(project)located in the cities of Huntington Beach and
Fountain Valley,California.The GWRS is an advanced water treatment facility constructed by the Orange
County Water District(OCWD)and the Orange County Sanitation District(OCSD)that supplements local water
supplies by providing reliable,high quality source of treated water to recharge the Orange County Groundwater
Basin and to protect the Orange County Groundwater Basin from seawater intrusion.The GWRS consists of
three major components: an advanced water purification facility and pumping stations,a major pipeline
connecting the treatment facilities to existing recharge basins and an existing seawater intrusion barrier.The
proposed project would include the construction and operation of an expanded microfiltration treatment facility,
expanded Reverse Osmosis Treatment Capacity,expanded ultraviolet light treatment facility at the existing
OCWD GWRS Facility in Fountain Valley. The project would also include construction and operation of a new
PUMP station at the OCSD Treatment Plant No.2 in Huntington Beach and the renovation of an existing water
supply pipeline located on the west side of the Santa Ana River. A separate headworks facility and a bypass
pipeline would be constructed on OCSD's Plant No. 2 that will segregate the brine flows from the typical
influent domestic wastewater flows to Plant No. 2. As seen on the attached topographic map,the project area is
located within multiple sections of Townships 5 and 6 south;Range 10 West of the United States Geologic
Survey(USGS)Newport Beach,CA 7.5' topographic quadrangle.
Section 106 of the National Historic Preservation Act of 1966(NHPA)considers the effects a project may have
on historic properties.The definition of"historic properties"can include properties of traditional religious and
cultural significance to Native American groups.To determine whether the proposed project may impact any
historic properties,including traditional cultural properties,ESA has reviewed background information and
consulted with the Native American Heritage Commission(NAHC). Our records search at the South Central
Coastal Information Center(SCCIC), indicate that there are no known cultural resources in the Area of Potential
Effect(APE). A record search of the NAHC's Sacred Land File has failed to indicate the presence of Native
American cultural resources in the immediate APE. The NAHC has listed you as a tribal contact for this project.
r ESA
Chairperson Anthony Morales
June 20,2016
Page 2
We would appreciate your comments identifying any sensitive sites in or near the project area that you may be
aware of,any concerns or issues pertinent to this project,or the names of others who may be interested in this
project.Thank you for your cooperation on this matter. If you have any questions or comments,please contact me
at 949.870.1524(cell)or abdelwahed@esassm.com.
Sincerely,
Arabesque Said-Abdelwahed,MPP
Community Development
r ESA 2121 Mon Pwr aY www.esassoc.com
Suite 100
JIrvine,CA 92606
213.599.6300 phone
213.599.6301 fax
June 20,2016
Chaiperson Sandonne Goad
Gabrielino/Tongva Nation
106 1/2 Judge John Aliso St.
#231
Los Angeles,CA 90012
Subject: Groundwater Replenishment System Final Expansion Project—D160387.01
Dear Chaiperson Goad:
ESA is conducting a cultural resources assessment as part of CEQA-Plus documentation for the Groundwater
Replenishment System(GWRS)Final Expansion Project(project)located in the cities of Huntington Beach and
Fountain Valley,California.The GWRS is an advanced water treatment facility constructed by the Orange
County Water District(OCWD)and the Orange County Sanitation District(OCSD)that supplements local water
supplies by providing reliable,high quality source of treated water to recharge the Orange County Groundwater
Basin and to protect the Orange County Groundwater Basin from seawater intrusion.The GWRS consists of
three major components: an advanced water purification facility and pumping stations,a major pipeline
connecting the treatment facilities to existing recharge basins and an existing seawater intrusion barrier.The
proposed project would include the construction and operation of an expanded microfiltration treatment facility,
expanded Reverse Osmosis Treatment Capacity,expanded ultraviolet light treatment facility at the existing
OCWD GWRS Facility in Fountain Valley. The project would also include construction and operation of a new
pump station at the OCSD Treatment Plant No.2 in Huntington Beach and the renovation of an existing water
supply pipeline located on the west side of the Santa Ana River.A separate headworks facility and a bypass
pipeline would be constructed on OCSD's Plant No. 2 that will segregate the brine flows from the typical
influent domestic wastewater flows to Plant No. 2. As seen on the attached topographic map,the project area is
located within multiple sections of Townships 5 and 6 south;Range 10 West of the United States Geologic
Survey(USGS)Newport Beach,CA 7.5'topographic quadrangle.
Section 106 of the National Historic Preservation Act of 1966(NHPA)considers the effects a project may have
on historic properties.The definition of"historic properties"can include properties of traditional religious and
cultural significance to Native American groups.To determine whether the proposed project may impact any
historic properties,including traditional cultural properties,ESA has reviewed background information and
consulted with the Native American Heritage Commission(NAHC). Our records search at the South Central
Coastal Information Center(SCCIC),indicate that there are no known cultural resources in the Area of Potential
Effect(APE). A record search of the NAHC's Sacred Land File has failed to indicate the presence of Native
American cultural resources in the immediate APE. The NAHC has listed you as a tribal contact for this project.
r ESA
Chaiperson Sandonne Goad
June 20,2016
Page 2
We would appreciate your comments identifying any sensitive sites in or near the project area that you may be
aware of,any concerns or issues pertinent to this project,or the names of others who may be interested in this
project.Thank you for your cooperation on this matter. If you have any questions or comments,please contact me
at 949.870.1524(cell)or a abdelwahed@esmsoc.com.
Sincerely,
4
Arabesque Said-Abdelwahed, MPP
Community Development
I ESA 2121 Mon Pwr aY www.esassoc.com
Suite 100
JIrvine,CA 92606
213.599.6300 phone
213.599.6301 fan
June 20,2016
Chairwoman Teresa Romero
luanefio Band of Mission Indians Acjachemen Nation
31411-A La Matanza Street
San Juan Capistrano,CA 92675
Subject: Groundwater Replenishment System Final Expansion Project—D160387.01
Dear Chairwoman Romero :
ESA is conducting a cultural resources assessment as part of CEQA-Plus documentation for the Groundwater
Replenishment System(GWRS)Final Expansion Project(project)located in the cities of Huntington Beach and
Fountain Valley,California.The GWRS is an advanced water treatment facility constructed by the Orange
County Water District(OCWD)and the Orange County Sanitation District(OCSD)that supplements local water
supplies by providing reliable,high quality source of treated water to recharge the Orange County Groundwater
Basin and to protect the Orange County Groundwater Basin from seawater intrusion.The GWRS consists of
three major components: an advanced water purification facility and pumping stations,a major pipeline
connecting the treatment facilities to existing recharge basins and an existing seawater intrusion barrier.The
proposed project would include the construction and operation of an expanded microfiltration treatment facility,
expanded Reverse Osmosis Treatment Capacity,expanded ultraviolet light treatment facility at the existing
OCWD GWRS Facility in Fountain Valley. The project would also include construction and operation of a new
PUMP station at the OCSD Treatment Plant No.2 in Huntington Beach and the renovation of an existing water
supply pipeline located on the west side of the Santa Ana River. A separate headworks facility and a bypass
pipeline would be constructed on OCSD's Plant No. 2 that will segregate the brine flows from the typical
influent domestic wastewater flows to Plant No. 2. As seen on the attached topographic map,the project area is
located within multiple sections of Townships 5 and 6 south;Range 10 West of the United States Geologic
Survey(USGS)Newport Beach,CA 7.5' topographic quadrangle.
Section 106 of the National Historic Preservation Act of 1966(NHPA)considers the effects a project may have
on historic properties.The definition of"historic properties"can include properties of traditional religious and
cultural significance to Native American groups.To determine whether the proposed project may impact any
historic properties,including traditional cultural properties,ESA has reviewed background information and
consulted with the Native American Heritage Commission(NAHC). Our records search at the South Central
Coastal Information Center(SCCIC), indicate that there are no known cultural resources in the Area of Potential
Effect(APE). A record search of the NAHC's Sacred Land File has failed to indicate the presence of Native
American cultural resources in the immediate APE. The NAHC has listed you as a tribal contact for this project.
r ESA
Chairperson Teresa Romero
June 20,2016
Page 2
We would appreciate your comments identifying any sensitive sites in or near the project area that you may be
aware of,any concerns or issues pertinent to this project,or the names of others who may be interested in this
project.Thank you for your cooperation on this matter.If you have any questions or comments,please contact me
at 949.870.1524(cell)or a abdelwahed@esmsoc.com.
Sincerely,
4
Arabesque Said-Abdelwahed, MPP
Community Development
r ESA 2121 Aron Pwr aY www.esassoc.com
Suite 100
JIrvine,CA 92606
213.599.6300 phone
213.599.6301 fan
June 20,2016
Vice Chairperson Adolph"Bud" Sepulveda
luanefio Band of Mission Indians
P.O.Box 25828
Santa Ana, CA 92799
Subject: Groundwater Replenishment System Final Expansion Project—D160387.01
Dear Vice Chairperson Sepulveda :
ESA is conducting a cultural resources assessment as part of CEQA-Plus documentation for the Groundwater
Replenishment System(GWRS)Final Expansion Project(project) located in the cities of Huntington Beach and
Fountain Valley,California.The GWRS is an advanced water treatment facility constructed by the Orange
County Water District(OCWD)and the Orange County Sanitation District(OCSD)that supplements local water
supplies by providing reliable,high quality source of treated water to recharge the Orange County Groundwater
Basin and to protect the Orange County Groundwater Basin from seawater intrusion.The GWRS consists of
three major components: an advanced water purification facility and pumping stations,a major pipeline
connecting the treatment facilities to existing recharge basins and an existing seawater intrusion barrier.The
proposed project would include the construction and operation of an expanded microfiltration treatment facility,
expanded Reverse Osmosis Treatment Capacity,expanded ultraviolet light treatment facility at the existing
OCWD GWRS Facility in Fountain Valley. The project would also include construction and operation of a new
PUMP station at the OCSD Treatment Plant No. 2 in Huntington Beach and the renovation of an existing water
supply pipeline located on the west side of the Santa Ana River. A separate headworks facility and a bypass
pipeline would be constructed on OCSD's Plant No. 2 that will segregate the brine flows from the typical
influent domestic wastewater flows to Plant No. 2. As seen on the attached topographic map,the project area is
located within multiple sections of Townships 5 and 6 south;Range 10 West of the United States Geologic
Survey(USGS)Newport Beach,CA 7.5' topographic quadrangle.
Section 106 of the National Historic Preservation Act of 1966(NHPA)considers the effects a project may have
on historic properties.The definition of"historic properties"can include properties of traditional religious and
cultural significance to Native American groups.To determine whether the proposed project may impact any
historic properties,including traditional cultural properties,ESA has reviewed background information and
consulted with the Native American Heritage Commission(NAHC). Our records search at the South Central
Coastal Information Center(SCCIC), indicate that there are no known cultural resources in the Area of Potential
Effect(APE). A record search of the NAHC's Sacred Land File has failed to indicate the presence of Native
American cultural resources in the immediate APE. The NAHC has listed you as a tribal contact for this project.
r ESA
Vice Chairperson Adoplh'Bud" Sepulveda
June 20,2016
Page 2
We would appreciate your comments identifying any sensitive sites in or near the project area that you may be
aware of,any concerns or issues pertinent to this project,or the names of others who may be interested in this
project.Thank you for your cooperation on this matter. If you have any questions or comments,please contact me
at 949.870.1524(cell)or a abdelwahed@esmsoc.com.
Sincerely,
4
Arabesque Said-Abdelwahed, MPP
Community Development
r ESA 2121 Mon Parkway .www.eeeeeoc.cnm
Suite 100
JIrvine,CA 92606
213.599.6300 phone
213.599.6301 fax
June 20,2016
Tribal Chairperson Sonia Johnston
luanefio Band of Mission Indians
P.O.Box 25628
Santa Ana, CA 92799
Subject: Groundwater Replenishment System Final Expansion Project—D160387.01
Dear Tribal Chairperson Johnston:
ESA is conducting a cultural resources assessment as part of CEQA-Plus documentation for the Groundwater
Replenishment System(GWRS)Final Expansion Project(project) located in the cities of Huntington Beach and
Fountain Valley,California.The GWRS is an advanced water treatment facility constructed by the Orange
County Water District(OCWD)and the Orange County Sanitation District(OCSD)that supplements local water
supplies by providing reliable,high quality source of treated water to recharge the Orange County Groundwater
Basin and to protect the Orange County Groundwater Basin from seawater intrusion.The GWRS consists of
three major components: an advanced water purification facility and pumping stations,a major pipeline
connecting the treatment facilities to existing recharge basins and an existing seawater intrusion barrier.The
proposed project would include the construction and operation of an expanded microfiltration treatment facility,
expanded Reverse Osmosis Treatment Capacity,expanded ultraviolet light treatment facility at the existing
OCWD GWRS Facility in Fountain Valley. The project would also include construction and operation of a new
PUMP station at the OCSD Treatment Plant No.2 in Huntington Beach and the renovation of an existing water
supply pipeline located on the west side of the Santa Ana River. A separate headworks facility and a bypass
pipeline would be constructed on OCSD's Plant No. 2 that will segregate the brine flows from the typical
influent domestic wastewater flows to Plant No. 2. As seen on the attached topographic map,the project area is
located within multiple sections of Townships 5 and 6 south;Range 10 West of the United States Geologic
Survey(USGS)Newport Beach,CA 7.5' topographic quadrangle.
Section 106 of the National Historic Preservation Act of 1966(NHPA)considers the effects a project may have
on historic properties.The definition of"historic properties"can include properties of traditional religious and
cultural significance to Native American groups.To determine whether the proposed project may impact any
historic properties,including traditional cultural properties,ESA has reviewed background information and
consulted with the Native American Heritage Commission(NAHC). Our records search at the South Central
Coastal Information Center(SCCIC), indicate that there are no known cultural resources in the Area of Potential
Effect(APE). A record search of the NAHC's Sacred Land File has failed to indicate the presence of Native
American cultural resources in the immediate APE. The NAHC has listed you as a tribal contact for this project.
r ESA
Tribal Chairperson Sonia Johnston
June 20,2016
Page 2
We would appreciate your comments identifying any sensitive sites in or near the project area that you may be
aware of, any concerns or issues pertinent to this project,or the names of others who may be interested in this
project.Thank you for your cooperation on this matter. If you have any questions or comments,please contact me
at 949.870.1524(cell)or mbdelwahed@esmsoc.com.
Sincerely,
Arabesque Said-Abdelwahed, MPP
Community Development
r ESA 2121 Mon Parkway .www.eeaeeoc.cnnn
Suite 100
JIrvine,CA 92606
213.599.6300 phone
213.599.6301 fax
June 20,2016
Co-Chairperson Bernie Acuna
Gabrielino-Tongva Tribe
1999 Avenue of the Stars
Suite 1100
Los Angeles,CA 90067
Subject: Groundwater Replenishment System Final Expansion Project—D160387.01
Dear Co-Chairperson Aeons :
ESA is conducting a cultural resources assessment as part of CEQA-Plus documentation for the Groundwater
Replenishment System(GWRS)Final Expansion Project(project)located in the cities of Huntington Beach and
Fountain Valley,California.The GWRS is an advanced water treatment facility constructed by the Orange
County Water District(OCWD)and the Orange County Sanitation District(OCSD)that supplements local water
supplies by providing reliable,high quality source of treated water to recharge the Orange County Groundwater
Basin and to protect the Orange County Groundwater Basin from seawater intrusion.The GWRS consists of
three major components: an advanced water purification facility and pumping stations,a major pipeline
connecting the treatment facilities to existing recharge basins and an existing seawater intrusion barrier.The
proposed project would include the construction and operation of an expanded microfiltration treatment facility,
expanded Reverse Osmosis Treatment Capacity,expanded ultraviolet light treatment facility at the existing
OCWD GWRS Facility in Fountain Valley. The project would also include construction and operation of a new
pump station at the OCSD Treatment Plant No.2 in Huntington Beach and the renovation of an existing water
supply pipeline located on the west side of the Santa Ana River.A separate headworks facility and a bypass
pipeline would be constructed on OCSD's Plant No. 2 that will segregate the brine flows from the typical
influent domestic wastewater flows to Plant No. 2. As seen on the attached topographic map,the project area is
located within multiple sections of Townships 5 and 6 south;Range 10 West of the United States Geologic
Survey(USGS)Newport Beach,CA 7.5'topographic quadrangle.
Section 106 of the National Historic Preservation Act of 1966(NHPA)considers the effects a project may have
on historic properties.The definition of"historic properties"can include properties of traditional religious and
cultural significance to Native American groups.To determine whether the proposed project may impact any
historic properties,including traditional cultural properties,ESA has reviewed background information and
consulted with the Native American Heritage Commission(NAHC). Our records search at the South Central
Coastal Information Center(SCCIC),indicate that there we no known cultural resources in the Area of Potential
Effect(APE). A record search of the NAHC's Sacred Land File has failed to indicate the presence of Native
American cultural resources in the immediate APE. The NAHC has listed you as a tribal contact for this project.
r ESA
Co-Chairperson Bernie Acura
June 20,2016
Page 2
We would appreciate your comments identifying any sensitive sites in or near the project area that you may be
aware of,any concerns or issues pertinent to this project,or the names of others who may be interested in this
project.Thank you for your cooperation on this matter. If you have any questions or comments,please contact me
at 949.870.1524(cell)or abdelwahed@esassoc.com.
Sincerely,
Arabesque Said-Abdelwahed, MPP
Community Development
r ESA 2121 Mon Parkway .www.eeeeeoc.cnm
Suite 100
JIrvine,CA 92606
213.599.4300 phone
213.599.4301 fax
June 20,2016
Tribal Manager Joyce Perry
luanefio Band of Mission Indians Acjachemen Nation
4955 Paseo Segovia
Irvine,CA 92612
Subject: Groundwater Replenishment System Final Expansion Project—D160387.01
Dear Tribal Manager Perry:
ESA is conducting a cultural resources assessment as part of CEQA-Plus documentation for the Groundwater
Replenishment System(GWRS)Final Expansion Project(project)located in the cities of Huntington Beach and
Fountain Valley,California.The GWRS is an advanced water treatment facility constructed by the Orange
County Water District(OCWD)and the Orange County Sanitation District(OCSD)that supplements local water
supplies by providing reliable,high quality source of treated water to recharge the Orange County Groundwater
Basin and to protect the Orange County Groundwater Basin from seawater intrusion.The GWRS consists of
three major components: an advanced water purification facility and pumping stations,a major pipeline
connecting the treatment facilities to existing recharge basins and an existing seawater intrusion barrier.The
proposed project would include the construction and operation of an expanded microfiltration treatment facility,
expanded Reverse Osmosis Treatment Capacity,expanded ultraviolet light treatment facility at the existing
OCWD GWRS Facility in Fountain Valley. The project would also include construction and operation of a new
PUMP station at the OCSD Treatment Plant No.2 in Huntington Beach and the renovation of an existing water
supply pipeline located on the west side of the Santa Ana River. A separate headworks facility and a bypass
pipeline would be constructed on OCSD's Plant No. 2 that will segregate the brine flows from the typical
influent domestic wastewater flows to Plant No. 2. As seen on the attached topographic map,the project area is
located within multiple sections of Townships 5 and 6 south;Range 10 West of the United States Geologic
Survey(USGS)Newport Beach,CA 7.5' topographic quadrangle.
Section 106 of the National Historic Preservation Act of 1966(NHPA)considers the effects a project may have
on historic properties.The definition of"historic properties"can include properties of traditional religious and
cultural significance to Native American groups.To determine whether the proposed project may impact any
historic properties,including traditional cultural properties,ESA has reviewed background information and
consulted with the Native American Heritage Commission(NAHC). Our records search at the South Central
Coastal Information Center(SCCIC), indicate that there are no known cultural resources in the Area of Potential
Effect(APE). A record search of the NAHC's Sacred Land File has failed to indicate the presence of Native
American cultural resources in the immediate APE. The NAHC has listed you as a tribal contact for this project.
r ESA
Tribal Manager Joyce Perry
June 20,2016
Page 2
We would appreciate your comments identifying any sensitive sites in or near the project area that you may be
aware of,any concerns or issues pertinent to this project,or the names of others who may be interested in this
project.Thank you for your cooperation on this matter. If you have any questions or comments,please contact me
at 949.870.1524(cell)or a abdelwahed@esmsoc.com.
Sincerely,
4
Arabesque Said-Abdelwahed, MPP
Community Development
r ESA 2121 Mon Parkway .www.eeeeeoc.cnnn
Suite 100
JIrvine,CA 92606
213.599.6300 phone
213.599.6301 fax
June 20,2016
Co-Chairperson Linda Candelaria
Gabrielino-Tongva Tribe
1999 Avenue of the Stars
Suite 1100
Los Angeles,CA 90067
Subject: Groundwater Replenishment System Final Expansion Project—D160387.01
Dear Co-Chairperson Candelaria:
ESA is conducting a cultural resources assessment as part of CEQA-Plus documentation for the Groundwater
Replenishment System(GWRS)Final Expansion Project(project)located in the cities of Huntington Beach and
Fountain Valley,California.The GWRS is an advanced water treatment facility constructed by the Orange
County Water District(OCWD)and the Orange County Sanitation District(OCSD)that supplements local water
supplies by providing reliable,high quality source of treated water to recharge the Orange County Groundwater
Basin and to protect the Orange County Groundwater Basin from seawater intrusion.The GWRS consists of
three major components: an advanced water purification facility and pumping stations,a major pipeline
connecting the treatment facilities to existing recharge basins and an existing seawater intrusion barrier.The
proposed project would include the construction and operation of an expanded microfiltration treatment facility,
expanded Reverse Osmosis Treatment Capacity,expanded ultraviolet light treatment facility at the existing
OCWD GWRS Facility in Fountain Valley. The project would also include construction and operation of a new
pump station at the OCSD Treatment Plant No.2 in Huntington Beach and the renovation of an existing water
supply pipeline located on the west side of the Santa Ana River.A separate headworks facility and a bypass
pipeline would be constructed on OCSD's Plant No. 2 that will segregate the brine flows from the typical
influent domestic wastewater flows to Plant No. 2. As seen on the attached topographic map,the project area is
located within multiple sections of Townships 5 and 6 south;Range 10 West of the United States Geologic
Survey(USGS)Newport Beach,CA 7.5' topographic quadrangle.
Section 106 of the National Historic Preservation Act of 1966(NHPA)considers the effects a project may have
on historic properties.The definition of"historic properties"can include properties of traditional religious and
cultural significance to Native American groups.To determine whether the proposed project may impact any
historic properties,including traditional cultural properties,ESA has reviewed background information and
consulted with the Native American Heritage Commission(NAHC). Our records search at the South Central
Coastal Information Center(SCCIC),indicate that there are no known cultural resources in the Area of Potential
Effect(APE). A record search of the NAHC's Sacred Land File has failed to indicate the presence of Native
American cultural resources in the immediate APE.The NAHC has listed you as a tribal contact for this project.
r ESA
Co-Chairperson Linda Candelaria
June 20,2016
Page 2
We would appreciate your comments identifying any sensitive sites in or near the project area that you may be
aware of,any concerns or issues pertinent to this project,or the names of others who may be interested in this
project.Thank you for your cooperation on this matter. If you have any questions or comments,please contact me
at 949.870.1524(cell)or a abdelwahed@esmsoc.com.
Sincerely,
4
Arabesque Said-Abdelwahed, MPP
Community Development
r ESA 2121 Mon Parkway .www.eeeeeoc.cnnn
Suite 100
JIrvine,CA 92606
213.599.6300 phone
213.599.6301 fax
June 20,2016
Chairperson Andrew Salas
Gabrieleno Band of Mission Indians-Kizh Nation
P.O.Box 393
Covina,CA 91723
Subject: Groundwater Replenishment System Final Expansion Project—D160387.01
Dear Chairperson Salas :
ESA is conducting a cultural resources assessment as part of CEQA-Plus documentation for the Groundwater
Replenishment System(GWRS)Final Expansion Project(project)located in the cities of Huntington Beach and
Fountain Valley,California.The GWRS is an advanced water treatment facility constructed by the Orange
County Water District(OCWD)and the Orange County Sanitation District(OCSD)that supplements local water
supplies by providing reliable,high quality source of treated water to recharge the Orange County Groundwater
Basin and to protect the Orange County Groundwater Basin from seawater intrusion.The GWRS consists of
three major components: an advanced water purification facility and pumping stations,a major pipeline
connecting the treatment facilities to existing recharge basins and an existing seawater intrusion barrier.The
proposed project would include the construction and operation of an expanded microfiltration treatment facility,
expanded Reverse Osmosis Treatment Capacity,expanded ultraviolet light treatment facility at the existing
OCWD GWRS Facility in Fountain Valley. The project would also include construction and operation of a new
PUMP station at the OCSD Treatment Plant No.2 in Huntington Beach and the renovation of an existing water
supply pipeline located on the west side of the Santa Ana River. A separate headworks facility and a bypass
pipeline would be constructed on OCSD's Plant No. 2 that will segregate the brine flows from the typical
influent domestic wastewater flows to Plant No. 2. As seen on the attached topographic map,the project area is
located within multiple sections of Townships 5 and 6 south;Range 10 West of the United States Geologic
Survey(USGS)Newport Beach,CA 7.5' topographic quadrangle.
Section 106 of the National Historic Preservation Act of 1966(NHPA)considers the effects a project may have
on historic properties.The definition of"historic properties"can include properties of traditional religious and
cultural significance to Native American groups.To determine whether the proposed project may impact any
historic properties,including traditional cultural properties,ESA has reviewed background information and
consulted with the Native American Heritage Commission(NAHC). Our records search at the South Central
Coastal Information Center(SCCIC), indicate that there are no known cultural resources in the Area of Potential
Effect(APE). A record search of the NAHC's Sacred Land File has failed to indicate the presence of Native
American cultural resources in the immediate APE. The NAHC has listed you as a tribal contact for this project.
r ESA
Chairperson Andrew Salas
June 20,2016
Page 2
We would appreciate your comments identifying any sensitive sites in or near the project area that you may be
aware of,any concerns or issues pertinent to this project,or the names of others who may be interested in this
project.Thank you for your cooperation on this matter.If you have any questions or comments,please contact me
at 949.870.1524(cell)or a abdelwahed@esmsoc.com.
Sincerely,
4
Arabesque Said-Abdelwahed, MPP
Community Development
r ESA 2121 Mon Parkway .www.eeaeeoc.cnnn
Suite 100
JIrvine,CA 92606
213.599.6300 phone
213.599.6301 fax
June 20,2016
Conrad Acura
Gabrielino-Tongva Tribe
1999 Avenue of the Stars
Suite 1100
Los Angeles,CA 90067
Subject: Groundwater Replenishment System Final Expansion Project—D160387.01
Dear Conrad Acura:
ESA is conducting a cultural resources assessment as part of CEQA-Plus documentation for the Groundwater
Replenishment System(GWRS)Final Expansion Project(project)located in the cities of Huntington Beach and
Fountain Valley,California.The GWRS is an advanced water treatment facility constructed by the Orange
County Water District(OCWD)and the Orange County Sanitation District(OCSD)that supplements local water
supplies by providing reliable,high quality source of treated water to recharge the Orange County Groundwater
Basin and to protect the Orange County Groundwater Basin from seawater intrusion.The GWRS consists of
three major components: an advanced water purification facility and pumping stations,a major pipeline
connecting the treatment facilities to existing recharge basins and an existing seawater intrusion barrier.The
proposed project would include the construction and operation of an expanded microfiltration treatment facility,
expanded Reverse Osmosis Treatment Capacity,expanded ultraviolet light treatment facility at the existing
OCWD GWRS Facility in Fountain Valley. The project would also include construction and operation of a new
pump station at the OCSD Treatment Plant No.2 in Huntington Beach and the renovation of an existing water
supply pipeline located on the west side of the Santa Ana River.A separate headworks facility and a bypass
pipeline would be constructed on OCSD's Plant No. 2 that will segregate the brine flows from the typical
influent domestic wastewater flows to Plant No. 2. As seen on the attached topographic map,the project area is
located within multiple sections of Townships 5 and 6 south;Range 10 West of the United States Geologic
Survey(USGS)Newport Beach,CA 7.5' topographic quadrangle.
Section 106 of the National Historic Preservation Act of 1966(NHPA)considers the effects a project may have
on historic properties.The definition of"historic properties"can include properties of traditional religious and
cultural significance to Native American groups.To determine whether the proposed project may impact any
historic properties,including traditional cultural properties,ESA has reviewed background information and
consulted with the Native American Heritage Commission(NAHC). Our records search at the South Central
Coastal Information Center(SCCIC),indicate that there are no known cultural resources in the Area of Potential
Effect(APE). A record search of the NAHC's Sacred Land File has failed to indicate the presence of Native
American cultural resources in the immediate APE. The NAHC has listed you as a tribal contact for this project.
r ESA
Conrad Acuna
June 20,2016
Page 2
We would appreciate your comments identifying any sensitive sites in or near the project area that you may be
aware of,any concerns or issues pertinent to this project,or the names of others who may be interested in this
project.Thank you for your cooperation on this matter. If you have any questions or comments,please contact me
at 949.870.1524(cell)or a abdelwahed@esmsoc.com.
Sincerely,
4
Arabesque Said-Abdelwahed, MPP
Community Development
r ESA 2121 Mon Parkway .www.eeeeeoc.cnm
Suite 100
JIrvine,CA 92606
213.599.6300 phone
213.599.6301 fax
June 20,2016
Cultural Resources Director Sam Dunlap
Gabrielino/Tongva Nation
P.O.Box 86908
Los Angeles,CA 90086
Subject: Groundwater Replenishment System Final Expansion Project—D160387.01
Dear Cultural Resources Director Dunlap :
ESA is conducting a cultural resources assessment as part of CEQA-Plus documentation for the Groundwater
Replenishment System(GWRS)Final Expansion Project(project)located in the cities of Huntington Beach and
Fountain Valley,California.The GWRS is an advanced water treatment facility constructed by the Orange
County Water District(OCWD)and the Orange County Sanitation District(OCSD)that supplements local water
supplies by providing reliable,high quality source of treated water to recharge the Orange County Groundwater
Basin and to protect the Orange County Groundwater Basin from seawater intrusion.The GWRS consists of
three major components: an advanced water purification facility and pumping stations,a major pipeline
connecting the treatment facilities to existing recharge basins and an existing seawater intrusion barrier.The
proposed project would include the construction and operation of an expanded microfiltration treatment facility,
expanded Reverse Osmosis Treatment Capacity,expanded ultraviolet light treatment facility at the existing
OCWD GWRS Facility in Fountain Valley. The project would also include construction and operation of a new
PUMP station at the OCSD Treatment Plant No.2 in Huntington Beach and the renovation of an existing water
supply pipeline located on the west side of the Santa Ana River. A separate headworks facility and a bypass
pipeline would be constructed on OCSD's Plant No. 2 that will segregate the brine flows from the typical
influent domestic wastewater flows to Plant No. 2. As seen on the attached topographic map,the project area is
located within multiple sections of Townships 5 and 6 south;Range 10 West of the United States Geologic
Survey(USGS)Newport Beach,CA 7.5' topographic quadrangle.
Section 106 of the National Historic Preservation Act of 1966(NHPA)considers the effects a project may have
on historic properties.The definition of"historic properties"can include properties of traditional religious and
cultural significance to Native American groups.To determine whether the proposed project may impact any
historic properties,including traditional cultural properties,ESA has reviewed background information and
consulted with the Native American Heritage Commission(NAHC). Our records search at the South Central
Coastal Information Center(SCCIC), indicate that there are no known cultural resources in the Area of Potential
Effect(APE). A record search of the NAHC's Sacred Land File has failed to indicate the presence of Native
American cultural resources in the immediate APE. The NAHC has listed you as a tribal contact for this project.
r ESA
Cultural Resources Director Sam Dunlap
June 20,2016
Page 2
We would appreciate your comments identifying any sensitive sites in or near the project area that you may be
aware of,any concerns or issues pertinent to this project,or the names of others who may be interested in this
project.Thank you for your cooperation on this matter. If you have any questions or comments,please contact me
at 949.870.1524(cell)or a abdelwahed@esmsoc.com.
Sincerely,
4
Arabesque Said-Abdelwahed, MPP
Community Development
ESA 2121 Alton Parkway www.eeeeepc.cnnn
Suite 100
JIrvine,CA 92606
213.599.4300 phone
213.599.4301 fax
June 20,2016
Subject: Groundwater Replenishment System Final Expansion Project—D160387.01
Dear Sir or Madam, :
ESA is conducting a cultural resources assessment as part of CEQA-Plus documentation for the Groundwater
Replenishment System(GWRS)Final Expansion Project(project)located in the cities of Huntington Beach and
Fountain Valley,California.The GWRS is an advanced water treatment facility constructed by the Orange
County Water District(OCWD)and the Orange County Sanitation District(OCSD)that supplements local water
supplies by providing reliable,high quality source of treated water to recharge the Orange County Groundwater
Basin and to protect the Orange County Groundwater Basin from seawater intrusion.The GWRS consists of
three major components: an advanced water purification facility and pumping stations,a major pipeline
connecting the treatment facilities to existing recharge basins and an existing seawater intrusion barrier.The
proposed project would include the construction and operation of an expanded microfiltration treatment facility,
expanded Reverse Osmosis Treatment Capacity,expanded ultraviolet light treatment facility at the existing
OCWD GWRS Facility in Fountain Valley. The project would also include construction and operation of a new
PUMP station at the OCSD Treatment Plant No.2 in Huntington Beach and the renovation of an existing water
supply pipeline located on the west side of the Santa Ana River.A separate headworks facility and a bypass
pipeline would be constructed on OCSD's Plant No. 2 that will segregate the brine flows from the typical
influent domestic wastewater flows to Plant No. 2. As seen on the attached topographic map,the project area is
located within multiple sections of Townships 5 and 6 south;Range 10 West of the United States Geologic
Survey(USGS)Newport Beach,CA 7.5'topographic quadrangle.
Section 106 of the National Historic Preservation Act of 1966(NI-IPA)considers the effects a project may have
on historic properties.The definition of"historic properties"can include properties of traditional religious and
cultural significance to Native American groups. To determine whether the proposed project may impact any
historic properties,including traditional cultural properties,ESA has reviewed background information and
consulted with the Native American Heritage Commission(NAHC). Our records search at the South Central
Coastal Information Center(SCCIC),indicate that there are no known cultural resources in the Area of Potential
Effect(APE). A record search of the NAHC's Sacred Land File has failed to indicate the presence of Native
American cultural resources in the immediate APE.The NAHC has listed you as a tribal contact for this project.
We would appreciate your comments identifying any sensitive sites in or near the project area that you may be
aware of, any concerns or issues pertinent to this project,or the names of others who may be interested in this
project. Thank you for your cooperation on this matter.If you have any questions or comments,please contact me
at 949.870.1524(cell)or aabdelwahed@esmsoc.com.
Sincerely,
r ESA
Name of recipient
Date
Page 2
44�
Arabesque Said-Abdelwahed,MPP
Community Development
Native American Contact Log
Individual Contacted/Affiliation Number/Email Letter Sent Response Follow-up Phone Call Response Action Item
SW:Ms Joyce Stanfield-Perry(Cultural Resources);Recommends NA and Arc
Maths Belardes,Chairperson Juaneno monitoring during all ground disturbing activities.She also recommends that in
Band of Mission Indians,Acjachemen the event of a discovery,the project stop and the tribe and agency evaluates
Nation 949.293.8522 20-Jun-16 No response 28-Jun-16 the mitigation plan
Adolph Sepulveda,Vice-Chaiperson 714.914.1812/
Juaneno band of Mission Indians bssepul@yahoo.com 20-Jun-16 No response 28-Jun-16 Left VM.No response to date.
SW:Mr.Anthony Morales stated that he is very familiar with the Project area
and its vicinity,and he knows it to be very sensitive for Native American
cultural resources. Mr.Anthony Morales also stated that although that Project
Anthony Morales,Chairperson, is located within an industrial area,any ground disturbances may still
Gabrielino/Tongva San Gabriel Band of (626)483-3564/ encounter previously undisturbed soils and resources and should therefore be
Mission Indians GTTribalcouncil@aol.com 20-Jun-16 No response 28-Jun-16 closely monitored by a Native American monitor.
Sonia Johnston,Tribal Chairperson
Juaneno Band of Mission Indians sonia.johnston@sbcglobal.net 20-Jun-16 No response 28-Jun-16 Sent email.No response to date
Sandunne Goad,Chairperson, (951)807-0479/ SW:Ms.Sadonne Goad stated that she would prefer to forward all comments
Gabrielino/Tongva Nation sgoad@gabrielino=tongva.com 20-Jun-16 No response 28-Jun-16 to San Dunlap;No response from Mr.Dunlap
Bernie Acura,Co-Chairperson,
Gabrielino/Tongva Tribe 310A28.5690 20-Jun-16 No response 28-Jun-16 Left VM.No response to date.
Teresa Romero,Chairwoman,Juaneno
Band of Mission Indians Acjachemen 949.488.3484/
Nation tromero@juaneno.com 20-Jun-16 No resonse 28-Jun-16 Left VM.Ncrescnsetodate.
SW:MSJoyce Stan ie -Perry Cult
u tura Resources);Recommends NA and Arc
Joyce Perry,Tribal Manager,Juaneno monitoring during all ground disturbing activities.She also recommends that in
Band of Mission Indians Acjachemen 949.293.8522/ the event of a discovery,the project stop and the tribe and agency evaluates
Nation kaamalam@gmail.com 20-Jun-16 No response 28-Jun-16 the mitigation plan
Robert Dorame,Tribal Chair,Grarielino
To igva Indians of California Tribal 562.761.6417/ Forwarded a PDF copy of letter to
Council gton @verizon.net 20-Jun-16 No response 28-Jun-16 SW:Mr Dorame and he requested an email copy of the letterfor review gtongva@verizon.net on June 28,2016
Linda Candelaria,Co-Chairperson,
Gabrielino Ton va Tribe 626.676.1184 20-Jun-16 No response 28-Jun-16 Left VM.No response to date.
SW:Mr.Sa las and he recommends that NA and Arch monitoring be conducted
Andrew Salas,Chairperson,Gabrielino (626)9263131/ during all ground disturbance.He also requested a digital copy of the letter Forwarded a PDF copy of letter to
Band of Mission Indians-Kith Nation gabrielinoindia ns@ahoo.com 20-Jun-16 No response I 28-Jun-16 that was sent out. and alas07@ahoo.com on June 28,2016
Sam Dunlap,Cultural Resources Director, (909)262-9351/ Forwarded a PDF copy of the letter to
Gabrielino/Tongva Nation samdunlap@earthlink.net 20-Jun-16 No response 28-Jun-16SW:Mr Dunlap and he requested an email copy of the letter for review samdunlap@earthlink.net on June 28,2016
Conrad Acura,Gabriel in-Tongva Tribe 20-Jun-16 No response No contact info provide by the NAHC
SW=Spoke with
VM=Voicemail
Page 1 of 1
GAMIELENO BAND OF MISSION INDIAN5-KIZH NATION
3 2 Histordaa1196ownasT6e5an6a6relbandofM.�'ionlndian5
Recognized 69 the State of California as ebe akorig ail tn6e of the Los Angeles 6asin
NaCaN
Dear Vanessa Ortiz,
"The project locale lies in an area where the Ancestral 6 traditional territories of the Kizh(Kidc)Gabrielerho villages,adjoined and overlapped with each other,
at least during the Late Prehistoric and Protohistoric Periods.The homeland of the Kizh(Kitt)Gabrielenos,probably the most influential Native American
group in aboriginal southern California(Bean and Smith 1978a:538),was centered in the Los Angeles Basin,and reached as far east se the San Bernardino-
Riverside area. The homeland of the Sections;was primarily the San Bernardino Mountains,including the slopes and lowlands on the north and south
flanks.LVhateoer the linguistic affiliation,Native Americans in and around the project area exhibited similar organization and resource procurement
strategies. Villages were based on clan or lineage groups.Their home/base sites are marked by midden deposits,often with bedrock mortars.During their
seasonal rounds to exploit plant resources,small groups would migrate within their traditional territory in search of specific plants and animals.Their
gathering strategies often left behind signs ofspecial use sites,usually grinding slicks on bedrock boulders,at the locations of the resources. Therefore
in order to protect our resources we're requesting one of our experienced 6 certified Native American monitors as well as Arceo-Monitoring to be on
site during any 6 all ground disturbances (this includes but is not limited to pavement removal,pot-holing or auguring,haring,grading,
excavation and trenching).
In all cases,when the NAHC states there are"No" records of sacred sites"in the subject area;they always refer the contractors back to the Native American
Tribes whose tribal territory the project area is in. This is due to the fact,that the NAHC is only aware of general information on each California NA Tribe
they are"NOT" the"experts"an our Tribe. Our Elder Committee 6 Tribal Historians are the experts and is the reason why the NAHC will always refer
Contractors to the local tribes.
In addition,we are also often told that an area has been previously developed or disturbed and thus there are no concerns for cultural
resources and thus minimal impacts would be expected. I have two major recent examples of how similar statements on other projects were
proven very inadequate.An archaeological study claimed there would be no impacts to an area adjacent to the Plaza Church at Clasen Street,
the original Spanish settlement of Los Angeles, now in downtown Los Angeles.In fact, this site was the Gabrude vi village of Yangrw long
before it became what it is now today. The new development wrongfully began their construction and they,in the process, dug up and
desecrated 118 burials. The area that was dismissed as culturally sensitive was in fact the First Cemetery of Los Angeles where it had been
well documented at the Huntington Library that 400 of our Tribe's ancestors were buried there along with the founding families of Los
Angeles(Pico's,Sepulveda's,and Alvarado's to name a few).In addition, there was another inappropriate study for the development of a new
sports complex at Fedde Middle School in the City of Hawaiian Gardens could commence.Again,a village and burial site were desecrated
despite their mitigation measures. Thankfully,we were able to work alongside the school district to quickly and respectfully mitigate a
mutually beneficial resolution.
Given all the above, the proper thing to do for your project would be for our Tribe to monitor ground disturbing construction work. Native
American monitors and/or consultant can see that cultural resources are treated appropriately from the Native American point of view.
Because we are the lineal descendants of the vast area of Los Angeles and Orange Counties,we hold sacred the ability to protect what little of
our culture remains. We thank you for taking seriously your role and responsibility in assisting us in preserving our culture.
With respect,
Please contact our office regarding this project to coordinate a Native American Monitor to be present. Thank You
/r r.
Andrew Salo,Chairman
Cell(626)926-4131
Addendum:clarification regarding some confusions regarding consultation under AB52:
Andrew5alas,Chairman Nadine Silas,Vice Chairman Chrolne 5wlndall Martine,secretary
Apart Pere,treasured Martha Gonzalez temps,musurer ll Richard Gedias, cheirmanofthecouncilaf Elders
FOE>cm 393 Covina,CA 91723 ww,Qabdelenolndfartseduaboo.eom gabdelenotndvans@yaboo.com
AB52 dearly states that consultation must occur with tribes that claim traditional and cultural affiliation with a project site. Unfortunately, this statement
has been left open to interpretation so much that neighboring tribes are claiming affiliation with projects well outside their traditional tribal territory. The
territories of our surrounding Native American tribes such as the Luiseno,Chumash,and Cabuilla tribal entities. Each of our tribal territories has been well
defined by historians,ethnographers,archaeologists,and ethnographers-a list of resources we can provide upon request. Often,each Tribe as well educates
the public on their very awn website as to the definition of their tribal boundaries. You may have received a consultation request from another Tribe.
However we are responding because your project site lies within our Ancestral tribal territory,which,again,has been well documented.What does
Ancestrally or Ancestral mean?The people who were in your family in past times,Of,belonging to,inherited from,or denoting an ancestor or
ancestors httoyAmm,thefreedictionary.com/ancestral.. If you have questions regarding the validity of the"traditional and cultural affiliation"of another
Tribe,we urge you to contact the Native American Heritage Commission directly. Section 5 section 21080.3.1(c)states"...the Native American Heritage
Commission shull assist the lead agency in identifying the California Native American tribes that are traditionally and culturally affiliated with the project
men." In addition,please see the map below.
CC:NAHC
APPENDIX 1: Map 1.2; Bean and Smhh 1978 map.
Teach. is
na San
I� 4 CNu1Ba
r:=
skew Berm,i
V Fig. 1. Tribal territory.
The Unhul States National Museum's Map of(abnellno Territory:
Bean,Loren John and Charles R.South
1978 Cabnehno IN handbook of North American Indians.
Civilians,Vol.8,edited by R F.Had.,Smdhsonam
Institution Press. Washington.D.C.,pp.538 549
Andrew Sales,Chairman Nadine 5alaa,Vice Chairman Ch,olre 5wlndall Marina,secretary
Alhen Pere;treaau,erl Martha Gonnla lemm,mn,i,ar ll Richard Gndiaa, Cheirmanofthe[ouncidof Elders
PC)E>ox 393 Covina,CA 91723 gab wlenotcdvans@yahoo.�om
Sacred Lands File&Native American Contacts List Request
NATIVE AMERICAN HERITAGE COMMISSION
1550 Harbor Blvd, Suite 100
West Sacramento, CA 95691
(916) 373-3710
(916) 373-5471 —Fax
nahc@nahc.ca.gov
Information Below is Required for a Sacred Lands File Search
Project: Section 106 Cultural Resources Assessment for the Groundwater
Replenishment System Phase 3 Expansion
County: Orange
USGS Quadrangle Name: Newport Beach
Townships: 5 and 6 South---Range: 10 West Section(s): Multiple
Company: FirstCarbon Solutions
Contact Person: Arabesque Said, MPP
Street Address: 220 Commerce, Suite 200
Cell 951.310.7031
Office Phone: 714.508.4100
Fax: 714.508.4110
Email as needed: asaidabrandman.com
SEE ATTACHED MAP
The project will include the construction and operation of an expanded
microfiltration treatment facility, expanded reverse osmosis treatment facility,
expanded ultraviolet light treatment facilities at existing Orange County
Sanitations District's Treatment Plant No.2 in Huntington Beach and the
renovation of an existing water supply pipeline located on the west side of the
Santa Ana River. Excavation will be necessary to access the pipeline.
FCS' project 0435.0043
AVC
Is IN
Legend s�'i:— • — l � ♦ 4d3
Project Area 7 , m11■■/�1l
Plant Facilities - :77■� �\ - ,
--
3'6 — ExisUn9 Pipeline .AVE. - -�;T,yjrywi' -32 HI
0 Pipeline Entry Locations
�/ 4A •_ C^RAN .v[ Y I,� I $. '� a, _ JI_I
]n-NmEM
--_, __rwvE>u�.
at9nNGT,,. ACB nCONr n(LNDARY
,)S
MEMO L PA�
t - o .yas.owr L� ... yte >Vo a • >. N.. ..M _< ! I.
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9 ,E u� lad V . � E ..,Jj E
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ark
.P .
,
< • s ... I. _ .. 1
4J,t\ Op 6
es
i < .. > IA.J•r Ong Ca
` r \etvpnrt. Heights -
Source:TOPOI USGB Newport Beach,CA(19T8)7.5'DRG.
z,000 1.000 0 z,000 Local Vicinity Map
FlratCarbon' �
SOLUTIONS e Feet Topographic Base
0435OD43.08120141 local topo.maE OCWD•GARS PHASE III EXPANSION
CULTURAL RESOURCES ASSESSMENT
06/22/2014 14:45 FAX 916 657 5490 11Aa6 11001
ST ^FG'IFOXNIA
NATIVE AMERICAN HERITAGE COMMISSION
15604a w91ee.,seem IN
%e819ACRAMENTO.CA 05801
re16)V13 0'
F..(916)3 IWI
August 22,2014
Arabesque Said
First Carbon Solutions
220 Commerce, Suite 200
Irvine, CA 92602
Sent by Fax:(714)508-4110
Number of Pages!2
He:Project Section 106 Cultural Resources Assessment for the Groundwater Replenishment
System Phase 3 Expansion,Orange County.
Dear Mr. Said,
A record search of the sacred land file has failed to indicate the presence of Native American
cultural resources in the immediate project area. The absence of specific site information in the
sacred lands fge does not indicate the absence of cultural resources in any project area. Other
sources of cultural resources should also be contacted for information regarding known and
recorded sites.
Enclosed Is a list of Native Americans individuals/organizations who may have knowledge of -
cultural resources In the project area. The Commission makes no recommendation or
preference of a single individual, or group over another. This list should provide a starting place
in locating areas of potential adverse impact within the proposed project area. I suggest you
contact all of those indicated, if they cannot supply information, they might recommend others
with specific knowledge. By contacting all those listed, your organization will be better able to
respond to claims of failure to consult with the appropriate tribe or group. If a response has not
been received within two weeks of notification, the Commission requests that you follow-up with
a telephone call to ensure that the project information has been received.
It you receive notification of change of addresses and phone numbers from any of these
Individuals or groups, please notify me. With your assistance we are able to assure that our
lists contain current information. If you have any questions or need additional information,
please contact me et(916)373-3712.
Sinncce®reelly, i W
Katy Sanchez
Associate Government Program Analyst
08/22/2014 14:46 FAX 916 657 5390 NAHC Z004
Native American Contact List
Orange County
August 21,2014
Tongva Ancestral Territorial Tribal Nation Gabrielino-Tongva Tribe
John Tommy Rosas, Tribal Admin. - Linda Candelana, Co-Chairperson
Gabrielino Tongva P.O. Box 180 Gabrielino
tattnlawCgmail.com Bonsall CA92003
(310) 570-6567
(760) 636-0854 Fax
Gabdelenolfongva San Gabriel Band of Mission Gabrieleno Band of Mission Inds s
Anthony Morales, Chairperson ✓ Andrew Sales, Chairperson ,7
P.O. Box 693 Gabrielino Tongva P.O. Box 393 Gabrielino
San Gabriel CA 91778 Covina CA 91723
GTrrlbalmultcllOwl. m gabrielenoindfanstmyahoo.
(626) 489.3564 fall (626) 926.4131
(626)286-1262 Fax
Gabrialino/Tongva Nation Gabrielino-Tongva Tribe
Sandonne Goad, Chairperson Conrad Al
1061/2 Judge John Also St. Gabrielino Tongva P.O. Box 180 Gabrielino
Los Angeles , CA 90012 Bonsall , CA 92003
§gqDadQgabrielino.ton9vacorn (760) 636-0854 Fax
1y51) N7-0479
Gabrielino Tongva Indians of California Tribal Council Gabrielino/Toril Nation z
Robert F. Dorame, Tribal Chair/Cultural Resources Sam Dunlap, Cultural Resources Director,
P.O. Box 490 Gabrielino Tongva P.O. Box 86908 Gabrlellne,Tongva
Bellflower CA 90707 Los Angeles . CA 90086
�ton va@verizon.net 9amdunlap@earthlinknet
562y 761-6417 Voice/Fax (909)262-9351
Gabrielino-To vaTribe
Bernie Acuna, Co-Chairperson
P.O. Box 160 Gabrielino
Bonsall CA 920M
bacunal NO
(619)294- Office
(310)428-5690 Cell
(760) 636-0854 Fax
This list it current only as of the dateef this document.
Distribuion of this Ibt does not relieve any person of the statutory mSponsolay as defined in section 7090.5 tithe Health add9alaty Cede,
Section 0197.94 of Ma Public Resources Code and liestlon 5097.98 of the PublM Resources Code,
The list Is only applicable for cor9adtlng local Native Americana were Ward to clarinet resources ror the proposed Section 106 Call
Rosources Assessment for the Groundwater Replenishment System Phase 3 Expansion,Orange County.
North America I Europe I Australia 1 Asia FirstCarbon°
w ww.FirsiCarbo nSol orlon s.com / , S 0 L U T 10 N S
August 27, 2014 ,
Subject: Proposed Groundwater Replenishment System Phase 3 Expansion,5650 Ea enue, ' ies of Huntington
Beach and Fountain Valley,California (Newport Beach,CA USGS Topogr Quadr (.
Dear
FirstCarbon Solutions is completing CEQA-Plus documentation associat ith the propose e
Replenishment System Phase 3 Expansion Project located in the Cities of inVexpan
ountain Valley,
California.The proposed project will include the construction a eration icrofiltration treatment
facility, expanded reverse osmosis treatment facility,expand ultraviolet lightities at the existing
Orange County Water District GWRS Facility in Fountain V The project wou construction and
operation of a new pump station at the Orange County Sanitation District's (OCSD)Treatment Plant No.2 in Huntington
Beach and the renovation of an existing water supp eline on the west side of the Santa Ana River.As seen in
the attached topographic map,the project area is to d ithin iple sections of Townships 5 and 6 South; Range 10
West ofthe USGS Newport Beach,CA 7.5'topographi ua gle.
Section 106 of the National Historic Pres tion Act of 196 considers the effects a project may have on historic
properties.The definition of"historic prop 'can inclu properties of traditional religious and cultural significance
to Native American groups.To determine whe r the pro d project may impact any historic properties, including
traditional cultural properties, rolb&eviewed bac round information and consulted with the Native American
Heritage Commission(NAHC).O a ch at outh Central Coastal Information Center(SCCIC), indicated that
[here are no known cultural reso s In of►potential Effect(APE).A record search of the NAHC's Sacred Land
File has failed to Indic a prese ative American cultural resources in the immediate APE.The NAHC has listed
you as a tribal con is project
FCS is sending thiligetter to ask if h any information or concerns about this proposed project and/or if the
proposed project have an lm t on cultural resources that are important to you. Please
Please feel free to cent 14.509.4100 or via email at asaidPbrandman.com if you have any questions or would
like to discuss the project ore detail.
Sincerely,
Arabesque Said-Abdelwahed, MPP
Assistant Project Manager
FirstCarbon Solutions
220 Commerce,Suite 200
Irvine,CA 92602
Enclosures: Map of Survey Area
AVE •� /g 1..
T ..■. 4� r —4" —�iv.BErti ---.
t�L I —•' B i t� s •�■ $ �
Legend s�'i:— • — �� ♦ 483
Project Area 7 , .8
11■■1/1�l ti '
Plant Facilities - :77■� �\ - , i
3'6 Existing Pipeline .Ars.. - - ;T,ylryw�' -32 His
I
0 Pipeline Entry Locations
Nm•M
xt'unNcnnxi:ecB.. ncoNr n(LNMxx - i 'is i�
acst�
s o Ntwo .1111,w PA
n •l:r. tE '�
4A'
w� .'. e....:a. .y ycAq ' 1
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err JIB
• ,: Irr
x 0 " q " A, sir
�.
y
o �Nis
or
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Ns
_ 3n•
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pNI�II'I9Y I, O^� 5 I riAll
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� � f ' •
yh\ .�• C.SPi. 0 - .. _ AIL•. - '%
IN
es
i < .. > Is•.J•r Ong Ca
` r \e,port Heights
Source:TOPOI USGS Newport Beach,CA(1978)7.5'DRG.
2,000 1.000 0 2,000 Local Vicinity Map
�Fa°L°T'°N5 e MMMMMper+ Topographic Base
0435OD43.08120141 local topo.mmi OCWD•GARS PHASE III EXPANSION
CULTURAL RESOURCES ASSESSMENT
Call log
Listed Tribe to Contact Contact Name Phone number Call Date Call Time Notes Result JIM
Concerned about project because located wihthin a
sensiti�archaelogical area. Recommends testing
Cohn Tommy Roses 310. 570 6567 9/9/2014 am prior to exc"tion or full time archaeological and Returned FCS phone call
Tongue Acenstral Territorial Tribal Nation Nat!Ce American monitoring.
Concerned about the project because of its location
Anthony Morales 1626[483 3564 9/9/2014 4:14pm along the Santa Ana River. Suggested archaeological Returned FCS phone call
Gabrielenofrongle San Gabriel Band of Mission and paleontological monitoring.
Gabrielino/Tongle Nation Sandonne Goad [951 D807 0479 9/9/2014 4:15pm Referred to Sam Dunlap Answered FCSCphone call
Gabrielino Tongle Indians of California Tribal Council Robert F Dorame [562f1761[6417 9/9/2014 4:20pm FCS left a Coicemail
9/18/2014 3:OOpm No answer
Bernie Acuna 13100428156901aell
GabrielinoQongEe Tribe E519E294ES660®Nce 9/10/2014 1:45pm FCS left a [bicemail and sent an email
Gabrielino[TongEla Tribe 9/18/2014 3:02pm No answer
Gabdeleno Band of Mission Indians Linda Candelaria E626DB76EI184 9/9/2014 1:55pm FCS left a Coicemail
Mr. Sales expressed concerned about the project due
to its location in an archaeological sensitiDa area. Mr.
Gabrielino[TongEla Tribe Andrew Sales E62611926[4131 9/10/2014 1:56pm Sales suggested archaeological and Native American Answered FCSgthone call
monitoring take place to protect and preser:19 any
cultural resources that may be disco red during
excavations.
No phone
Conrad Acuna d60o636ED8541ax number or
email
Gabrielinolfongle Nation prodded
Sam Dunlap C9091262E9351 9/10/2014 2:15pm FCS left a voicemail. Mr. Dunlap prodded a response to FCS
❑a email on September 11
On September 11, 2014 Mr. Dunlap sent an email to
FCS. Mr. Dunlap expressed concerns about
construction and recommended archaeological and
Nati Ca American monitoring
Inventory List 9/19/2014
Ap Wlx D.PhoWgmpha 0 We PmJW APE
APPENDIX D
Photographs of the Project APE
GrcunEweler RePlenlehmenl syelem F dl EspenalN PNjed ene E8 11QpW 01
Wabr Pwdudim Enhan—t P-g AUO.2016
Ph—I CulWnl Re—SWEy
Photo 1: Excavation area and laydown area for OCSD Pipeline(pipeline entry location 1)
at the northern portion of the OCSD Plant No.2 Facility;facing north.
b
Y �I
Photo 2: View to the east of the rip rap and Santa Ana River Trail from the contractor laydown area.
SOURCE:ESA,2016 OCWD Groundwater Replenishment System Final Expansion Project.160387..01
..Jt? TF a l 't i
Photo 3: Pump Station and Pipe Connection;facing west.
1
Photo 4: Headgates and Bypass Pipeline location.
SOURCE:ESA,2016 OCWD Groundwater Replenishment System Final Expansion Project.160387..01
f
t•'
Photo 5: Flow EO Pump Station.The sur6cial soils were previously
disturbed during construction of the OCSD Plant No.2.
Photo 6: Flow EO MetedControl.
SOURCE:ESA,2016 OCWD Groundwater Replenishment System Final Expansion Project.160387..01
{
_s
Photo]: Secontl pipeline entry location along the OCSD easement corridor_
_ - 5,0. 3x 1:t
Photo 8: Santa Ma River Trail situated on the levee;view(acing east.
SOURCE:ESA,2016 DCWD Groundwater Replenishment System Final Expansion Project.160387..01
Photo 9: Third pipeline entry location along the OCSD easement corridor;facing south.
lur , '�',7tl,
Photo 10: Fourth pipeline entry location along the OCSD easement corridor;facing south.
SOURCE:ESA,2016 OCWD Groundwater Replenishment System Final Expansion Project.160387..01
Photo 11: Fifth pipeline entry location along the OCSD easement condor;facing north.
t j
f_
i
.�4r
. Y
Photo 12: Sixth pipeline entry location along the OCSD easement condor;facing southwest.
SOURCE:ESA,2016 OCWD Groundwater Replenishment System Final Expansion Project.160387..01
r
Photo 13: Seventh pipeline entry location along the OCSD easement Corridor;facing west.
f
Photo 14: Eighth pipeline entry location along the OCSD easement corridor.
SOURCE:ESA,2016 OCWD Groundwater Replenishment System Final Expansion Project.160387..01
Photo IS: OCSD Pipe Connection to existing facilities.Note the area is paved and previously disturbed
during construction of the facility.
Photo 16: MF Building Expansion location;facing west.
SOURCE:ESA,2016 OCWD Groundwater Replenishment System Final Expansion Project.160387..01
Appendix D
Noise and Vibration Technical Report
The OCWD Water Production Enhancement Project
Noise and Vibration Technical Report
Prepared for August 2016
Orange County Water District
18700 Ward St
Fountain Valley, CA 92708
r ESA
J
The OCWD Water Production Enhancement Project
Noise and Vibration Technical Report
Prepared for August 2016
Orange County Water District
18700 Ward St
Fountain Valley, CA 92708
sum,wnParkway r ESA
21211W
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Table of Contents
OCWD Water Production Enhancement Project
Noise and Vibration Technical Report
Paqe
ExecutiveSummary.................................................................................................................1
1. Introduction.....................................................................................................................2
1.1 Project Location......................................................................................................2
2. Project Description........................................................................................................4
3. Environmental Setting...................................................................................................7
3.1 Noise Principles and Descriptors............................................................................7
3.2 Noise Exposure and Community Noise..................................................................7
3.3 Effects of Noise on People....................................................................................10
3.4 Noise Attenuation..................................................................................................11
3.5 Fundamentals of Vibration....................................................................................12
3.6 Existing Conditions................................................................................................13
3.7 Regulatory Setting.................................................................................................15
4. Impacts and Mitigation Measures..............................................................................21
4.1 Methodology..........................................................................................................21
4.2 Thresholds of Significance....................................................................................22
4.3 Project Impacts ..................................................................................24
5. Conclusion....................................................................................................................29
6. References....................................................................................................................30
Appendices
A. Ambient Noise Data
B. Construction Noise Calculations
C. Off[Site Construction Traffic Noise Calculations
List of Figures
Figure 1 Vicinity Location Map 3
Figure 2 Proposed Site Plan 6
Figure 3 Decibel Scale and Common Noise Sources..............................................................9
Figure 4 Noise Measurement Locations................................................................................14
O WO Water PmduNon EManmrmnt Propel E&4I WU7.03
None and Maranon TeMnlcal Repot Mgni M18
OCW D Water Producdon Enhancement Protect.Noise and Mbladon Tmhnlcal Report
E.Wre Summary
List of Tables
Table 1 OCSD Flow EDualil ation Tank, Pump Station, 0 Pipeline/Meter Vault
Construction EDtipment Mix...................................................................................5
Table 2 OCSD Flow EDuall Oation Tank, Pump Station, 0 Pipeline/Meter Vault
Worker 0 Daily Trip Summary................................................................................5
Table 3 Summary of ambient noise meausrement...............................................................15
Table 4 Construction Vibration Damage Criteria..................................................................16
Table 5 Groundborne Vibration Impact Criteria for General Assessment............................17
Table 6 Caltrans Vibration Damage Potential Threshold Criteria 18
Table 7 Caltrans Vibration Annoyance Potential Criteria 19
Table 8 Huntington Beach Exterior Noise Standards...........................................................20
Table 9 Construction ED3ipment Noise LeEbls.....................................................................24
Table 10 Estimated Construction Noise Lelbls at Offsite Sensitil a Uses.............................25
Table 11 Vibration Source Levels for Construction EDiipment..............................................27
Table 12 Groundborne Vibration Lelels at Offsite Sensitise Uses Compared to
Caltrans-and FTA Vibration Damage Potential Threshold...................................28
OCWO Water PmduNon Enhammnent Propel II E 11W3e7.03
None and Maranon TeMnlcal Repot M M19
OCWD Water Production Enhancement Project
Noise and Vibration Technical Report
Executive Summary
The purpose of this Noise and Vibration Technical Report is to evaluate the potential short-and
long-term noise and vibration impacts resulting from implementation of the proposed Orange
County Water District(OCWD)Water Production Enhancement Project. The project site is
located at the Orange County Sanitation District(OCSD)Plant 2 wastewater treatment facility
site at 22212 Brookhurst Street within the City of Huntington Beach(City). The OCSD Plant 2
wastewater treatment facility site is bounded by Hamilton Avenue to the north,the Santa Ana
River(SAR)to the east,Pacific Coast Highway(PCH)to the south,and Brookhurst Street to the
west.OCSD Plant 2 wastewater treatment facility site is composed of 110 acres,and is developed
with wastewater treatment structures,offices,paved parking areas, and roadways.
Based on the assessment conducted in this report,ambient noise and vibration levels would not
substantially increase ambient noise levels as a result of the construction and operation of the
proposed project. Construction activities generate noise and vibration from the ground
disturbances caused by the usage of the equipment,and also by noise emanating from the exhaust
of these vehicles' motors. However,construction activities would not increase the ambient noise
levels by 5 dBA and would not exceed the identified vibration significance thresholds at noise
sensitive receptors.Operational noise would not result in the increase in ambient noise levels
from daily onsite operation of the proposed pump station.
The report summarizes the potential for the project to conflict with applicable noise and vibration
regulations,standards,and thresholds. The findings of the analyses are as follows:
• The noise levels from construction of the project would not exceed the significance
threshold of 71 dBA at the nearest single-family residential uses west of the project site.
Therefore, impacts would be less than significant.
• Construction activities would result in sporadic, temporary vibration effects adjacent to
the project area, which would not exceed established thresholds for structures. Thus,
construction vibration impacts to structures would be less than significant.
• Operation of the project would result in less than significant noise and vibration impacts
to off-site noise sensitive receptors.
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Noise and Vni Testnioad Rai August 2016
OCW D Water Produdon Enhancement Project Noise aM Vlbm lon Tmhnlcal Report
1, Introdudon
1 . Introduction
This technical report has been prepared to support the Orange County Water District's(OCWD)
environmental review process and provide information regarding potential impacts to ambient
noise and vibration associated with the approval of the Water Production Enhancement Project
(project). The project consists of the installation of a secondary fluent flow equalization storage
tank at the Orange County Sanitation District's(OCSD)Plant No. 2 to receive maximum water
production at the Groundwater Replenishment System(GWRS)facility.OCSD's Plant No. 2 is a
wastewater treatment facility,which has varying influent(and effluent)flows of secondary
treated effluent.During the day,wastewater flows into OCSD's Plant No.2 can peak above 140
million gallons per day(MGD).These peak flows cannot be pumped to the GWRS facility due to
the limits of the conveyance facilities, i.e.effluent pump station and pipeline;that deliver the
secondary effluent to GWRS. Therefore,a secondary effluent flow equalization storage tank has
been proposed at OCSD's Plant No.2 to capture these peak flows during the day and store them
in the 6-million gallon tank until nighttime.During low flows at night,the flow equalization tank
would drain into the effluent pump station to supplement the low secondary effluent inflows and
allow the GWRS to treat these peak flows which would have otherwise been discharged to the
Pacific Ocean. This secondary effluent flow equalization storage tank is expected to deliver an
additional 6,000 acre-feet of secondary effluent for treatment at the GWRS facility.
This report describes the existing ambient noise in the project area, identifies applicable noise
regulations,and evaluates potential short-and long-term noise impacts associated with the build-
out of the project.Additionally,this report provides background information on vibration and
evaluates potential impacts associated with the project's contribution to ambient vibration levels.
Where applicable,measures to mitigate or minimize noise and vibration impacts associated with
the project are included.
Information used to prepare this analysis was obtained from the OCWD,the City of Huntington
Beach General Plan and Noise Ordinance, and other sources identified herein.
1 .1 Project Location
The OCSD Plant 2 wastewater treatment facility site is located at 22212 Brookhurst Street within
the City of Huntington Beach.The OCSD Plant 2 wastewater treatment facility site is bounded by
Hamilton Avenue to the north,the Santa Ana River(SAR)to the east,Pacific Coast Highway
(PCH)to the south,and Brookhurst Street to the west.OCSD Plant 2 wastewater treatment
facility site is composed of 110 acres,and is developed with wastewater treatment structures,
offices,paved parking areas,and roadways. Specifically,the project is located in the City of
Huntington Beach as shown in Figure 1,Vicinity Location Map.
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0 O Wader Produdon Enhancement Project Noise and Mimi Tednlcal Repoli
2, Proi Oesdptlon
2. Project Description
The Water Production Enhancement Project involves three construction activities: 1)construction
of flow equalization tank,2)construction of a pump station,and 3)construction of conveyance
piping and flow meter vault. The improvements proposed in the Water Production Enhancement
Project are shown in Figure 2,Proposed Site Plan.
A 6-million gallon(MG)flow equalization storage tank would be constructed at the north end of
OCSD Plant 2.The location of the flow equalization storage tank is shown in Figure 2. The
storage tank would be a circular-welded steel tank approximately 200-feet in diameter and 30-feet
tall from existing grade,with a 4-pump(3 duty+ 1 standby),pump station,and approximately
500-linear feet of 36-inch diameter connection piping with a meter vault(15-x 20-x 10-ft deep)
connected to the operations of the tank.The pump station would be housed in a 30-x 40-x 20-ft
block wall building.
The site preparation work for the flow equalization storage tank,pump station, and pipeline/vault
would involve excavating and hauling approximately 1,000 cubic yards(CY)of soil. In addition
to soil removal, an existing concrete parking lot would need to be demolished for the tank pad.
For this excavation work, four dump trucks would be required for five round trips each over a
period of 4 days to haul the soil off-site.For the demolition work, four dump trucks would be
required for three round trips each over a period of 14 days to haul the concrete/asphalt offsite.
The flow equalization storage tank would be constructed on concrete piles.Approximately 30-
piles would be required for supporting the tank. To construct the pilings, 12-inch diameter holes
would be drilled into the ground with an auger drill rig.Approximately 40 CY of soil from pile
drilling activity would be removed. Once the pile drilling is completed,the rebar support cages
for the piles would be installed into the drilled holes with a crone.Approximately 40 CY of
concrete would be Filled into the holes with the rebar and cured. The piles would be supporting a
2-foot thick concrete pad matching the diameter of the tank. This equates to 2,330 CY of concrete
for the tank pad.The pump station and meter vault would also require approximately 100 CY of
concrete to construct these structural facilities.
Once the piles and concrete pad have been constructed,the steel tank would be assembled.A
crane and welding laborers would be required to weld the steel components of the tank together.
Once the tank is welded,the surface would be prepped for a base coat and finally painted.
While the tank is being assembled,the contractor would be equipping the pump station and meter
vault with the use of laborers,fork lifts and cranes. The construction equipment for the tank,
meter vault,flow diversion box and pump station would include; an excavator,crane,pile driller,
bull dozer,backhoe,compactor,dump trucks,concrete trucks,water truck,man lifts and fork
lifts.The mix of construction equipment and hours of operation for each of the phases are shown
in Table 1,OCSD Flow Equalization Tank,Pump Station,&Pipeline/Meter Vault
Construction Equipment Mix. The daily haul trips and laborer estimates are shown in Table 2,
OCSD Flow Equalization Tank,Pump Station,&Pipeline/Meter Vault Worker Daily Trip
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Noise and Vni Teohniml Rei nu9uet 2016
OCWD Water Production Enhancement Project Noise and Vibration Technical Report
2, Project Description
Summary. The OCWD Water Production Enhancement Project would be implemented in five
construction phases beginning in August 2020 and concluding in December of 2022.
TABLE 7
OCSD FLOW EQUALIZATION TANK,PUMP STATION,$PIPELINE/METER VAULT CONSTRUCTION EQUIPMENT MIX
Equipment Time Total Total HP
Activity Equipment Description Quantity (Hrs/Day) (Days) (Hours) Rating
Bull Doter 2 6 30 360 250
Compactor 1 6 10 60 200
OCSD Flow E per such Tank,Pump ExcaOrtor 2 6 20 240 200
Station,Meter Vault Pipeline AAA Dump Trucks 4 6 4 96 350
Demo Dump Trucks 4 6 14 336 350
Water Trucks 1 8 45 360 350
Drill Rig 1 6 20 120 500
Backhoe 1 6 20 120 150
OCSD Flow E]dali[htion Tank Piles Concrete Trucks 1 5 3 15 350
]B�
Dump Trucks 2 5 3 30 350
Water Truck 2 4 25 200 350
Crane 1 5 5 25 300
OCSD Flow E]ali[htion Tank Pad Forklift 2 6 5 60 120
11CO
Concrete Trucks 4 5 24 480 350
Crane 1 6 10 60 300
OCSD Flow EyaliAnion Tank Forklift 4 6 30 720 120
Assembly�Coating ADO
Man Lift 5 6 15 450 75
Crane 1 6 10 60 300
OCSD Flow E]ali Aa ion Pump Station Forklift 4 6 30 720 120
❑Meter Vault Equipment D E�
Man Lift 5 6 15 450 75
SOURCE:OCWD,2016
TABLE 2
OCSD FLOW EQUALVATION TANK,PUMP STATION,&PIPELINE/METER VAULT WORKER&DAILY TRIP SUMMARY
Activity Worker Vendor Daily Haul Trips Total Haul Trips
1 A:ExciHauling,Grading for Flow E A.eli Anion Tank, 10 1 32 248
Pump Station,and Pipeline
I :Piles Construction for Flow Roundioation Tank 10 2 4 12
1C:Flow E[uali ation Tank Pad Construction 10 2 12 288
1D:Flow EOurialion Tank Assembly O Coating 5 2 m
1E:Assembly of Flow EA.aliDgion Pumps and Meter Vault 5 4 m
SOURCE:DOWD,2016
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SOURCE:county of orange Water District,2016 Figure 2
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OC ND Water Production Enhancement Project.Noise and Vlbmibn Technical Rerwa
3. Enlronmental3eaing
3. Environmental Setting
3.1 Noise Principles and Descriptors
Sound can be described as the mechanical energy of a vibrating object transmitted by pressure
waves through a liquid or gaseous medium(e.g.,air).Noise is generally defined as unwanted
sound(i.e., loud,unexpected,or annoying sound).Acoustics is defined as the physics of sound. In
acoustics,the fundamental scientific model consists of a sound(or noise)source,a receiver,and
the propagation path between the two.The loudness of the noise source and obstructions or
atmospheric factors affecting the propagation path to the receiver determines the sound level and
characteristics of the noise perceived by the receiver.Acoustics addresses primarily the
propagation and control of sound.
Sound,traveling in the form of waves from a source,exerts a sound pressure level (referred to as
sound level)that is measured in decibels(dB),which is the standard unit of sound amplitude
measurement.The dB scale is a logarithmic scale that describes the physical intensity of the
pressure vibrations that make up any sound,with 0 dB corresponding roughly to the threshold of
human hearing and 120 to 140 dB corresponding to the threshold of pain.Pressure waves
traveling through air exert a force registered by the human ear as sound.
Sound pressure fluctuations can be measured in units of hertz(Hz),which correspond to the
frequency of a particular sound.Typically,sound does not consist of a single frequency,but
rather a broad band of frequencies varying in levels of magnitude.When all the audible
frequencies of a sound are measured,a sound spectrum is plotted consisting of a range of
frequency spanning 20 to 20,000 Hz. The sound pressure level,therefore,constitutes the additive
force exerted by a sound corresponding to the sound frequency/sound power level spectrum.
The typical human ear is not equally sensitive to all frequencies of the audible sound spectrum.
As a consequence,when assessing potential noise impacts,sound is measured using an electronic
filter that deemphasizes the frequencies below 1,000 Hz and above 5,000 Hz in a manner
corresponding to the human ear's decreased sensitivity to extremely low and extremely high
frequencies.This method of frequency weighting is referred to as A-weighting and is expressed
in units of A-weighted decibels(dBA).A-weighting follows an international standard
methodology of frequency deemphasis and is typically applied to community noise
measurements. Some representative common outdoor and indoor noise sources and their
corresponding A-weighted noise levels are shown in Figure 3,Decibel Scale and Common
Noise Sources.
3.2 Noise Exposure and Community Noise
An individual's noise exposure is a measure of noise over a period of time. A noise level is a
measure of noise at a given instant in time. The noise levels presented in Figure 3 are
representative of measured noise at a given instant in time;however,they rarely persist
consistently over a long period of time. Rather, community noise varies continuously over a
period of time with respect to the contributing sound sources of the community noise
ocwo waur Pmdunlon Enhi Rgp<t 7 E&A1160361oa
Noise and VIi Tashniwl Repot August 2016
OCW D Water Productlon Enhancement Project Noise and Mai Technical PMod
3. Enlronnn.WISetdng
environment. Community noise is primarily the product of many distant noise sources,which
constitute a relatively stable background noise exposure,with the individual contributors
unidentifiable.The background noise level changes throughout a Typical day,but does so
gradually, corresponding with the addition and subtraction of distant noise sources such as traffic.
What makes community noise variable throughout a day,besides the slowly changing
background noise,is the addition of short-duration, single-event noise sources(e.g.,aircraft
flyovers,motor vehicles, sirens),which are readily identifiable to the individual.
These successive additions of sound in the community noise environment change the community
noise level from instant to instant,requiring the measurement of noise exposure over a period of
time to legitimately characterize a community noise environment and evaluate cumulative noise
impacts.This time-varying characteristic of environmental noise is described using statistical noise
descriptors.The most frequently used noise descriptors are summarized below:
Leg: The equivalent sound level,is used to describe noise over a specified period of time in terms
of a single numerical value;the L,of a time-varying signal and that of a steady signal
are the same if they deliver the same acoustic energy over a given time. The Leg may also
be referred to as the average sound level.
Los: The maximum,instantaneous noise level experienced during a given period of time.
Lien: The minimum,instantaneous noise level experienced during a given period of time.
L,: The noise level exceeded a percentage of a specified time period. For instance,Lho and
Lv6 represent the noise levels that me exceeded 50 percent and 90 percent of the time,
respectively.
Lan: the average A-weighted noise level during a 24-hour day,obtained after an addition of 10 dB
to measured noise levels between the hours of 10:00 p.m.to 7:00 a.m.to account nighttime
noise sensitivity.The Len is also termed the day-night average noise level(DNL).
CNEL: The Community Noise Equivalent Level(CNEL) is the average A-weighted noise level
during a 24-hour day that is obtained after an addition of 5 dB to measured noise levels
between the hours of 7:00 a.m,to 10:00 p.m. and after an addition of 10 dB to noise
levels between the hours of 10:00 p.m,to 7:00 a.m.to account for noise sensitivity in the
evening and nighttime,respectively.
ocwo Water Pmdunlon Enhanonrem Pgp01 8 ESAI tec36]06
Noise and Vni Te hassid Reim August 2016
COMMON OUTDOOR ACTIVITIES COMMON INDOOR ACTIVITIES
Rock band
Jet Flyover at 1,000 feet
rt
Gas lawnmower at 3 feet
Diesel truck at 50 feet at 50 mph Food blender at 3 feet
' Garbage disposal at 3 feet
Noisy urban area,daytime
Gas lawnmower, 100 feet Vacuum cleaner at 10 feet
Commercial area Normal speech at 3 feet
Heavy traffic at 300 feet '
Large business office
Quiet urban daytime Dishwasher in next room
Quiet urban nighttime ' Theater,large conference room
(background)
Quiet suburban nighttime
Library
Quiet rural nighttime Bedroom at night, concert hall
(background)
Broadcast/recording studio
NOISE LEVEL
(d BA)
Water Production Enhancement Project.160387
SOURCE:CalVans
Figure 3
Decibel Scale and Common Noise Sources
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DCW D Watar Produdon Enhancement Prole Noise and Vlblagon Technical Repoli
3. EnlronmmtalaeWng
3.3 Effects of Noise on People
Noise is generally loud, unpleasant, unexpected, or undesired sound that is typically associated
with human activity that is a nuisance or disruptive. The effects of noise on people can be placed
into four general categories:
• Subjective effects(e.g.,dissatisfaction,annoyance);
• Interference effects(e.g.,communication, sleep,and learning interference);
• Physiological effects(e.g., startle response);and
• Physical effects(e.g.,hearing loss).
Although exposure to high noise levels has been demonstrated to cause physical and
physiological effects,the principal human responses to typical environmental noise exposure are
related to subjective effects and interference with activities. Interference effects of environmental
noise refer to those effects that interrupt daily activities and include interference with human
communication activities, such as normal conversations,watching television,telephone
conversations,and interference with sleep. Sleep interference effects can include both awakening
and arousal to a lesser state of sleep.With regard to the subjective effects, the responses of
individuals to similar noise events are diverse and are influenced by many factors,including the
type of noise,the perceived importance of the noise,the appropriateness of the noise to the
setting,the duration of the noise,the time of day and the type of activity during which the noise
occurs,and individual noise sensitivity.
Overall,there is no completely satisfactory way to measure the subjective effects of noise,or the
corresponding reactions of annoyance and dissatisfaction on people.A wide variation in
individual thresholds of annoyance exists,and different tolerances to noise tend to develop based
on an individual's past experiences with noise. Thus,an important way of predicting a human
reaction to a new noise environment is the way it compares to the existing environment to which
one has adapted(i.e.,comparison to the ambient noise environment).In general,the more a new
noise level exceeds the previously existing ambient noise level,the less acceptable the new noise
level will be judged by those hearing it.With regard to increases in A-weighted noise level,the
following relationships generally occur:
• Except in carefully controlled laboratory experiments, a change of 1 dBA cannot be
perceived;
• Outside of the laboratory, a 3 dBA change in noise levels is considered to be a barely
perceivable difference;
• A change in noise levels of 5 dBA is considered to be a readily perceivable difference;
and
• A change in noise levels of 10 dBA is subjectively heard as doubling of the perceived
loudness.
ocWp Water PmEuglon Enesonenl Pmpcl 10 ii 411608/03
Noise and Vni Teniniul Repal Augus12016
OC ND Water Produedon Enhancement Project Noise and Mbmllon Technical Report
3. En ironmental Setting
These relationships occur in part because of the logarithmic nature of sound and the decibel scale.
The human ear perceives sound in a non-linear fashion hence the dB scale was developed.
Because the dB scale is based on logarithms,two noise sources do not combine in a simple
additive fashion,but rather logarithmically.Under the dB scale, a doubling of sound energy
corresponds to a 3 dBA increase.In other words,when two sources are each producing sound of
the same loudness,the resulting sound level at a given distance would be approximately 3 dBA
higher than one of the sources under the same conditions.For example,if two identical noise
sources produce noise levels of 50 dBA,the combined sound level would be 53 dBA,not 100
dBA.Under the dB scale,three sources of equal loudness together produce a sound level of
approximately 5 dBA louder than one source,and ten sources of equal loudness together produce
a sound level of approximately 10 dBA louder than the single source.
3.4 Noise Attenuation
When noise propagates over a distance, it changes in level and frequency content.The manner in
which noise reduces with distance depends on factors such as the type of noise source and the
propagation path.Noise from a localized source(i.e.,point source)propagates uniformly outward
in a spherical pattern;therefore,this type of propagation is referred to as"spherical spreading."
Stationary point sources of noise,including stationary mobile sources such as idling vehicles,
attenuate(lessen)at a rate between 6 dBA for acoustically"hard"sites and 7.5 dBA for"soft"
sites for each doubling of distance from the reference measurement as their energy is continuously
spread out over a spherical surface. Hard sites are those with a reflective surface between the
source and the receiver,such as asphalt or concrete surfaces or smooth bodies of water. No excess
ground attenuation is assumed for hard sites and the changes in noise levels with distance(drop-
off rate)is simply the geometric spreading of the noise from the source. Soft sites have an
absorptive ground surface such as soft dirt, grass,or scattered bushes and trees. In addition to
geometric spreading, an excess ground attenuation value of 1.5 dBA(per doubling distance)is
normally assumed for soft sites.
Roadways and highways consist of several localized noise sources on a defined path,and hence
are treated as`line"sources,which approximate the effect of several point sources.Noise from a
line source propagates over a cylindrical surface,often referred to as"cylindrical spreading."
Line sources(e.g.,traffic noise from vehicles)attenuate at a rate between 3 dBA for hard sites
and 4.5 dBA for soft sites for each doubling of distance from the reference measurement.)
Therefore,noise due to a line source attenuates leas with distance than that of a point some with
increased distance.
Additionally,receptors located downwind from a noise source can be exposed to increased noise
levels relative to calm conditions,whereas locations upwind can have lowered noise levels.
Sound levels can be increased at large distances(e.g.,more than 500 feet)due to atmospheric
temperature inversion(i.e.,increasing temperature with elevation). Other factors such as air
temperature,humidity,and turbulence can also have significant effects.
1 Califomia Department of Transportation(Caltrans),Technical Noun,Supplement(TeNS).September,2013,
OCWO WaKr Pmdsocn Enhancement Pnaed tt EZA 1160810a
Noise and Vlbm4an Tsui Issi Augus12016
01 Water Prodadon Enhancement ProlimM Noise and Vlbragon Tmhnlcal Repoli
3. En'loamental Setting
3.5 Fundamentals of Vibration
Vibration can be interpreted as energy transmitted in waves through the ground or man-made
structures.These energy waves generally dissipate with distance from the vibration source.
Because energy is lost during the transfer of energy from one particle to another,vibration
becomes less perceptible with increasing distance from the source.
As described in the Federal Transit Administration's(FTA) Transit Noise and Nlbration Impact
Assessment,ground-borne vibration can be a serious concern for nearby neighbors of a transit
system route or maintenance facility,causing buildings to shake and rumbling sounds to be
heard.2 In contrast to airborne noise,ground-borne vibration is not a common environmental
problem. It is unusual for vibration from sources such as buses and trucks to be perceptible,even
in locations close to major roads. Some common sources of ground-borne vibration are trains,
heavy trucks traveling on rough roads,and construction activities such as blasting,pile-driving,
and operation of heavy earth-moving equipment.
There are several different methods that are used to quantify vibration. The peak particle velocity
(Pi is defined as the maximum instantaneous peak of the vibration signal.The Pi is most
frequently used to describe vibration impacts to buildings.The root mean square(RMS)
amplitude is most frequently used to describe the effect of vibration on the human body. The
RMS amplitude is defined as the average of the squared amplitude of the signal.Decibel notation
(VdB)is commonly used to measure RMS.The relationship of Pi to RMS velocity is expressed
in terms of the`crest factor,"defined as the ratio of the Pi amplitude to the RMS amplitude.
Pi is typically a factor of 1.7 to 6 times greater than RMS vibration velocity.3 The decibel
notation acts to compress the range of numbers required to describe vibration.Typically,ground-
home vibration generated by man-made activities attenuates rapidly with distance from the source
of the vibration. Sensitive receptors for vibration include structures(especially older masonry
structures),people(especially residents,the elderly, and sick),and vibration sensitive equipment.
The effects of ground-borne vibration include movement of the building floors,rattling of
windows,shaking of items on shelves or hanging on walls,and rumbling sounds. In extreme
cases,the vibration can cause damage to buildings. Building damage is not a factor for most
projects,with the occasional exception of blasting and pile-driving during construction.
Annoyance from vibration often occurs when the vibration levels exceed the threshold of
perception by only a small margin.A vibration level that causes annoyance will be well below the
damage threshold for normal buildings.The FTA measure of the threshold of architectural
damage for conventional sensitive structures is 0.2 in/sec PPV.4
In residential areas, the background vibration velocity level is usually around 50 VdB
(approximately 0.0013 in/sec PPV).This level is well below the vibration velocity level threshold
of perception for humans,which is approximately 65 VdB.A vibration velocity level o£75 VdB
2 FrA,2006.Transit Noise and Vibration Impact Assessment May.
3 Ibid.
4 Ibid.
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3. En ironmcntal Seain,
is considered to be the approximate dividing line between barely perceptible and distinctly
perceptible levels for many people.5
3.6 Existing Conditions
Some land uses are considered more sensitive to ambient noise levels than others are,due to the
amount of noise exposure(in terms of both exposure duration and insulation from noise)and the
types of activities typically involved. According to the General Plan,residential areas are to be
the most sensitive type of land use to noise and industrial/commercial areas are considered to be
the least sensitive. Existing noise sensitive uses in the vicinity of the project site include the
following:
• Residential Uses: single-family residences and multi-family residential uses are located to
the west and north of the project site along Brooldrurst Street.
Ambient Noise Levels
The predominant existing noise source surrounding the project site is roadway noise from
Brookhurst Street to the west.
Ambient noise measurements were conducted at two locations,representing the nearby land uses
in the vicinity of the project site to establish conservative ambient noise levels. The measurement
locations along with existing development and nearby future development are shown on Figure
4,Noise Measurement Locations. Long-term(24-how)measurements were conducted at
locations Rl and R2. Ambient sound measurements were conducted on Wednesday,July 13,
2016,to characterize the existing noise environment in the project vicinity.
The ambient noise measurements were conducted using the Larson-Davis 820 Precision
Integrated Sound Level Meter("SLM'). The Larson-Davis 820 SLM is a Type 1 standard
instrument as defined in the American National Standard Institute SI A. All instruments were
calibrated and operated according to the applicable manufacturer specification. The microphone
was placed at a height of 5 feet above the local grade,at the following locations as shown in
Figure 4:
• Measurement Location RL represents the existing noise environment of single-family
residential uses west of the project site along Brookhurst Street. The SLM was placed on
the west of the project site along Brookhurst Street.
• Measurement Location R2: represents the existing noise environment of multi-family
residential uses north of the project site along Brookhmst Street. The SLM was placed
on the southwestern boundary of the multi-family residential uses along Brookhmst
Street.
5 Ibid.
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Noise and Vni Teohnical Report nu9u.2016
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SOURCE:County of Orange Water District,2016;ESA,2016 Figure 4
Noise Measurement Locations
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3. Enlionments Seding
TABLE 3
SUMMARY OF AMBIENT NOISE MEAUSREMENT
Daytime Daytime Nighttime Nighttime 24-Hour
Location,Duration,Existing Land Uses (7 A.M.to 10 P.M.) Average (10 P.M.to 7 A.M.) Average Average,
and,Date of Measurements Hourly L,a Hourly L,a Hourly L,a Hourly L,a CNEL
R1 0 SingleUamily Residential Uses 66 069 67 56 067 61 69
7/13/16124 hour2ldCetlnesday
R2 0 Multidamily Residenfial Uses 66 o70 69 56 066 62 71
7113/16 24 hour Ndednesday
SOURCE:ESA,2016
A summary of noise measurement data is provided in Table 3,Summary of Ambient Noise
Measurements. As shown in Table 3,the existing ambient daytime noise levels ranged from
66 dBA to 69 dBA,Lag, at Rl and from 68 dBA to 70 dBA,Lag at R2. The existing ambient
nighttime noise levels ranged from 56 dBA to 67 dBA,Leg at Rl and from 58 dBA to 66 dBA, Leg
at R2.
Existing Groundborne Vibration Levels
Aside from periodic construction work that may occur throughout the City, other sources of
groundbome vibration in the project site vicinity may include heavy-duty vehicular travel(e.g.,
refuse trucks,delivery trucks,etc.)on local roadways.Truck traffic at a distance of 50 feet
typically generate groundbome vibration velocity levels of approximately 63 VdB (approximately
0.006 in/sec PPV),and these levels could reach 72 VdB (approximately 0.016 ini PPV)where
trucks pass over irregularities in the road surface.6
3.7 Regulatory Setting
Detailed below is a discussion of the relevant regulatory setting and noise regulations,plans,and
policies.
Federal
Federal Noise Standards
Under the authority of the Noise Control Act of 1972,the United States Environmental Protection
Agency(USEPA)established noise emission criteria and testing methods published in Parts 201
through 205 of Title 40 of the Code of Federal Regulations(CFR)that apply to some
transportation equipment(e.g.,interstate rail carvers,medium trucks, and heavy trucks) and
construction equipment. In 1974, the USEPA issued guidance levels for the protection of public
health and welfare in residential land use areas]of an outdoor Lda of 55 dBA and an indoor Ld„of
45 dBA. These guidance levels are not considered as standards or regulations and were developed
6 FTA,Transit Noise and Vibration Impact Assessment.May 2006.
7 USEPA,EPA Idenhfres Noise Levels Affecting H.hhond Welfore.April 1974,
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3. Enlronmental Selling
without consideration of technical or economic feasibility.There are no federal noise standards
that directly regulate environmental noise related to the construction or operation of the project.
Under the Occupational Safety and Health Act of 1970(29 U.S.C. §1919 et seq.),the
Occupational Safety and Health Administration(OSHA)has adopted regulations designed to
protect workers against the effects of occupational noise exposure. These regulations list
permissible noise level exposure as a function of the amount of time during which the worker is
exposed.The regulations further specify a hearing conservation program that involves monitoring
the noise to which workers are exposed,ensuring that workers are made aware of overexposure to
noise, and periodically testing the workers' hearing to detect any degradation.
Federal Vibration Standards
The FTA has adopted vibration standards that are used to evaluate potential building damage
impacts related to construction activities. The vibration damage criteria adopted by the FTA are
shown in Table 4,Construction Vibration Damage Criteria.
TABLE 4
CONSTRUCTION VIBRATION DAMAGE CRITERIA
Building Category PPV(indsec)
I.Reinforce izoncrete,steel or timber Lao plaslero 0.5
II.Engineered concrete and masonry mo plaslero 0.3
III.Nonangineered timber and masonry buildings 0.2
IV.Buildings extremely susceptible to Obri damage 0.12
SOURCE:FTA,2006,Transit Noise and Vibration Impact Assessment May
In addition,the FTA has also adopted standards associated with human annoyance for
groundbome vibration impacts for the following three land-use categories: Vibration Category I
—High Sensitivity,Vibration Category 2—Residential,and Vibration Category 3—Institutional.
The FTA defines Category 1 as buildings where vibration would interfere with operations within
the building,including vibration-sensitive research and manufacturing facilities,hospitals with
vibration-sensitive equipment,and university research operations.Vibration-sensitive equipment
includes,but is not limited to, electron microscopes,high-resolution lithographic equipment, and
normal optical microscopes.Category 2 refers to all residential land uses and any buildings where
people sleep,such as hotels and hospitals. Category 3 refers to institutional land uses such as
schools,churches,other institutions,and quiet offices that do not have vibration-sensitive
equipment,but still have the potential for activity interference.The vibration thresholds
associated with human annoyance for these three land-use categories are shown in Table 5,
Groundborne Vibration Impact Criteria for General Assessment.No vibration thresholds
have been adopted or recommended for commercial and office uses.
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TABLE 5
GROUNDBORNE VIBRATION IMPACT CRITERIA FOR GENERAL ASSESSMENT
Frequent Occasional Infrequent
Land Use Category Events' Events° Events`
Category 1:Buildings where Ubration would interfere with interior operations. 65 VdB' 65 VEBd 65 VdB'
Category 2:Residences and buildings where people normally sleep. 72 VdB 75 VdB 80 VUB
Category 3: Institutional land uses with primarily daytime use. 75 VdB 78 VdB 83 WE
a TheAmnt E ants is defined as more than 70 nbration a ants of the same source per day,
b 10ccasional E ants is defined as between 30 and 70 nation a ants of the same source per day.
a Ilnfre uentE ants Is defined as fewer than 30 Ibrationa ants of the same kind per day.
d This criterion is based on Is as that are acceptable for most motlerately sonar e e uipment Such as Opti..l improop.pae.
SOURCE:ETA,20%,Transit Noise and Vibrodon Impact Assessment May,
State
California Noise Standards
The State of California does not have statewide standards for environmental noise,but the
California Department of Health Services(DHS)has established guidelines for evaluating the
compatibility of various land uses as a function of community noise exposure.The purpose of
these guidelines is to maintain acceptable noise levels in a community setting for different land
use types.Noise compatibility by different land uses types is categorized into four general levels:
"normally acceptable,"..conditionally acceptable,"..normally unacceptable,"and"clearly
unacceptable."For instance,a noise environment ranging from 50 dBA CNEL to 65 dBA CNEL
is considered to be`normally acceptable"for multi-family residential uses,while a noise
environment of 75 dBA CNEL or above for multi-family residential uses is considered to be
"clearly unacceptable."In addition,California Government Code Section 65302(t)requires each
county and city in the State to prepare and adopt a comprehensive long-range general plan for its
physical development,with Section 65302(g)requiring a noise element to be included in the
general plan.The noise element must: (1)identify and appraise noise problems in the community;
(2)recognize Office of Noise Control guidelines;and(3)analyze and quantify current and
projected noise levels.
The state has also established noise insulation standards for new multi-family residential units,
hotels,and motels that would be subject to relatively high levels of transportation-related noise.
These requirements are collectively known as the California Noise Insulation Standards(Title 24,
California Code of Regulations). The noise insulation standards set forth an interior standard of
45 dBA CNEL in any habitable room. They require an acoustical analysis demonstrating how
dwelling units have been designed to meet this interior standard where such units are proposed in
areas subject to noise levels greater than 60 dBA CNEL.Title 24 standards are typically enforced
by local jurisdictions through the building permit application process.
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California Vibration Standards
There are no state vibration standards.Moreover,according to the California Department of
Transportation's(Caltrans) Transportation and Construction Vibration Guidance Manual,there
are no official Caltrans standards for vibrations However,this manual provides guidelines that
can be used as screening tools for assessing the potential for adverse vibration effects related to
structural damage and human perception. The manual is meant to provide practical guidance to
Caltrans engineers,planners,and consultants who must address vibration issues associated with
the construction,operation,and maintenance of Caltrans projects.The vibration criteria
established by Caltrans for assessing structural damage and human perception are shown in Table
6,Caltrans Vibration Damage Potential Threshold Criteria,and Table 7,Caltrans
Vibration Annoyance Potential Criteria,respectively.
TABLE 6
CALTRANS VIBRATION DAMAGE POTENTIAL THRESHOLD CRITERIA
Maximum Pi(In/see)
Continuous/Frequent
Structure and Condition Transient sources Intermittent Sources
Extremely fragile historic buildings, 0.12 0.08
ruins,ancient monuments
Fragile buildings 0.2 0.1
Historic and some old buildings 0.5 0.25
Older residential structures 0.5 0.3
New residential structures 1.0 0.5
Modem industrial/commercial buildings 2.0 0.5
NOTE: Transient s capers a single isolated ibrefion a era such as blasting or drop balls.
Continuouslrre and Intitlent sources include Impact pile dri-ere, pogoreick compactors, crack andleeat
e uipment, Ibratory pile on are and battery compaction a bipment.
SOURCE'.Caltand ,2013.Transportation and Construction Vibration Guldens Manual.Septembe,
8 Caltrans,Transportation and Construction Vibration Guidance Manual,September 2013.
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TABLE 7
CALTRANS VIBRATION ANNOYANCE POTENTIAL CRITERIA
Maximum li(firo )
Continuou dlerequent
Structure and Condition Transient Sources Irdennittant Sources
Barely perceptible 0.04 0.01
Distinctly perceptible 0,25 0.04
Strongly perceptible 0.9 0.10
Se one 2.0 0.4
NOTE'. Transient sources create a single isolated ibmgon eFent such as blasting or drop balls.
Continuousllre uenl intendant sources Include impact pile drivers, pogondick oxnpactors, crack
andes ei moment,Tbretorypileddrers,and Nlxadorycompactioner ipi
SOURCE:Cafter,,2013.Transportation and construction Vibre4on Guidance Manuel.September.
Local
In California,local regulation of noise involves implementation of general plan policies and noise
ordinance standards. Local general plans identify general principles intended to guide and
influence development plans, and noise ordinances set forth the specific standards and procedures
for addressing particular noise sources and activities.General plans recognize that different types
of land uses have different sensitivities toward their noise environment;residential areas are
considered to be the most sensitive type of land use to noise and industrial/commercial areas are
considered to be the least sensitive.
City of Huntington Beach
General Plan Noise Element
The Noise Element of the General Plan acknowledges that a number of residential,commercial,
and industrial land uses in the City of Huntington Beach,particularly along arterial roadways,are
impacted by vehicular noise levels that exceed city noise/land use compatibility standards(City
of Huntington Beach, 1995). For residential land uses,the normally acceptable interior and
exterior noise standards are 45 and 60 Ldn,respectively.
Relevant noise policies from the Noise Element include:
Policy N 1.2.2—Require new industrial and commercial land uses or the major expansion of
existing land uses to demonstrate that the new or expanded use would not be directly
responsible for causing exterior noise levels to exceed 65 Lou in areas containing noise
sensitive land uses.
Policy N 1.2.5—Require development that generates increased traffic and subsequent
increases in ambient noise levels adjacent to noise sensitive land uses to provide for
appropriate mitigation measures in accordance with acceptable limits of the City's Noise
Ordinance.
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3. En lmnmental Setting
Policy N 1.6.1 —Ensure that construction activities be regulated to establish houre of
operation,to prevent and/or mitigate the generation of excessive or adverse noise impacts
through implementation of the City's Noise Ordinance.
Policy N 1.12.1 —Require detailed and independent acoustical studies be completed for any
new or renovated land uses or structures determined to be potential major stationary noise
sources.
Municipal Code
Chapter 8.40 of the Huntington Beach Municipal Code serves as the City's Noise Ordinance,
which establishes noise standards to control unnecessary, excessive,and annoying noise levels in
the City.Table 8,Huntington Beach Exterior Noise Standards,presents the applicable exterior
noise standards for the designated noise canes established in the City's Noise Ordinance.
TABLE S
HUNTINGTON BEACH EXTERIOR NOISE STANDARDS
Noise Zone Exterior Noise Time Period
Standards
1 DAM residential properties. 55 dbuk� 7:00 a.m. 010:00 p.m.
50 db[A� 10:00 p.m.07:00 a.m.
2 DAM professional office 0 public 55 dbMkO Anytime
institution properties.
3 oAll commercial properties with 60 db6i3O Anytime
the exception of professional
office properties.
4❑AII industrial properties. 70 dbMhO Anytime
SOURCE:City of Huntington Beall Muniapal Code Sendon 0.40 050
The exterior noise levels shown in Table 8 are meant to be further applied as noise standards
based on the duration of the noise;i.e.,the louder the noise,the shorter the time it can last.
According to Section 8.40.060 of the City Noise Ordinance,it is unlawful for any person at any
location within the incorporated area of the City to create noise levels that,when measured on
any residential,public institutional,professional,commercial,or industrial property,to exceed the
exterior noise standards shown in Table 5:
a) For a cumulative period of more than thirty(30)minutes in any hour;
b) Plus 5 dB(A)for a cumulative period of more than fifteen(15)minutes in any hour,,
c) Plus 10 dB(A)for a cumulative period of more than five(5)minutes in any hour;
d) Plus 15 dB(A)for a cumulative period of more than one(1)minute in any hour; or
e) Plus 20 dB(A)for any period of time.
Section 8.40.060 further states that in the event the ambient noise level exceeds any of the fast
four noise limit categories provided above,the cumulative period noise level applicable to said
category shall be increased to reflect said ambient noise level.In the event the ambient noise level
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4. Impacts and Mitigation Measures
exceeds the fifth noise limit category,the maximum allowable noise level under said category
shall be increased to reflect the maximum ambient noise level.
According to Section 8.40.090(D)of the City Noise Ordinance,construction noise is among one
of the noise sources that are exempt from the City's established noise standards.Provided that a
permit has been obtained from the City,noise sources associated with construction,repair,
remodeling, or grading of any real property are deemed to be exempt from the City's noise
standards as long as such activities are not conducted between the hours of 8:00 p.m. and
7:00 a.m.on weekdays,including Saturday,or at any time on Sunday or a federal holiday.
4. Impacts and Mitigation Measures
This section describes the impact analysis relating to noise and vibration impacts for the Project.
It describes the methods and applicable thresholds used to determine the impacts of the proposed
Project.
4.1 Methodology
Construction Noise Levels
Project construction noise levels were estimated using the FHWA's Roadway Construction Noise
Model(RCNM)and construction equipment information provided by the OCWD.Potential noise
levels were identified for the nearest sensitive receptors located offsite based on their respective
distances from the project site.To present a conservative impact analysis,the estimated noise
levels were calculated for a scenario in which all construction equipment was assumed to be
operating simultaneously and located at the construction area nearest to the affected receptors.
These assumptions represent the worst-case noise scenario because construction activities would
typically be spread out throughout the project site and would be located further away from the
affected receptors. The estimated noise levels at the affected receptors were then analyzed against
the construction noise standards established in the HBMC.
Roadway Noise Levels
Off-site construction related traffic noise levels were calculated based on traffic information
provided by the OCWD. Brookhurst Street was selected for analysis and is expected to be most
directly impacted by construction-related traffic.Noise levels along Brookhurst Street were
calculated using the FITWA-RD-77-108 model and construction-related traffic volumes provided
by the OCWD because noise sensitive residential uses are located along the street.
Onsite Stationary Source Noise Levels
During operation of the project,noise levels would be generated onsite by stationary noise
sources such as the proposed pump station. The noise levels generated by the proposed pump
station are assessed based on the HBMC requirements and measured data.The potential impacts
on the nearby offsite receptors are determined based on the proposed pump station's distance
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4. Impacts and Mitigation Measures
from these receptors.The noise levels determined at the offsite,noise-sensitive receptors are then
compared to the stationary source noise significance thresholds identified in the HBMC.
Groundborne Vibration Levels
Groundborne vibration levels resulting from construction activities at the project site were
estimated using data in the FTA Transit Noise and Vibration Impact Assessment document.
Potential vibration levels resulting from construction of the project are identified for offsite
locations that are sensitive to vibration(i.e.,existing residential buildings)based on their distance
from construction activities.
4.2 Thresholds of Significance
Based on Appendix G of the CEQA Guidelines, a project would have a significant effect on the
environment with respect to noise and/or ground-borne vibration if it would result in:
• Exposure of persons to,or generation of,noise levels in excess of standards established in
the local general plan or noise ordinance,or applicable standards of other agencies;
• Exposure of persons to,or generation of,excessive ground-borne vibration or ground-
home noise levels;
• A substantial permanent increase in ambient noise levels in the project vicinity above
levels existing without the project;
• A substantial temporary or periodic increase in ambient noise levels in the project
vicinity above levels existing without the project;
• Exposure of people residing or working in the project area to excessive noise levels
(for a project located within an airport land use plan or,where such a plan has not been
adopted,within two miles of a public airport or public use airport);or
• Exposure of people residing or working in the project area to excessive noise levels
(for a project within the vicinity of a private airstrip).
The project site is not located within two miles of an airport,and no public airport or private
airstrip is currently located in the vicinity of the project site.The nearest airport to the project site
is the John Wayne Airport,which is located approximately five miles northeast of the project site.
Therefore,the project would not expose people to excessive noise from a public airport or private
airstrip,and these issue areas would not be further analyzed in this report.
Noise Criteria
As set forth in the HBMC,a project would normally have a significant impact on noise levels
from construction if.
9 PTA,Transit Noise and Vibration Impact Assessment May 2006.
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• Construction activities are undertaken between 8:00 p.m. and 7:00 a.m on weekdays or
8:00 p.m. and 8:00 a.m. on Saturdays;and construction activities exceed the stationary
noise thresholds of 55 dBA at sensitive receptors between 8:00 p.m. and 10:00 p.m. and
50 dBA between 10:00 p.m. and 7:00 a.m.,or ambient noise levels where the ambient
noise exceeds the above standards.
A change in noise levels of less than 3 dBA is not discernible to the general population,while an
increase in average noise levels of 3 to 5 dBA is clearly discernible to most people(California
DOT, 1991). An increase in the noise environment of 5 dBA or greater is considered to be the
minimum required increase for a change in community reaction(U.S. DOT, 1990)and,for the
purposes of this analysis,constitutes a significant noise impact. With temporary construction
noise impacts, identification of"substantial increases"depends upon the duration of the impact,
the temporal daily nature of the impact, as well as the absolute change in dBA levels. Substantial
increase in noise levels are defined as follows.
• Project construction activities cause the exterior ambient noise level to increase by 5 dBA
or more at a noise-sensitive use, as measured at the property line of any sensitive use.
• Noise from project-related operational(non-transportation)noise sources such as the
proposed pump station exceeds the nighttime average ambient noise levels in Table 3.
Vibration Criteria
The CEQA Guidelines do not define the levels at which groundbome vibration or groundbome
noises me considered"excessive."The City of Huntington Beach currently does not have a
significance threshold to assess vibration impacts during construction.Additionally,there are no
federal,state,or local vibration regulations or guidelines directly applicable to the project.
However,publications of the FTA and Caltrans are two of the seminal works for the analysis of
vibration relating to transportation and construction-induced vibration. The project is not subject
to FTA or Caltrans regulations;nonetheless,these guidelines serve as a useful tool to evaluate
vibration impacts. For the purpose of this analysis,the vibration criteria for structural damage and
human annoyance established in the most recent Caltrans' Transportation and Construction
Vibration Guidance Manual,which are shown previously in Tables 6 and 7,respectively,are
used to evaluate the potential vibration impacts of the project on nearby sensitive receptors.
Given the nature of the project,"excessive"groundbome vibration or noises that could occur at
the project site would only be those generated during project construction. Construction activities
at the project site have the potential to generate low levels of groundbome vibration as the
operation of heavy equipment(i.e.,dozer,excavators,backhoes,haul trucks,etc.)generates
vibrations that propagate though the ground and diminish in intensity with distance from the
source.No high-impact activities, such as pile driving or blasting,would be used during project
construction.The nearest offsite sensitive receptors are located approximately 460 feet from the
proposed pump station. Due to the rapid attenuation of ground-borne vibration and distance
between the project and the nearest single-family residential uses(approximately 460 feet), there
is no potential for operational-period impacts with respect to ground-borne vibration.
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4. Impacts and Mitigation Measures
Accordingly,the groundborre vibration analysis presented in this report is limited to the project's
construction activities.
4.3 Project Impacts
Impact 1: The project would not result in the exposure of persons to,or generation of,noise
levels in excess of standards established in the local general plan or noise ordinance,or
applicable standards of other agencies. (Less than Significant)
Construction Noise
Onsite Construction Noise
Construction of the proposed project would require the use of heavy equipment during the
demolition, grading,and excavation activities at the project site.During each stage of
development,there would be a different mix of equipment.As such,construction activity noise
levels at and near the project site would fluctuate depending on the particular type,number,and
duration of use of the various pieces of construction equipment.
Individual pieces of construction equipment anticipated during Project construction could
produce maximum noise levels of 60 dBA to 83 dBA L_at a reference distance of 50 feet from
the noise source,as shown in Table 9,Construction Equipment Noise Levels. These maximum
noise levels would occur when equipment is operating at full power. The estimated usage factor
for the equipment is also shown in Table 9. The usage factors are based on FHWA's li
User's Guide.10
TABLE 9
CONSTRUCTION EQUIPMENT NOISE LEVELS
Noise Level at So Feet
Construction Equipment idea,-max) Estimated Usage Factor,
Backhoe2 69 50
Bull Doer' 82 40
Compactor' 83 20
Concrete Truck' 75 25
Crane' 81 40
Dump Truck' 76 20
Drill Rig Traci 76 50
Exca ator' 81 40
Forklli 60 50
Man Lift' 68 25
Water Truck' 80 10
' (Amenedirom FHWA Roadway Construction Noise Model,2001
' Obtain uc ham Noise Abatement Plan Mid Basin Monitoring Well aAR111,papered by Vista Enlmnmental,
August ll 2011,
10 Federal Highway Administration,Roadway Construction Noise Model User's Guide,2006.
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During project construction,the nearest and most notable offsite sensitive receptors that would be
exposed to increased noise levels would be the existing single-family residential uses located in
proximity to the project site. Specifically,the nearest offsite noise sensitive receptors include the
following:
• Single-family residences along Broold urst Street approximately 260 feet west of the
project site;and
• Multi-family residences along Brookhurst Street approximately 800 feet north of the
project site.
Over the course of a construction day,the highest noise levels would be generated when multiple
pieces of construction equipment are being operated concurrently.As discussed previously,the
project's estimated construction noise levels were calculated for a scenario in which all
construction equipment was assumed to be operating simultaneously and located at the
construction area nearest to the affected receptors to present a conservative impact analysis.The
estimated noise levels at the offsite sensitive receptors were calculated using the FHWA's
RCNM, and were based on the concurrent operation of 6 pieces of equipment(i.e., front end
loader,backbone,dozer,haul truck,drill rig truck,etc.)which is considered a worst-case
evaluation because the project would use less overall equipment on a daily basis,and as such
would generate lower noise levels.Table 10,Estimated Construction Noise Levels at Offshe
Sensitive Uses,shows the estimated construction noise levels that would occur at the nearest
offsite sensitive uses during a peak day of construction activity at the project site.
TABLE 10
ESTIMATED CONSTRUCTION NOISE LEVELS AT OFFSITE SENSITIVE USES
Estimated
Approximate Maximum
Distance to Construction
Project site Noise Levels Significance Noise Level
Offshe Sensitive Land Uses Locallon (R.), (dBA L,a) Threshold3 Increase
Singleltamily residential uses West ofthe project site along 260 652 71 F
Brookhuret Street
Multifamily residential uses North of the project site 800 562 73 17
Brookhurst Street
1 The distance represents the nearestconstruction area on the project site to the property line ofthe excite receptor.
2 Receptors are partially shielded tram the construction site by existing walls:and such shielding is included in the analyses representing a 5 dBA
reduction in noise lsr d,
3 The slgniflcance thmsbolds are the lowest daytime ambient noise 1i as shown In Table 3 plus 5 di
SOURCE:ESA,2016.
As shown in Table 10,the peak day construction noise levels experienced by the offsite sensitive
receptors would range from 56 dBA,Lro at the multi-family residential uses located north of the
project site to 65 dBA, Lrs at the single-family residential uses located west of the project site.
Thus,construction activities associated with the project would generate episodic noise levels
below the significance threshold of 71 dBA(the lowest daytime ambient noise level of 66 dBA as
shown in Table 3 plus 5 dBA)at the nearest residential uses west of the project site.Because
ocwo water Pmdwan unsimmident Pgp4t 25 ESAIte03i
Noise and NGretion Termical Repot August 2016
ocwD water Production Enhancement Project,Noise and Vibration Technical Report
4. Impacts and Mitigation Measures
construction noise levels associated with the project would not exceed the significance threshold
at the offside sensitive locations,construction activities associated with the project would not
expose persons to,or generate noise levels in excess of standards established in the local general
plan or noise ordinance,or applicable standards of other agencies,Therefore,impacts would be
less than significant, and no mitigation measures would be required.
Off-Site Construction Traffic Noise
Delivery truck and haul hock trips would occur throughout the construction period. Trucks
traveling to and from the project site would be required to travel along Brookhutst Street. As
shown in Table 2,an estimated maximum of approximately 10 worker's vehicle trips, 1 vendor
truck trip,and 32 haul truck trips would occur per day.
The project's truck trips would generate noise levels of approximately 50 dBA, CNEL at 25 feet
distance along Brookhurst Street. As shown in Table 3,the existing noise levels along Brookhurst
Street ranged from 69 dBA to 71 dBA,CNEL. Noise levels of 50 dBA, CNEL generated by
construction-related traffic would not increase the ambient noise levels along Brockhurst Street.
Therefore, off-site construction traffic noise impacts would be less than significant.
Operational Noise
Once the proposed pump station is operational,noise levels generated at the project site would
mainly occur from the pump station.The flow equalization tank would have a 4-pump,
approximately 500-linear feet of 36-inch diameter connection piping with a meter vault(15-ft x
20-fir x 10-ft deep)connected to the operations of the tank.The pump station would be housed in
a 30-fir x 40-ft x 20-fir block wall building.
The analysis of the pump station-related noise is based upon reference noise measurement
conducted on July 15,2016 at a pump station located in the OCWD facility at 18700 Ward Street,
Fountain Valley,CA.Pump station-related noise levels were measured inside of the pump station
and outside of the pump station at 5 feet from a louver.Noise level of 80 dBA was measured
inside of the pump station and noise level of 66 dBA was measured at 5 feet from the louver
outside of the pump station. The pump station house with louvers would provide approximately
14 dBA noise reduction.
The nearest single-family residential uses west of the project site would be located approximately
460 feet from the proposed pump station.Based on a noise level source strength of 66 dBA at a
reference distance of 5 feet,and accounting for distance attenuation(minimum 39 dBA insertion
loss)and barrier insertion loss by block walls(minimum 5 dBA insertion loss),pump station
related noise would be reduced to 22 dBA at the nearest noise sensitive uses(RI pump station
related noise would not exceed the significance threshold of 61 dBA(the lowest nighttime
ambient noise level of 56 dBA as shown in Table 3 plus 5 dBA). Operation of the project would
not expose persons to,or generate noise levels in excess of standards established in the local
general plan or noise ordinance,or applicable standards of other agencies,Therefore, impacts
would be less than significant.
ocwp water Pmennion Enhanoseent Pmpa 26 r&4 r tep3a]pa
Noise and Vibration Tedmiwl Re,un nu9uet 2016
OCW D Water production Enhancement protect.Noise and Vibration Technical Report
4. Impacts and Mitigation Measures
Impact 2: The project would not expose persons to,or generate,excessive ground-borne
vibration or ground-borne noise levels.(Less than Significant)
Construction Vibration
Construction activities at the project site have the potential to generate low levels of goundbome
vibration as the operation of heavy equipment(i.e.,compactor,backhoe,dozer,excavators,haul
trucks,etc.)generates vibrations that propagate though the ground and diminish in intensity with
distance from the source.No high-impact activities, such as pile driving or blasting,would be
used during project construction.The nearest offsite receptors to the project site that could be
exposed to vibration levels generated from project construction include single-family residential
uses west of the project site. Groundbome vibrations from construction activities very rarely
reach the levels that can damage structures,but they may be perceived in buildings very close to a
construction site.
The PPV vibration velocities for several types of construction equipment,along with their
corresponding RMS velocities(in VdB),that can generate perceptible vibration levels are
identified in Table 11,Vibration Source Levels For Construction Equipment.Based on the
information presented in Table 11,vibration velocities could range from 0.003 to 0.089 in/sec
PPV at 25 feet from the source of activity.
TABLE 11
VIBRATION SOURCE LEVELS FOR CONSTRUCTION EQUIPMENT
Approximate PPV(inh ae) Approximate RMS(VAB)
25 50 60 75 100 25 50 60 75 100
Equipment Feet Feet Feet Feet Feet Feet Feet Feet Feet Feet
Large BulldoEar 0.089 0.031 0.024 0.017 0.011 87 78 76 73 69
Caisson Drilling u089 0.031 0.024 0.017 0.011 87 78 76 73 69
Loaded Trucks 0.076 0.027 0.020 0.015 0.010 86 77 75 72 68
]ackhammer 0.035 0.012 0.009 0.007 0,004 79 70 68 65 61
Small Build. an 0.003 0.001 u0008 0.0006 0.0004 58 49 47 44 40
SOURCE:ETA,2006.Transit Noise and Vibration Impact Assessment.May
Table 12,Groundbore Vibration Levels at Offsite Sensitive Uses Compared to Caltrans'
and Fill Vibration Damage Potential Threshold,shows the estimated construction-related
goundbome vibration levels that could occur at the nearest offsite structures during construction
at the project site and a comparison to the identified significance threshold.
As shown in Table 12,the vibration velocities forecasted to occur at the offsite sensitive receptors
could potentially be up to 0.0027 in/sec;PPV(or 57 VdB)at the nearest single-family residential
uses.
ocwo waur Rmdunion Entunionmem Rrop<t 27 ESAIIII03 >.pa
Noise and Vibration Tedrmul Repot Aisuat 2016
ocwD Water Production Enhancement Project Noise and Vibration Technical Report
4. Impacts and Mitigation Measures
TABLE 12
GROUNDBORNE VIBRATION LEVELS AT OFFSITE SENSITIVE USES COMPARED TO CALTRANS'AND FTA
VIBRATION DAMAGE POTENTIAL THRESHOLD
Approximate Calbans'Vibralion FTAVibralion Exceed Caltrans'
Distance to Damage Potential Damage Potential or FTA Vibration
Project Site Estimated PPV Threshold,PPV Threshold,PPV Threshold?
Offsite Sensitive Land Use fil (iNsec)NEB (house,)` (in/sec)° (Yes or No)
Single®amily residential
uses:West of the project site 260 0.0027/57 0.5 0.5 No
along Brookhurst Street
rt,ntoo
lose,n Inches per second.
a Approximate distances are measured from the nearest construction area wehin the pool see Mew 11braeon levels would be generated to the nearest
ogseestiucture.
In Mthough the retail uses are located directly north of and up against me project site it is antlelpated that the constreal area where oe¢oad eruipment
would operate would be located at a minimum of fi e feet from the renal shocNres.
° Caltrans Vibration Damage Potential Thresholds were taken from Table 3,
FTA Vibration Damage Potential Thresholds were taken from Table f.
SOURCE:ESA,2016,
Under the FTA construction vibration damaged criteria,the existing residential structures are
considered"reinforce-concrete, steel or timber(no plaster). With respect to the vibration sources
associated with project construction, it is anticipated that continuous/frequent intermittent sources
of vibration,as defined under Caltrans' criteria,would occur from compaction activities at the
project site,although no pile-driving would be required. As such,the vibration level criteria for
continuous/frequent intermittent sources are used in this analysis.
Based on the information shown in Table 10 which shows an estimated PPV of 0.0027,none of
the existing offsite residential structures(considered as"new residential structures"and
"reinforced-concrete,steel or timber"under the Caltrans' and ETA construction vibration damage
criteria,respectively)located to the west of the project site would be exposed to PPV
groundborne vibration levels exceeding the ETA and Caltrans' 0.5 inches per second criteria as
shown in Tables 4 and 6,respectively.As such,the vibration impacts at these residential
structures would be less than significant.
With respect to human annoyance,the City Noise Element identifies residential areas as noise-
sensitive land uses. Currently,these types of sensitive uses that are located in the project site
vicinity include the single-family residential uses that are located to the west of the project site.
Under the Caltrans' vibration annoyance potential criteria(refer to Table 7),vibration levels
exceeding 0.04 inches per second PPV for continuous/frequent intermittent sources would be
considered distinctly perceptible. In addition,under the ETA vibration impact criteria for general
assessment,residential receptors are considered to be a Category 2 land use(refer to Table 2).
Land uses under this ETA category exposed to vibration levels exceeding 80 VdB for infrequent
events would be considered an impact. As shown in Table 12,the single-family residential
receptors located west of the project site would be exposed to vibration levels of 0.0027 in/sec
PPV/57 Vi which is well below the Caltrans' 0.04 in/sec PPV distinctly perceptible threshold
ocwo We.,Protests,enen(ermt Pmpct 28 Fsn I wandil
Noise and Vmretion rechnni RePat A.1ufl 2016
OC ND Water Produdon Enhancement Protect Noise and Vlbra lon Technical Report
5, conclusion
and the FTA's 80 VdB impact threshold.Thus,vibration impacts related to human annoyance
would be less than significant.
Impact 3: The project would not result in a substantial permanent increase in ambient noise
levels in the project vicinity above levels existing without the project?
As discussed previously under Impact 1,due to the proximity of the existing offsite sensitive uses
to the project site,the project's operation activities would not expose these sensitive receptors to
increased exterior noise levels. As set forth in Section 4.2 above,a project would normally have a
significant impact on noise levels from operation if the project would exceed the nighttime
average ambient noise levels in Table 3 at a noise-sensitive use.Based on the measured noise
levels at the nearest offsite sensitive receptors to the project site, it was determined that the pump
station-related noise levels would not exceed the nighttime average ambient noise levels at the
offsite sensitive receptors.As such,there would not be a substantial permanent increase in
ambient noise levels in the project vicinity above levels existing without the project,and impacts
would be less than significant. No mitigation measures are required.
Impact 4: The project would not result in a substantial temporary or periodic increase in
ambient noise levels in the project vicinity above levels existing without the project?(Less
than Significant Impact)
Construction Noise
As discussed previously under Impact 1,due to the distances of the existing offsite sensitive uses
to the project site,the project's construction activities would not expose these sensitive receptors
to increased exterior noise levels.As set forth in Section 4.2 above,a project would normally
have a significant impact on noise levels from construction if the project would exceed the
ambient noise levels by 5 dBA or more at a noise-sensitive use.Based on the measured noise
levels at the nearest offsite sensitive receptors to the project site that are shown in Table 10,it was
determined that construction noise levels would not exceed the ambient noise levels by 5 dBA at
the offsite sensitive receptors.Thus,short-term noise impacts from construction would be less
than significant at these sensitive offsite locations.
5. Conclusion
Construction noise and vibration levels associated with the project would not exceed the
significance threshold at the offsite sensitive locations,construction activities associated with the
project would not expose persons to, or generate noise and vibration levels in excess of standards
established in the local general plan or noise ordinance,or applicable standards of other agencies,
Therefore, construction noise and vibration impacts would be less than significant.
Operation of the project would not expose persons to,or generate noise levels in excess of
standards established in the local general plan or noise ordinance,or applicable standards of other
agencies,Therefore,operation noise impacts would be less than significant.
oveD Warr Prodnnion Enhanrgrem Pio a 29 ESArtei
Noise and VIi Teshniwl Repot August 2016
Ca n Wai Pmdudon Enhancement Prolect Noise and Vlbiatlon Technical Repoli
6. References
As discussed above,the project construction and operation would not result in a substantial
temporary or permanent increase in ambient noise and vibration levels at offsite sensitive receptor
locations. Therefore, impacts would be less than significant.
6. References
California Department of Transportation(Caltrans), Technical Noise Supplement(TeNS).
September,2013.
Caltrans, Transportation and Construction Vibration Guidance Manual. September 2013.
Federal Highway Administration,Roadway Construction Noise Model User's Guide,2006.
FTA, 2006. Transit Noise and Vibration Impact Assessment. May.
USEPA,EPA Identifies Noise Levels Affecting Health and Welfare.April 1974.
o ai wain Pmdnnlon Enesonnem Pnswd 30 ESk11WaT03
Nolte and Vni Te lsioad RepU August 2016
APPENDIX A
Ambient Noise Data
O WO WaWr PwduNon Enha—t Pm)M E&4I1WU7.03
NolSe-n Te.nlnel Repot Mgni M18
Measured Ambient Noise LeCeIS
Project: OCWD Water Production Enhancement Project
Location: R1 [West of the Project Site
Sources: Ambient
Date: ILIy 13, 2016
HNL,
TIME dB(A) 80.0
12:00 AM 59.8
A
2:00 70.0
3:00 AM Q
4:00 AM m
5:00 A ° 60.0
6:00 AM 63.3 W
7:00 AM 65.9 >
8:00 AM 67.0 j 60.0
9:00 AM 66.2 W
10:0 N 40.0
11:00 AM O
12:00 PM Z
w 30.0
2:00 P F
3:00 PM =
4:00 PM W 20.0
5:00 PM
3
7:00 PM Q 10.0
8:00 PM95T-
P
0:0 0.0
11:00 PM
CNEL, dB(A): 69.2 000000000000000000000000
000000000000000000000000
iV � iV i+i V in iprcp OiO � iV � NixiR � i01� W OiO �
TIME
NOTES:
flelOcnel.xls
Measured Ambient Noise LeCels
Project: OCWD Water Production Enhancement Project
Location: R2 0.Southwestern Boundary of Multifamily Residential Uses
Sources: Ambient
Date: Wly 13, 2016
HNL,
TIME d6(A) 80.0
12:00 AM 61.8
A
2:00 AM 70.0
3:00 AM Q
4:00 AM m
5: A ° 60.0
6:00 AM 65.5 W
7:00 AM 68.2 >
8:00 AM 69.3 Lu 60.0
9:00 AM 68.6 W
10:00 AM 40.0
11:00 AM O
12:00 PM Z
w 30.0
2:00 P F
3:00 PM =
4:00 PM W 20.0
3
7:00 PM Q 10.0
8:00 PM
P
10:0 0.0
11:00 PM
CNEL, dB(A): 71.21 000000000000000000000000
000000000000000000000000
iV � iV i+i V id iOr W OiO � iV � NixiR � i01� W OiO �
TIME
NOTES:
flelOcnel.xls
APPENDIX B
Construction Noise Calculations
O WO WaWr PwduNon Enha—t Pm)M E&4I1WU7.03
Nol--n Te.nlnel Repot Mgni M18
Project: The OCWD Water Production Enhancement
Construction Phase: OCSD Flow EO Tank,PS,Meter Vault&Pipeline
Receptor: R1
Construction
Reference Estimated Equipment Noise
No.of Noise Level at Noise Level at A Sensitive
Equip. 501t,Lmax Daily Usage Factor Distance to Shielding,dBA Receptor Location
Construction Equipment A B C Receptor R D E F
DOLar 1 82 400 260 5 59
Compactor 1 83 200 260 5 57
ExcaLator 1 81 400 260 5 58
Dump Truck 1 76 200 260 5 50
Demo Dump Truck 1 76 200 260 5 50
Water Truck 1 80 100 260 5 51
DOLar 1 82 400 360 5 56
ExcaCator 1 81 400 360 5 55
Dump Truck 3 76 200 360 5 52
Demo Dump Truck 3 76 200 360 5 52
Construction Noise Levels of Each Construction Equipment at A Sensitive Receptor
dBA,Leq=[AxB-20LogtDe/50t-E+IOW,,(C/I00)I
Construction Hour: 12 Hours during daytime fr am to 7 pmn
0 Hours during eFaning fr pm to 10 pmn
0 Hours during nighttime 10 pm W 7 amn
Combined Noise Le-ala of Each Construction E uipment
Construction Noise Level at R1 65 dBA,Leq Noise Level at A Sensitive Receptor Location
Source for Ref.Noise Lerals:LA CEGA Guides,2006 n FHWA RCNM,2005
N:NntlR Prgerv\R noC W r P,Wudlm EnaennemenaCanslo k Cela\Cansoron MV
7w�
Project: The OCWD Water Production Enhancement
Construction Phase: OCSD Flow EO Tank Piles
Receptor: R1
Construction
Reference Estimated Equipment Noise
No.of Noise Level at Noise Level at A Sensitive
Equip. Oft,Lmax Daily Usage Factor Distance to Shielding,dBA Receptor Location
Construction Equipment A B C Rece tor, R D E F
Drill Rig 1 76 500 260 5 54
Backhoe 1 69 500 260 5 47
Concrete Truck 1 75 250 260 5 50
Dump Truck 1 76 200 260 5 50
Water Truck 1 80 10D 260 5 51
Dump Truck 1 76 200 360 5 47
Water Truck 1 80 10D 360 5 48
Construction Noise Levels of Each Construction Equipment at A Sensitive Receptor
dBA,Leq=[AxB-20Log[De/50)-E+I0LOS(C/100)l
Construction Hour: 12 Hours during daytime fr am to 7 pmn
0 Hours during eFaning fr pm to 10 pmn
0 Hours during nighttime 110 pm to 7 amn
Combined Noise Le-ala of Each Construction Equipment
Construetlon Noise Level at R1 58 dBA,Leq Noise Level at A Sensitive Receptor Location
Source for Ref.Noise Leq ls:LA CEGA Guides,2006 n FHWA RCNM,2005
N:NntlR Proferv\R MD W r Pm Urflrn EnxennemenaConssu k Cela\C s urSv MV
qr�
Project: The OCWD Water Production Enhancement
Construction Phase: OCSD Flow EO Tank Pad
Receptor: R1
Construction
Reference Estimated Equipment Noise
No.of Noise Level at Noise Level at A Sensitive
Equip. Sort,Lmax Daily Usage Factor Distance to Shielding,tlBA Receptor Location
Construction Equipment A B C Receptor,It D E F
Crane 1 81 400 260 5 58
Forklift 1 60 500 260 5 38
Concrete Truck 1 75 250 260 5 50
Forklift 1 60 500 360 5 35
Concrete Truck 3 75 250 360 5 52
Construction Noise Levels of Each Construction Equipment at A Sensitive Receptor
ties,Last=[AxB-IOLog(De/50[--E+IOLog[C/100[[
Construction HOUC 12 Hours during daytime O am to 7 noun
0 Hours during a timing 7 pm to 10 pmi
0 Hours during nighttime 10 pm to 7 amn
Combined Noise Levels of Each Construction Eruipment
Construction Noise Level at R7 59 tlBA,Le; Noise Leval at A Sensitive Receptor Location
Source for Ref.Noise Levels:LA CEGA Guides,nos n FHWA RCNM,2005
N:odms Profetls\R Ml,WD Wedr wohudmn enhancemed,Coninudko Celc\Caneudko MV
Project: The OCWD Water Production Enhancement
Construction Phase: OCSD Flow EO Tank Assembly&Coating
Receptor: RI
Construction
Reference Estimated Equipment Noise
No.of Noise Leval at Noise Level at A Sensitive
Equip. 5",Lmax Daily Usage Factor Distance to Shielding,dBA Receptor Location
Construction Equipment A B C Receptor,ft D E F
Crane 1 81 400 260 5 58
Forklift 1 60 500 260 5 38
Man Lift 1 68 250 260 5 43
Foddift 3 60 500 360 5 40
Man Lift 4 68 250 360 5 46
Construction Noise Levels of Each Construction Equipment at A Sensitive Receptor
dBA,Leq=lAxB-20Lo,(De/50)-E+IOLodC/IWJl
Construction Hour: 12 Hours during daytime I am to]pmr
0 Hours during e,Bring p pm 1010 pmn
O Hours during nighttime 10 pm to]emn
Combined Noise Lerbls of Each Construction EFuipmenl
Construction Noise Level at RI 58 dBA,Leq Noise Le-ol at A Sensl 11 Receptor Location
Source for Ref.Noise Levels:LA CEGA Guides,2006 n FHWA RCNM,20M
NWtiro Rajed $A-OCWDWN,Pmtloyon Enhanmme,tCmWdion Gl$IOngmdion-OCWD
Project: The OCWD Water Production Enhancement
Construction Phase: OCSD Flow EO PS&Meter Vault Equipping
Receptor: RI
Construction
Reference Estimated Equipment Noise
No.of Noise Leval at Noise Level at A Sensitive
Equip. 5",Lmax Daily Usage Factor Distance to Shielding,dBA Receptor Location
Construction Equipment A B C Receptor,ft D E F
Crane 1 81 400 260 5 58
Forklift 1 60 500 260 5 38
Man Lift 1 68 250 260 5 43
Foddift 3 60 500 360 5 40
Man Lift 4 68 250 360 5 46
Construction Noise Levels of Each Construction Equipment at A Sensitive Receptor
dBA,Leq=lAxB-20LogtDe/50)-E+IOLodC/IWJl
Construction Hour: 12 Hours during daytime q am to]pmr
0 Hours during e,aping p pm 1010 pmn
O Hours during nighttime 10 pm to]emn
Combined Noise Levels of Each Construction EFuipmenl
Construction Noise Level at RI 58 dBA,Leq Noise Leal at A Sensl 11 Receptor Location
Source for Ref.Noise Levels:LA CEGA Guides,2006 n FHWA RCNM,20M
NWtiro Rajed $A-OCWDWN,Pmtloyon Enhanmme,tCmW dion Gl$r Ongmdion-OCWD
Project: The OCWD Water Production Enhancement
Construction Phase: OCSD Flow EO Tank,PS,Meter Vault&Pipeline
Receptor: R2
Construction
Reference Estimated Equipment Noise
No.of Noise Level at Noise Level at A Sensitive
Equip. 50ft,Lmax Daily Usage Factor Distance to Shielding,dBA Receptor Location
Construction Equipment A B C Receptor,R D E F
DOLar 1 82 400 800 5 49
Compactor 1 83 200 800 5 47
ExwLator 1 81 400 800 5 48
Dump Truck 1 76 200 800 5 40
Demo Dump Truck 1 76 200 800 5 40
Water Truck 1 80 100 800 5 41
DOLar 1 82 400 900 5 48
ExcaCator 1 81 400 900 5 47
Dump Truck 3 76 200 900 5 44
Demo Dump Truck 3 76 200 900 5 44
Construction Noise Levels of Each Construction Equipment at A Sensitive Receptor
dBA,Lee=[AxB-20LogtDe/50t-E+IOLOSIC/I00II
Construction Hour: 12 Hours during daytime fr am to 7 pmn
0 Hours during eFaning fr pm to 10 pmn
0 Hours during nighttime 10 pm W 7 amn
Combined Noise Levels of Each Construction E uipment
Construction Noise Level at R2 56 dBA,Leq Noise Level at A Sensitive Receptor Location
Source for Ref.Noise Lerals:LA CEQA Guides,2006 n FHWA RCNM,2005
N:NntlR P,ofetls\R McneDW r P,Wudlm EnaennemenaConsWC Cela\C suclkn McvaO
7w�
Project: The OCWD Water Production Enhancement
Construction Phase: OCSD Flow EO Tank Piles
Receptor: R2
Construction
Reference Estimated Equipment Noise
No.of Noise Level at Noise Level at A Sensitive
Equip. Oft,Lmax Daily Usage Factor Distance to Shielding,dBA Receptor Location
Construction Equipment A B C Receptor,R D E F
Drill Rig 1 76 500 800 5 44
Backhoe 1 69 500 800 5 37
Concrete Truck 1 75 250 800 5 40
Dump Truck 1 76 200 800 5 40
Water Truck 1 80 10D 800 5 41
Dump Truck 1 76 200 900 5 39
Water Truck 1 80 10D 900 5 40
Construction Noise Levels of Each Construction Equipment at A Sensitive Receptor
dM,Leq=[AxB-20Log[De/50)-E+I0LOS(C/100)l
Construction Hour: 12 Hours during daytime fr am to 7 pmn
0 Hours during eFaning fr pm to 10 pmn
0 Hours during nighttime 10 pm W 7 amn
Combined Noise Levels of Each Construction Equipment
Construction Noise Level at R2 49 dBA,Leq Noise Level at A Sensitive Receptor Location
Source for Ref.Noise Levels:LA CEQA Guides,2006 n FHWA RCNM,2005
N:NntlR Profetls\RSAMD W r Pm Urflrn EnxennemenaConsWC Cela\ suclkn MCsD
qr�
Project: The OCWD Water Production Enhancement
Construction Phase: OCSD Flow EO Tank Pad
Receptor: R2
Construction
Reference Estimated Equipment Noise
No.of Noise Level at Noise Level at A Sensitive
Equip. Sort,Lmax Daily Usage Factor Distance to Shielding,tlBA Receptor Location
Construction Equipment A B C Receptor,It D E F
Creole 1 81 400 800 5 48
Forklift 1 60 500 800 5 28
Concrete Truck 1 75 250 800 5 40
Forklift 1 60 500 900 5 27
Concrete Truck 3 75 250 No 5 44
Construction Noise Levels of Each Construction Equipment at A Sensitive Receptor
ties,Leq=[AxB-IOLog(De/50[--E+IOLog[C/100[[
Construction HOUC 12 Hours during daytime O am to 7 noun
0 Hours during a timing 7 pm to 10 pmi
0 Hours during nighttime 10 pm to 7 amn
Combined Noise Levels of Each Construction Eruipment
Construction Noise Level at R2 50 tlBA,Leq Noise Level at A Sensitive Receptor Location
Source for Ref.Noise Levels:LA CEGA Guides,nos n FHWA RCNM,2005
N:odms Profeds\R Ml,WD Wedr wohedmn Enhennement\ConaWCkn Cela\Canatruclkn MV
Project: The OCWD Water Production Enhancement
Construction Phase: OCSD Flow EO Tank Assembly&Coating
Receptor: R2
Construction
Reference Estimated Equipment Noise
No.of Noise Leval at Noise Level at A Sensitive
Equip. 5",Lmax Daily Usage Factor Distance to Shielding,dBA Receptor Location
Construction Equipment A B C Receptor,ft D E F
Crane 1 81 400 800 5 48
Forklift 1 60 500 800 5 28
Man Lift 1 68 250 800 5 33
Foddift 3 60 500 900 5 32
Man Lift 4 68 250 900 5 38
Construction Noise Levels of Each Construction Equipment at A Sensitive Receptor
dBA,Leo=lAxB-20Lo,dDe/50)-E+IOWg(C/100N
Construction Hour: 12 Hours during daytime I am to]pmr
0 Hours during e,Bring p pm W 10 pmn
O Hours during nighttime 10 pm to]emn
Combined Noise Lerbls of Each Construction EFuipmenl
Construction Noise Level at R2 49 dBA,Leq Noise Le-ol at A Sensl 11 Receptor Location
Source for Ref.Noise Levels:LA CEGA Guides,2006 n FHWA RCNM,20M
NWtiro Rajed $A-OCWDWN,Pmtloyon Enhanmme,tCmWdion Gl$IOngmdion-OCWD
Project: The OCWD Water Production Enhancement
Construction Phase: OCSD Flow EO PS&Meter Vault Equipping
Receptor: R2
Construction
Reference Estimated Equipment Noise
No.of Noise Leval at Noise Level at A Sensitive
Equip. 5",Lmax Daily Usage Factor Distance to Shielding,dBA Receptor Location
Construction Equipment A B C Receptor,ft D E F
Crane 1 81 400 800 5 48
Forklift 1 60 500 800 5 28
Man Lift 1 68 250 800 5 33
Foddift 3 60 500 900 5 32
Man Lift 4 68 250 900 5 38
Construction Noise Levels of Each Construction Equipment at A Sensitive Receptor
dBA,Leo=lAxB-20LogtDe/50)-E+IOWdC/100N
Construction Hour: 12 Hours during daytime q am to]pmr
0 Hours during e,aping p pm W 10 pmn
O Hours during nighttime 10 pm to]emn
Combined Noise Lerals of Each Construction EFuipmenl
Construction Noise Level at R2 49 dBA,Leq Noise Leal at A Sensl 11 Receptor Location
Source for Ref.Noise Levels:LA CEDA Guides,2006 n FHWA RCNM,20M
NWtiro Rajed $A-OCWDWN,Pmtloyon Enhanmme,tCmW dion Gl$r Ongmdion-OCWD
APPENDIX C
Off-Site Construction Traffic Noise Calculations
O WO Water PwduNon EManmrmnt Propel E&4I1WU7.03
None and Maranon TeMnlcal Repot Mgni M18
Off Site Traffic Noise Calculations
Project:OCWD Water Production Enhancement Project
Off-site Construction Traffic Noise
Traffic Volumes Lgq CNEL
Roadw ISe mint AM PM ACT ROW 25 Feat W Fast ROW 25 Feet I 50 Feat
B.khuml Street 43 55.9 53.2 51.6 52.9 50.2 46.6
0 0
0 0
0 0
B 0
Traffic Volumes Lac
CNEL
Roadw ISm e int AM PM ACT ROW 1 25 Feel 1 50 Feet ROW 25 Feet 1 50 Feet
0
0
0
0
0
Traffic Volumes L¢ CNEL
RuadW ISe mart AM PM ACT ROW 25 Feel 50 Feat ROW 25 Feet 1 50 Fast
0
0
0
0 F n F F n
0 F F F F
CNEL
Summary 25 M1.from ROW At ROW
Project Cumulative Project Cumulative
Roadway/Segment Increment Increment Increment Increment
Brookhurs(Slreel
0
0
0
0
TENS 1.1 rTrucksrrOCWD 7/ M)16
Orange County Water District
Water Production Enhancement Project
Final Initial Study/Mitigated Negative Declaration
Response to Comments
State Clearinghouse No. 20160811067
Prepared By
Orange County Water District
18700 Ward Street n
Fountain Valley, CA 92708
Contact: Daniel Bott �f
October 2016 SINCE 19JJ
Table of Contents
Section Page
SECTION 1.0 PURPOSE ........................................................................................1 d
SECTION 2.0 COMMENT LETTERS ❑ RESPONSE TO COMMENT LETTERS....211
Table
Table 1: Water Production Enhancement Project ........................................................211
Water Production Enhancement Project Final ISMND—Response to Comments i
Section 1
SECTION 1.0 PURPOSE
In compliance with the reniirements of the California Endronmental Quality Act [CEQAo
Public Resources Code Section 21000 at se¢ and the CEQA Guidelines, the Orange
County Water District IDCWDohas prepared a Draft Initial Study/Mitigated Negatila
Declaration [Draft IS/MNDOtor the Water Production Enhancement Project [State
Clearinghouse No. 2016081106711
The Draft IS/MND was circulated for public redew from August 30, 2016 to September
28, 2016. Except for an acknowledgement letter from the State Clearinghouse that
OCWD has complied with the CEQA public redew process, no other public comments
were receded. No response was rewired. The State Clearinghouse acknowledgement
letter is prodded in Section 2.0.
Water Production Enhancement Project Final ISMND—Response to Comments 1-1
Section 2
SECTION 2.0 COMMENT LETTERS & RESPONSE TO COMMENT
LETTERS
In accordance with Section 15088 of the CEQA Guidelines, the OCWD as the Lead
Agency has elaluated the comments retailed on the Water Enhancement Project Draft
IS/MND. Below in Table 1 is a listing of the public agencies that redewed and prodded
comments on the Draft IS/MND. Each comment letter and indiddual comments are
numbered so that can be cross referenced with responses.
Table 1: Water Production Enhancement Project
Letter Sender Date Received
A State Clearinghouse September 26, 2016
Water Production Enhancement Project Final ISMND—Response to Comments 2-1
l Beyer rty�
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STATE OF CALIFORNIA
GOVERNOR'S OFFICE of PLANNING AND RESEARCH PI&M I
STATE CLEARINGHOUSE AND PLANNING UNIT 6wcNl'�
EDMUND O. BROWN JR. Km Aixx
DUVRRNOR DIRKTUR
September 27,2016
Daniel Bon
Orange County Water District
18700 Ward St
Fountain Valley,CA 92708
Subject: Water Production Enhancement Project
SCHB: 2016081067
Dear Daniel BOB:
The Smle Clearm ehouse submitted the above named Mili'�tl d cyotivr Inr laration to selected slate
^ci ( t,, I cl lh0 rt vlcw prI OIL! -1 ned On �_plonhcr le,'Ole. and uo 'll l cncics_ohm11
nmimonts by that Mute- 'Phis letter achnoWlcdgca that you have complied with the State Clearinghouse
rrcle.I royuirements for draft environmental documents,pursuant to the California Envronmental Quality
\It
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'j'I" r 11110111. 11 "It'l,evc'a qucs( ... about the nl eo-nam,xl pn I rot, please infer to the
1,1, filrll Slmn I Ird.m;housc number When conmatinp this 111Lm.
OUI1111, tl:lk l:^aIn i, house
! IA Ialh oreet P.O.Box 3044 Sacramento,California 95812.3044
(916)445.0613 FAX(916)323-3018 www.opr.ca.gov