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IV. ENVIRONMENTAL IMPACT ANALYSIS
N. UTILITIES/SERVICE SYSTEMS
INTRODUCTION
This section of the Draft EIR analyzes the potential for adverse impacts related to utilities and service
systems resulting from implementation of the proposed Gateway Business Park Master Plan (Master
Plan) and Phase 1 Precise Plan (Precise Plan). This section of the Draft EIR describes utilities and service
systems serving the project site, information on regulations relating to this issue, and an analysis of
potential program-level impacts to utilities and service systems associated with the Master Plan
development and project-level impacts associated with the Precise Plan. Where appropriate, this section
provides project level analysis for the Phase 1 Precise Plan, and program level analysis for the remainder
of development proposed by the Gateway Business Park Master Plan. A regulatory framework is also
provided in this section describing applicable agencies and regulations related to utilities and service
systems.
Preparation of this section used data from various sources. These sources include the Water Supply
Assessment (WSA) prepared by the California Water Service Company (Cal Water) on December 2,
2008; City of South San Francisco General Plan prepared by Dyett & Bhatia and adopted in October
1999; the East of 101 Area Plan prepared by Brady and Associates and adopted in July 1994; and
communications with local service providers.
No comment letters related to utilities were received in response to the June 16, 2008 Notice of
Preparation (NOP) or the Revised October 22, 2008 NOP circulated for the project. The NOP and
comment letters are included in Appendix A of this Draft EIR.
ENVIRONMENTAL SETTING
Water
Domestic Water
Cal Water's South San Francisco District (SSF District) is located in northern San Mateo County
approximately six miles south of the City of San Francisco. The SSF District serves the communities of
South San Francisco (where the project site is located), Colma, a small portion of Daly City, and an
unincorporated area of San Mateo County known as Broadmoor, which lies between Colma and Daly
City. The SSF District water supply is a combination of purchased water and groundwater from Cal
Water- owned wells.
This project is not specifically covered in Cal Water's 2006 SSF District Urban Water Management Plan
(UWMP), which was adopted on December 15, 2006. Therefore, the project's water requirements and
how they would be met are addressed in the WSA prepared for the project included as Appendix I to this
Draft EIR.
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Cal Water purchases treated surface water from the San Francisco Public Utilities Commission (SFPUC).
This supply is predominantly from the Sierra Nevada, delivered through the Hetch Hetchy aqueducts, but
also includes treated water produced by the SFPUC from its local watersheds and facilities in Alameda
and San Mateo Counties. In 1984, Cal Water, along with 29 other Bay Area water suppliers, signed a
Settlement Agreement and Master Water Sales Contract (Master Contract) with San Francisco,
supplemented by an individual Water Supply Contract. These contracts, which expire in June 2009,
provide for 184 million gallons per day (mgd), expressed on an annual average basis of supply assurance
to SFPUC wholesale customers collectively. Cal Water's supply assurance is 35.39 mgd or 39,642 acre
feet per year. Although the Master Contract and accompanying Water Supply Contract expire in 2009,
the Supply Assurance (which quantified San Francisco's obligation to supply water to its individual
wholesale customers) survives their expiration and continues indefinitely.
The SFPUC can meet the demands of its retail and wholesale customers in years of average and above
average precipitation. The Master Contract allows the SFPUC to reduce water deliveries during droughts,
emergencies and for scheduled maintenance activities. The SFPUC and all wholesale customers adopted
an Interim Water Shortage Allocation Plan in 2000 to address the allocation of water between San
Francisco and wholesale customers in aggregate and among individual wholesale customers during water
shortages of up to 20 percent of system-wide use. This plan, which also expires in June 2009, is
described in more detail in the SSF UWMP.
Groundwater is extracted from Cal Water-owned wells in the Merced Formation of the Colma Creek
Basin, a sub-basin of the Merced Valley Groundwater Basin. Groundwater supplies ten to fifteen percent
of the SSF District's water demand. In June 2003, Cal Water entered into an agreement with the SFPUC
to conduct a conjunctive use test program its practicality and potential impact on the regional
groundwater basin and Lake Merced recovery. The conjunctive use program was for a three-year
duration. In 2008, Cal Water's wells are being put back into operation.
Active wells in the SSF District have total capacity of 1,534 AFY. The total supply capacity of SSF
District wells is expected to increase slightly over time as new wells are installed. For the purpose of this
WSA analysis, groundwater supply projections are based on current well capacity. Based on historical
data and future demand projections, contracted treated water deliveries from SFPUC are expected to
increase by about 1,200 AF between 2008 and 2028 or about 60 AF per year. Therefore, SSF District
annual demand of SFPUC supply in 2028 is 8,496 AFY, resulting in a total supply of 10,030 acre feet per
year (AFY) in 2008 during a normal hydrologic year.
The 2008 estimated average demand for the SSF District is 8,830 AFY. The estimated average annual
demand for the SSF District in 2013 is 9,070 AFY or 8.09 mgd. Therefore, the forecasted increase in
average day demand from 2008 to 2013 (5-year period) is 240 AFY or 214,000 gpd. The estimated
average annual demand for the SSF District in 2028 is 10,030 AFY or 8.95 mgd. Therefore, the increase
in average day demand from 2008 to 2028 (20-year period) is 1,200 AFY or 1.07 mgd.
The water distribution system in the East of 101 Area was designed and constructed to meet industrial
water demands. Existing water distribution mains within the site include a 12-inch main along Gateway
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Boulevard and 16-inch mam along Oyster Point Boulevard. There is no eXlstmg on-site public
distribution system. Private on-site services for the existing six buildings include typical domestic water,
fire and irrigation service.
The City's historical water use patterns illustrate the differences between residential or commercial and
industrial water use. Industrial water use is most prevalent in the East of 101 Area.1 While industrial
water consumption showed no consistent pattern of decrease during the drought in the late 1980s and
early 1990s, residential and commercial water use levels declined considerably. Therefore, compared to
the historic reduction of residential and commercial water use during drought, industrial water use
appears inelastic and therefore represents a critical issue for drought planning.
Fire Protection
Discussion of fire protection services is included in Section IV.L (Public Services). This section addresses
the infrastructure to deliver the required water used for fire protection. Fire protection is currently
provided on the site by water provided by CWSc. The water system consists of a network of 12 and 10-
inch lines.
Waste Water
Waste Water Collection System
Sewage and wastewater generated within the City is collected through the City's sewer system and is
disposed of and treated at the South San Francisco/San Bruno Water Quality Control Plant (WQCP). The
City's sanitary sewer system, east of Highway 101, has an interconnecting network of approximately 13
miles of 6-inch to 30-inch diameter gravity sewer mains, force mains, and nine pump stations, which
function together to bring wastewater from individual homes and businesses to the WQCP. Some pump
stations act as tributaries to a few stations that handle most of the wastewater from large portions of the
community.
Older portions of the City's sewer system are subject to infiltration and inflow (III) problems. III
problems occur when leaks and breaks in sewer pipes, or cross connection with the storm drain system,
result in the entrance of rainfall and other water from the storm drain system into the sewer pipes. There
are also some reliability issues at pump stations and areas where sewer lines have sunk, decreasing
hydraulic capacity and increasing the potential deposit of solids.
Existing facilities serving the site and the East 101 Area are described as follows:
. Oyster Point Boulevard has a 10 and 12-inch pipe installed circa 1982 as part of the Gateway
Assessment District improvements discharging to Pump Station 2. This pipe collects all flows
from the Oyster Point basin and existing Buildings 800, 850, 900, and 1000 Gateway Boulevard.
City of South San Francisco, City of South San Francisco General Plan: Existing Conditions and Planning
Issues, 1997.
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. Pump Station 2 is located southwest of the Oyster Point Boulevard and Gateway Boulevard
intersection. Water flows through a lO-inch force main to the existing 15-inch pipe located in
Gateway Boulevard. The current final Sewer System Master Plan (SSMP) prepared by Carollo
Engineers, dated September 2002, recommends that the pump station capacity be increased by
replacing the existing pumps to handle future peak wet weather flows, increasing the firm
capacity to 1,400 gpm.
. Gateway Boulevard has a 15-inch pipe installed circa 1982 as part of the Gateway Assessment
District improvements which discharges south to Pump Station 4. This pipe collects flows from
existing Buildings 700 and 750 Gateway Boulevard.
. Pump Station 4 is located northeast of the intersection of Mitchell Avenue and Harbor Way. This
station collects and pumps almost all flows from the East of 101 Area sub-basins to the WQCP
through an existing 21-inch force main. The current SSMP recommends that the pump station
capacity be increased by replacing the existing pumps to increase future firm capacity of 9,000
gpm.
Based on the SSMP, Pump Station 2, located at 955 Gateway Boulevard, has an existing firm capacity of
1,000 gallons per minute (gpm? and currently does not meet the existing peak sewer discharge. In
addition, Pump Station 4 needs to be upgraded to improve reliability. The upgrade of Pump Station 4 is
critical to serving the proposed growth under the East of 101 Area Plan, and has been included in the
Downtown/Central Redevelopment plan for funding. Necessary system improvements, including Pump
Stations 2 and 4, are identified in the SSMP, which also establishes a program for implementing the
improvements. The SSMP estimates cost share of the improvements, with respect to how they relate to
existing users and future users. Costs from existing users are recovered through rates. Impact fees,
collected prior to the issuance of a building permit, fund the improvements as they relate to future users.
The SSMP lists the 2002 average dry weather flow in 2001 as 1.5 mgd? The SSMP also identified
deficiencies in the current system to handle current and projected flows. An addendum to the SSMp4
recalculated demands based on the planning assumptions that have changed. These changes include land
use, development densities and intensities, and population growth rates assumptions. The revised flow
estimates were less than previously calculated. Other than adding upgrades to Pump Station 6 and Pump
Station 8, the recommendations did not change. As a result, the project list in the SSMP is still applicable.
Further development in the East of 101 Area may require that the City undertake extensive improvements
to the existing sewer treatment facilities above and beyond those sewer system improvements already
budgeted in the Capital Improvement Program. Although required by increased development in the East
of 101 Area, most of the sewer treatment improvements will result in citywide benefits. For this reason,
the City has determined that it is appropriate that most of these improvements be financed through the
2
3
Carollo Engineers, 2002 East of Highway 101 Sewer System Master Plan, page 4-7.
Carollo Engineers, 2002 East of Highway 101 Sewer System Master Plan, page 5-1.
Carollo Engineers for the City of South San Francisco, Addendum to the City of South San Francisco East of
Highway 101 Sewer Master Plan, May 2007.
4
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issuance of sewer revenue bonds. The revenues required to pay off the bonds would be collected through
increased rates charged to current and future users of the sewer system.
Solids from wastewater treatment process are referred to as sludge. Sludge consists of inert solids from
the wastewater and microbial biomass created during treatment. Sludge is thickened, anaerobically
digested, and then dewatered. Final disposal of sludge is by trucking to a landfill for disposal.
The City currently does not limit the amount of flow or the peak pollutant concentrations that industries
can discharge. However, the East of 101 Area Plan requires projects in the East of 101 Area that are likely
to generate large quantities of wastewater to lower their treatment needs through recycling, on-site
treatment, graywater irrigation, and other programs where feasible. Onsite utilities are primarily located
within buildings and underground.
Water Quality Control Plant
The South San Francisco and San Bruno Water Quality Control Plant (WQCP), located in South San
Francisco, will serve the proposed project. The WQCP operates under NPDES No. CA0038130 and
Waste Discharge Requirements R2 2003-0010. The current facility has an average dry weather flow
capacity to provide secondary level treatment for 13 mgd of domestic, commercial, and industrial
wastewater from the cities of South San Francisco and San Bruno, portions of the city of Daly City, and
the Town of Colma.5 The WQCP can handle a peak hourly wet weather flow of 62 mgd and the current
average dry weather flow is 9 mgd.6 The cities of South San Francisco and San Bruno are each entitled up
to 50 percent of the available treatment capacity. Treated wastewater is pumped through a 54-inch force
main located along the Lower Campus, then discharged 2 miles out into San Francisco Bay via a joint
outfall pipe operated by the North Bayside System Unit (NBSU), which is the joint powers authority
responsible for operation of certain shared transport, treatment, and disposal facilities. The NBSU
includes the Cities of Millbrae, Burlingame, South San Francisco and San Bruno, and the San Francisco
International Airport (SIFA) (both the Airport's Industrial Wastewater Treatment Plant and Water Quality
Control Plant).
The treatment facility consists of bar screens, grit chambers, primary sedimentation, aeration tanks, final
clarifiers and disinfection equipment. NBSU de chlorinates the combined effluent prior to discharging via
the joint NBSU outfall off Point San Bruno.
The WQCP had five discharge violations during 2003, as reported in RWQCB Order No. R2 2004-0075.
Since 2003 there have been a total of four violations; three occurred in 2005 and one in 2006. Effluent
concentrations of oils and grease, cyanide, and biological oxygen demand (BOD), settleable solids, and
fecal coliform were exceeded. These results are summarized in Table IV.N-1. No violations have been
reported during the 2004 and 2007 annual reports.
5
Ken Navarre, Assistant Superintendant, South San Francisco Water Quality Control Plant, written response to
request for service information, July 10, 2008.
Ibid.
6
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Table IV.N-l
WQCP Violations (2003-June 30, 2008)
alate ......... ri...... Lhnit .".,; . Value
..."..
20031
4/1/2003 Oil and Grease daily 20 mg/L 35 mgIL
maXImum
7/1/2003 Cyanide daily maximum IOg/L 19 gIL
10/4/2003 BOD weekly average 45 mg/L 52 mg/L
10/11/2003 BOD weekly average 45 mg/L 54 mg/L
10/31/2003 BOD monthly average 30 mg/L 37 mg/L
20052
1/5/2005 Test! Specie Eff llSamp 70% 0%
90th% %Sur minimum
2/15/2005 Total Settleable Solids Eff 0.2 mL/hour 3.5 mL/hour
Instant Max
3/23/2005 Fecal Coliform Eff 400 mpn/100mL 490 mpn/100mL
IOSamp 90th%
20062
10/30/2006 Oil and Grease monthly 10 11.10
average
Sources:
1 RWQCB NO R2-2004-0075.
2 Johnson Lam, ERS Program Manager and Water Resources Control Engineer, Regional Water Quality Control Board - San
Francisco Bay Region, em ail correspondence with CAJA staff August 27, 2009.
Surface Water and Storm Drainage
The project site is located near the eastern shoreline of the City overlying artificial fill and Bay mud. The
East of 101 Area generally slopes downward to the east, toward San Francisco Bay. The project site is
relatively flat. Average annual precipitation is between 18 and 22 inches per year, increasing to 26 inches
in the upper watersheds west of the City. Approximately 90 percent of the precipitation is received
between November and ApriC Runoff in the hills is relatively rapid because of the steep slopes and clay
soils, and is slower in the flat lowland areas. Some infiltration into the ground occurs, but because the
City is largely developed with a high proportion of impermeable surface, runoff is relatively high. Runoff
throughout the City is collected in the City's storm drainage system, which discharges to Colma Creek or
San Francisco Bay.8
Colma Creek is the City's main natural drainage system. The Colma Creek watershed is bounded on the
northeast by San Bruno Mountain and on the west by the ridge traced by Skyline Boulevard.9 It
discharges to San Francisco Bay south of the project site near Belle Air Island. However, Colma Creek
does not intersect the project site, nor does the project site drain to Colma Creek. No other creeks or
natural surface drainages are in the master plan area. Instead, surface water and stormwater runoff in the
8
9
Dyett & Bhatia, City of South San Francisco General Plan: Existing Conditions and Planning Issues,
September, 1997.
Ibid.
Ibid.
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master plan area are collected by the City's storm drainage system and discharged to San Francisco Bay
to the east of the project site.
The existing drainage system in the East of 10 1 Area is generally designed and constructed for industrial
development.1O The storm drainage system for the project site consists of underground pipes and outfalls
emptying into San Francisco Bay at various locations. The pipes are reinforced concrete pipe (RCP) or
high-density polyethylene (HDPE). The outfalls to the San Francisco Bay are both above and below the
mean high tide elevation of 3.1 feet. Outfalls below the mean high tide water elevation are likely to
experience flooding when a heavy storm event happens during high tide water elevations. The storm
drainage system in the master plan area is gravity flow and does not require pumps to transport the flows.
The majority of the project site consists of developed land, with approximately 22 percent pervious
surfaces.
Stormwater point and non-point source discharges are a major source of pollution in San Francisco Bay
from the City, as the City's storm drainage system discharges directly into the Bay. Stormwater quality in
the master plan area, and in the East of 101 Area as a whole, is generally influenced by typical urban
pollutants, such as construction sediments, vehicular fuel and oil, household cleaning surfactants, and
landscape pesticides, fertilizers, and herbicides. However, Bay water in the vicinity of the City is
considered to be generally good because this area of the Bay tends to be well-mixed.]]
Commercial development could degrade water quality through industrial pollutant discharges. Indirect
degradation of surface water quality could affect fish and wildlife species in local water bodies. To
combat this problem, the San Mateo Countywide Stormwater Pollution Prevention Program (STOPPP), a
partnership of the City/County Association of Governments (C/CAG), each incorporated city and town in
the county, and the County of San Mateo, has prepared a Best Management Practices (BMPs) plan to
control pollutants in their stormwater system. Compliance with the permit requirements for non-point
source stormwater discharge under the National Pollutant Discharge Elimination System (NPDES) also
requires the property owner of all construction projects over 1 acre in size to obtain a stormwater
discharge permit. The WQCP operates under STOPPP's Joint Municipal NPDES Permit. The Regulatory
Framework section, below, further describes the STOPPP and NPDES programs.
According to the Water Quality Control Plan for the San Francisco Bay Region (Basin Plan), beneficial
uses of South San Francisco Bay, to which the project site discharges, include wildlife habitat, shellfish
harvesting, fish spawning, preservation of rare and endangered species, fish migration, estuarine habitat,
navigation, water contact and non-contact recreation, commercial and sport fishing, and industrial service
supply.12 However, the Bay is listed on the 2002 CW A 303(d) list as an impaired water body. The various
pollutants and stressors listed as inflicting the Lower and Central San Francisco Bay are chlordane,
dichloro-diphenyl-trichloroethane (DDT), diazinon, dieldrin, dioxin compounds, exotic species, furan
10 Brady and Associates for the City of South San Francisco, East of 101 Area Plan, July, 1994.
Dyett & Bhatia, City of South San Francisco General Plan: Existing Conditions and Planning Issues,
September, 1997.
California Regional Water Quality Control Board - San Francisco Bay Region, Water Quality Control Plan
(Basin Plan), January 18,2007, Table 2-1.
11
12
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compounds, mercury, mercury (sediment), polycyclic aromatic hydrocarbons (PAHs), polychlorinated
biphenyls (PCBs), PCBs (dioxin-like), and selenium. Causes contributing to impairment include urban
runoff, other non-point sources, ballast water (exotic species), municipal point sources, industrial point
sources, resource extraction (mercury) and agriculture.
Solid Waste
Solid waste is collected from the City's homes and businesses, including the project site, by the South San
Francisco Scavenger Company.13 The Scavenger Company also serves the City of Brisbane, the City of
Millbrae, and the San Francisco International Airport.14 After collection, waste is brought to the
Scavenger Company's Blue Line Transfer, Inc. facility, a public disposal and recycling center located just
south of the project site at 500 East Jamie Court. The Blue Line Transfer facility has a permitted capacity
of 2,000 tons per day, but currently receives an average of approximately 800 tons per day,15
approximately 0.9 tons (0.1 percent) of which are currently from the project site.16
From the Blue Line Transfer facility, non-recyclable wastes are then deposited at the Ox Mountain
Sanitary Landfill near the City of Half Moon Bay. The Ox Mountain Sanitary Landfill is the only
remaining landfill in the County that will accept South San Francisco Scavenger Company waste. In
2005, the City landfilled approximately 85,091 tons.17 The landfill has a permitted maximum disposal of
3,598 tons per day.18 As of 2000, the landfill has exceeded its permitted capacity of 37.9 million cubic
yards by approximately 6.7 million cubic yards (17.8 percent). However, the closure date is planned for
2018.
The project site's existing baseline generation is 329 tons of non-hazardous waste per year,19 of which
220.43 tons (67 percent) are landfilled and 108.57 tons (33 percent) are recycled. No solid waste is
incinerated in the master plan area?O The master plan area's contribution to the amount of solid waste
landfilled by the City is approximately 0.003 percent.
13
Formosa, Paul, Chief Financial Officer, South San Francisco Scavenger Company, phone conversation with
CAJA staff, July 28, 2008.
South San Francisco Scavenger Company, Inc., website: http://www.ssfscavenger.com/transfer/index.cfin.
accessed August 3, 2008.
Formosa, Paul, Chief Financial Officer, South San Francisco Scavenger Company, phone conversation with
CAJA staff, July 28, 2008.
City of Los Angeles Bureau of Sanitation, Solid Waste Generation, 1981. Generation factor for office land use
is 6 lbs per 1,000 sf The existing daily solid waste generation is calculated as follows: 284,000 existing sf x (6
lbs / 1,000 sf! day) = 1, 704lbs / day (or 0.852 tons).
California Integrated Waste Management Board, Jurisdiction for the City of South San Francisco, website:
http://www.ciwmb.ca.gov/Profiles/Juris/JurProfile2. asp? RG=C&JURlD= 511 &JUR=South +San + Francisco,
accessed August 29, 2008.
California Integrated Waste Management Board, Active Landfills Profile for Ox Mountain Sanitary Landfill
(41-AA-0002), website:
http://www.ciwmb.ca.gov/Profiles/F acility/Landfill/LFProfile 1. asp ?COID= 7 &F ACID =41-AA -0002, accessed
September 4, 2008.
The existing annual solid waste generation is calculated as follows: (0.9 tons / day) x (365 days / year) = 329
tons.
Chamberlin Associates, 2008.
14
15
16
17
18
19
20
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A description of hazardous waste generation, collection, and disposal services in the master plan area is
provided in Section IV.G Hazards/Hazardous Materials.
Electricity and Natural Gas
Electricity
Pacific Gas and Electric (PG&E) provides natural gas to the master plan area. The underground 12.47 kV
distribution system that serves the area is configured in a looped network from the East Grand Avenue
substation. This enables PG&E some flexibility to continue to provide service to buildings through
switching, should problems be encountered with cabling. Each building or a cluster of buildings is
metered at either the primary or secondary rates. Most buildings are metered at the secondary 480 or 208
volt rates. PG&E has confirmed the ability to provide sufficient capacity to accommodate the proposed
. 21
project.
Natural Gas
PG&E provides natural gas to the master plan area. The high pressure gas distribution system is metered
at each building and is configured in a loop system that is served from three interconnected underground
pipelines; 3-inch Pipeline at Grandview; 4-inch pipeline at Forbes Avenue; 8-inch pipeline at East Grand
Avenue. PG&E has confirmed that it has sufficient capacity to accommodate the proposed project.22
Regulatory Setting
Federal
Clean Water Act
The CW A is the principal statute governing water quality. The statute's goal is to end all discharges
entirely and to restore, maintain, and preserve the integrity of the nation's waters, with an interim goal of
providing water that is both fishable and swimmable. The CW A regulates both the direct and indirect
discharge of pollutants into the nation's waters. It mandates permits for wastewater and stormwater
discharges, regulates publicly owned treatment works that treat municipal and industrial wastewater,
requires states to establish site-specific water quality standards for navigable bodies of water, and
regulates other activities that affect water quality, such as dredging and the filling of wetlands. The CW A
was enacted in 1977 as a series of amendments to the federal Water Pollution Control Act of 1948.
Section 303(d). Section 303(d) of the CW A requires each state to identify waters that will not achieve
water quality standards after application of effluent limits. For each water and pollutant, the state is
required to propose a priority for development of load-based (as opposed to concentration-based) limits
called total maximum daily loads (TMDLs). The TMDL determines how much of a given pollutant can
21
Bueb, Paul, Industrial Power Engineer, Pacific Gas and Electric Company, written correspondence with BKF
Engineers Surveyors Planners, May 2, 2008.
22 Ibid.
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be discharged from a particular source without causing water quality standards to be violated. Priorities
for development of TMDLs are set by the state, based on the severity of the pollution and uses of the
waters.
National Pollutant Dischan!e Elimination System (NPDES)
The NPDES permit system was established in the CW A to regulate both point source discharges and non-
point source discharges from construction, industrial, and municipal activities to surface waters of the US.
For point source discharges, each NPDES permit contains limits on allowable concentrations and mass
emissions of pollutants contained in the discharge. For non-point source discharges, the NPDES program
establishes a comprehensive stormwater quality program to manage urban stormwater and minimize
pollution of the environment to the maximum extent practicable. As permitted under the CW A, authority
for issuing NPDES permits has been delegated by the EPA to the San Francisco Bay Regional Water
Quality Control Board (RWQCB) in the San Francisco Bay Area.
The State Water Resources Control Board (SWRCB) has adopted a separate NPDES General Permit for
stormwater discharge associated with construction activity (NPDES Permit No. CAS000002). Under this
permit, developers proposing construction activity that disturbs more than 1 acre of land must submit a
Notice of Intent (NOI), develop a Stormwater Pollution Prevention Plan (SWPPP), conduct monitoring
and inspections, retain records of the monitoring, report incidences of noncompliance, and submit annual
compliance reports. The SWPPP must address both grading/erosion impacts and non-point source
pollution impacts of the development project, including post-construction impacts and
sampling/monitoring requirements. Individual development proposed under the project that would disturb
more than 1 acre of land would be required to obtain and comply with a NPDES General Permit for
construction activity.
Stormwater NPDES permlttmg for certain classes of industrial activities, including manufacturing
activity, are regulated under the Industrial Activities General Permit adopted by the SWRCB (NPDES
Permit No CAS000001). To comply with the conditions of this permit, facility operators are required to
submit a NOI, develop a SWPPP, and conduct stormwater monitoring, in addition to submitting annual
reports by July 1 of each year.
Municipal stormwater in the City is regulated by STOPPP's Joint Municipal NPDES Permit (No.
CAS0029921, Order No. R2-2004-0060, originally issued in 1999) for stormwater quality management.
STOPPP and its NPDES Permit are described further in "San Mateo Countywide Stormwater Pollution
Prevention Program," below.
State
Urban Water Mana2:ement Plannin2: Act
The Department of Water Resources (DWR) provides urban water management planning services to local
and regional urban water suppliers. In 1983, the California Legislature enacted the Urban Water
Management Planning Act (Water Code Sections 10610 through 10656). The Act states that every urban
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water supplier that provides water to 3,000 or more customers, or that provides over 3,000 acre-feet of
water annually, should make every effort to ensure the appropriate level of reliability in its water service
sufficient to meet the needs of its various categories of customers during normal, dry, and multiple dry
years. The Act describes the contents of the Urban Water Management Plans (UWMPs) as well as how
urban water suppliers should adopt and implement the plans. It is the intention of the Legislature, in
enacting this part, to permit levels of water management planning commensurate with the numbers of
customers served and the volume of water supplied.
Water Supply Assessments (SB 610)
Effective January 1, 2002, California, through Senate Bill 610 (SB 610), requires that a city or county,
and the associated public water system, prepare a Water Supply Assessment (WSA) for projects that meet
certain criteria. Three criteria include (1) a project creating the equivalent demand of 500 residential units,
(2) a proposed shopping center or business establishment employing more than 1,000 persons or having
more than 500,000 sf of floor space, and (3) a commercial office building employing more than 1,000
persons or having more than 250,000 sf of floor space. The project meets the criteria for requiring a WSA
because the project is projected to employ over 1,000 persons and would include development of
approximately 1 million additional square feet of office, research and development, amenities, and
parking structures. The purpose of the WSA is to assess the adequacy of water for the proposed project
over a 20-year horizon during normal, single dry, and multiple dry year conditions. The WSA completed
for the project is attached as Appendix G to this Draft EIR.
Water Qualitv Control Act (Porter-Colo2:ne Act)
The Porter-Cologne Water Quality Control Act is the primary state regulation that addresses water
quality. The requirements of the Act are implemented by the SWRCB at the state level, and the RWQCB
at the regional level. The SWRCB, as authorized by the Act, has promulgated regulations in Subchapter
15 of Title 23 of the California Code of Regulations (CCR) designed to protect water quality from the
effects of waste discharges to land. Under Subchapter 15, wastes that cannot be discharged directly or
indirectly to waters of the state (and therefore must be discharged to land for treatment, storage, or
disposal) are classified to determine specifically where such wastes may be discharged.
Pretreatment Pro2:ram and Storm Water Pollution Prevention Pro2:ram
The City's Office of Environmental Compliance administers a Pretreatment Program and a Storm Water
Pollution Prevention Program mandated by the state. The two programs regulate and control the
concentrations of wastewater and stormwater pollutants discharged by industrial, commercial, and
residential dischargers. Pollution prevention information is distributed to residents as well as schools and
businesses within the service area. These programs are enacted under Chapter 14.08 (Water Quality
Control) ofthe SSFMC, which is described in "City of South San Francisco Municipal Code," below.
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California Inte2rated Waste Mana2ement Act of 1989 (AB 939)
To minimize the amount of solid waste that must be disposed of by transformation and land disposal, the
State Legislature passed Assembly Bill 939, the California Integrated Waste Management Act of 1989
(AB 939), effective January 1990. According to AB 939, all cities and counties in California are required
to divert 25 percent of all solid waste to recycling facilities from landfill or transformation facilities by
January 1, 1995, and 50 percent by January 1,2000. The City of South San Francisco has not yet met this
goal. Between 2001 and 2004, the City has achieved a diversion of rate ranging between 40 and 48
percent. The City has submitted an application for a time extension with the California Integrated Waste
Management Board (CIWMB) until December 2005 to meet the 50 percent goal, but the CIWMB's
review of the City's application has been delayed.
Solid waste plans are prepared by each jurisdiction to explain how each city's AB 939 plan is integrated
with its county plan. The plans must promote in order of priority: source reduction, recycling and
composting, and finally, environmentally safe transformation, and land disposal.
Waste disposal efforts in the County of San Mateo are governed by the Countywide Integrated Waste
Management Plan. The County's Health Department, Environmental Health Division, acts as the solid
waste disposal enforcement agency, coordinating efforts and granting waste disposal permits.
California Code of Re2ulations (CCR) Title 24
New buildings in California are required to conform to energy conservation standards specified in Title
24 of the CCR. The standards establish "energy budgets" for different types of residential and
nonresidential buildings, with which all new buildings must comply. The energy budget has a
space conditioning component and a water-heating component, both expressed in terms of energy (British
thermal units, BTU) consumed per year. The regulations allow for trade-offs within and between the
components to meet the overall budget. Energy consumption of new buildings in California is regulated
by the State Building Energy Efficiency Standards, embodied in Title 24 of the CCR. The efficiency
standards apply to new construction of both residential and nonresidential buildings, and regulate energy
consumed for heating, cooling, ventilation, water heating, and lighting. The building efficiency standards
are enforced through the local building or individual agency permit and approval processes. The City
requires all new buildings to meet Title 24 standards.
Regional
Water Qualitv Control Plan for the San Francisco Bav Re2ion
Prepared by the RWQCB, the Water Quality Control Plan (Basin Plan) for the San Francisco Bay Region
identifies surface waters in the region as consisting of inland surface water (freshwater lakes, rivers, and
streams), estuaries, enclosed bays, and ocean waters. Historic and ongoing wasteload contributions to
surface water bodies in the region come from upstream discharges carried into the region via Delta
outflow, direct input in the forms of point and nonpoint sources, and indirect input via groundwater
seepage (SFB RWQCB 1995). The Basin Plan describes the water quality control measures that
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contribute to the protection of the beneficial uses of the Bay watershed. The Basin Plan identifies
beneficial uses for each segment of the Bay and its tributaries, water quality objectives for the reasonable
protection of the uses, and an implementation plan for achieving these objectives.
Local
San Mateo Countywide Stormwater Pollution Prevention Pro2:ram (STOPPP)
The STOPPP is a partnership of the City/County Association of Governments (C/CAG), each
incorporated city and town in the county, and the County of San Mateo. Many of STOPPP's activities are
coordinated through the City/County Association of Governments of San Mateo County. The STOPPP
functions under a Joint Municipal NPDES Permit (No. CAS0029921) for stormwater quality
management, as authorized by the RWQCB. This partnership also relies on each of the municipalities to
implement local stormwater pollution prevention and control activities for their local storm drain systems.
The STOPPP includes the following:
. Provisions for a model ordinance
. Identification of BMPs, including street sweeping, storm drain stenciling, spill clean-up, and
annual catch basin maintenance
. Measures for extensive public education and public awareness
. Pollutant source identification and water quality measurement, and elimination of illicit
discharges
. Structural and non structural controls for commercial and residential areas, and controls for
industrial facilities
. Controls for new development and construction sites and other elements
The STOPPP Stormwater Management Plan (SWMP) describes measures for the prevention and control
of stormwater pollution. The SMWP serves as part of the basis of STOPPP's third NPDES permit to be
reissued by the RWQCB (NPDES Permit No. CAS0029921), which expires in 2009. The SWMP, in
conjunction with the reissued permit adopted by the RWQCB, is designed to enable STOPPP to meet
requirements of the CW A. Because individual projects proposed under the project would apply for
coverage under the STOPPP NPDES Municipal Permit, the SWPPP prepared for each individual project
must to be consistent with the SWMP.
Because much of Colma Creek flows through private property, the City has also adopted BMPs aimed at
private land owners to control litter, gain compliance from industrial dischargers, reduce pollutants at
commercial sites, minimize construction sediment, and clean and maintain privately-owned watercourses.
San Mateo County Hazardous Waste Generator Pro2:ram
The County Health Department, Environmental Health Division, has maintained a Hazardous Waste
Generator Program since 1984 aimed at protecting public health and the environment. The California
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Department of Toxic Substances Control (DTSC) authorized the Division at that time to inspect and
regulate non-permitted hazardous waste generators in the County based on the Hazardous Waste Control
Law found in the California Health and Safety Code Division 20, Chapter 6.5 and regulations found in the
California Code of Regulations, Title 22, Division 4.5.
The above referenced regulations require businesses generating any amount of hazardous waste as
defined by regulation to properly store, manage and dispose of such waste. Division staff members
conduct annual inspections at over 1,900 businesses in order to assess compliance with state law and
regulations. Division staff members also conduct surveillance and enforcement activities in conjunction
with the County District Attorney's Office for businesses or individuals that significantly violate the
above referenced law and regulations. Furthermore, staff members respond within 24 hours to complaints
filed with the Division regarding potential violation ofthe aforementioned law and regulations.
City of South San Francisco General Plan
The City's General Plan, which contains implementing policies regarding public services and utilities, is
discussed below.
Water and Wastewater
General Plan Policies 5.3-1-1 and 5.3-1-2 of the Parks, Public Facilities, and Services Element call for the
City to work with CWSC and Westborough Water District to do the following:
. Ensure coordinated capital improvements
. Establish guidelines and standards for water conservation
. Actively promote the use of water-conserving devices and practices in both new construction
and major alterations and additions to existing buildings, including conservation as it relates
to any industrial or commercial construction
Industrial-related conservation measures regarding monitoring of industrial discharges to ensure that
wastewater quality continues to meet various federal, state, and regional standards and to encourage new
projects in the East of 101 Area (such as the MEIR Study Area and vicinity) that are likely to generate
large quantities of wastewater to lower treatment needs through recycling, pretreatment, or other means as
necessary are intended to help limit the demand for wastewater treatment plant capacity.
Policy 5.3-1-6
Monitor industrial discharges to ensure that wastewater quality continues to meet various federal, state,
and regional standards; treatment costs would remain affordable.
Policy 5.3-1-7
Encourage new projects in East of 101 area that are likely to generate large quantities of wastewater to
lower treatment needs through recycling, pretreatment, or other means as necessary.
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Solid Waste
General Plan Policy 8.3-1-1 of the Health and Safety Element calls for the City to continue working
toward reducing solid waste, increasing recycling, and complying with the San Mateo County Integrated
Waste Management Plan. The City has a responsibility to meet regional source reduction and recycling
initiatives in order to achieve state-mandated waste reduction targets and to extend the useful life of
existing landfill facilities. Under this policy, builders are encouraged to incorporate interior and exterior
storage areas for recyclables into new or remodeled buildings (both residential and commercial) to make
recycling activities more convenient for those who use the buildings. Also, the City is encouraged to
explore the feasibility of installing recycling receptacles in parks and public areas, such as the public open
space areas in the project site. Commercial and business parks are encouraged to install recycling
receptacles on their premises. The City is encouraged to explore incentives for businesses to establish
recycling programs.
East of 101 Area Plan
Public Facilities Element
The East of 101 Area Plan's overall intent regarding water, sewer, drainage, and utility facilities for the
East of 101 Area is to provide adequate municipal services to serve all development, and to limit
development ifit would exceed available service capacity.
Policy PF-l
The City shall allow development in the East of 101 Area only if adequate water supply to meet its needs
can be provided in a timely manner.
Policy PF-2
Low flow plumbing fixtures and drought tolerant landscaping shall be installed as part of all new
developments in the area.
Policy PF-7
Projects in the East of 101 Area that would generate large quantities of wastewater shall be required to
lower their wastewater treatment needs through water recycling, on-site treatment, gray water irrigation
and similar programs where feasible.
Policy PF-8
Specific development proposals in the East of 101 Area shall be evaluated individually to determine
drainage and flood protection requirements.
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Policy PF-9
All development in the East of 101 Area shall comply with the NPDES discharge program. Developments
over 5 acres in size shall obtain a storm water discharge permit from the NPDES, which may require
inclusion of on-site treatment of stormwater from parking areas.
Policy PF-iO
During the rainy season, developers shall be required to place appropriate erosion control devices, such as
silt fences, hay bales, etc. during construction activities to minimize the amount of silt directly entering
the Bay or other wetlands.
Policy PF-ll
Utility companies shall be provided early notification for any proposed project that could have an unusual
requirement for water, sewer, gas, electric, or telephone services.
DesiJ!n Element
The overall design policy of the City is to promote quality design; promote a functional, safe, and
attractive environment; preserve the character of the City's heritage; protect public investment and land
values; protect the natural environment; and facilitate evaluation of individual development proposals
through the use of Design Guidelines.
Policy DE-i3
New construction projects shall be required to supply and install street trees and landscaping and
landscaping to meet the City's specifications for the frontages.
. Streetscape planting, irrigation, and hardscape should be designed for minimum maintenance
by City staff.
. Medians should be cobbled and grouted or landscaped with low maintenance plants with
automatic irrigation.
Policy DE-i8
Paths with durable, all-weather surfaces should be located in medians and other landscaped areas within
parking lots to provide convenient pedestrian routes, and reduce wear on landscaped areas.
Policy DE-30
Utility lines serving new development shall be installed underground, unless the City finds that
undergrounding would be financially infeasible for a specific project.
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Financinf! Element
Policies in the Financing Element of the East of 101 Area Plan are intended to form an overall approach
to future discussions about who will pay for improvements and how sources of revenues will be used. In
addition, these policies provide some element of certainty to developers and property owners in terms of
what types of facilities and/or fees they will be expected to provide in conjunction with plans for future
development with the East of 101 Area.
Policy FIN-l
Costs of new infrastructure and public amenities shall be borne by both existing and future development.
Policy FIN-4
Ongoing operating and maintenance costs for new East of 101 Area improvements shall be financed
through ongoing revenues collected as fees, assessments, and taxes generated by future development in
the Area.
City of South San Francisco Municipal Code
Chapter 8.16 (Solid Waste-Scavenf!er Services)
Chapter 8.16 of the SSFMC contains health and sanitation rules and regulations applicable to all lands
and premises within the City. The purpose of Chapter 8.16 is to prevent the accumulation of quantities of
solid waste within the boundaries of the City, except for approved dump sites, in order to protect and
preserve the public health and welfare of City and neighboring communities. The Scavenger Company is
identified in this chapter as the entity with whom the City has contracted to collect, receive, carry and/or
transport solid waste in accordance with the provisions of this chapter.
Chapter 8.28 (Recvclable Materials)
The purpose of Chapter 8.28 is to increase participation rates, improve recyclable material recovery rates,
reduce landfill dependency, and ultimately maintain a cost-effective overall solid waste and recycling
program for the citizens, businesses, and institutions of the City. While the current SSFMC does not
appoint an authorized recycling agent, the Scavenger Company is responsible for providing recycling
services in the City. Also, the SSFMC does not establish recycling goals for the City.
Chapter 14.04 (Stormwater Manaf!ement and Discharf!e Controls)
Chapter 14.04 was created to ensure the future health, safety, and general welfare of the City and to
protect and enhance water quality pursuant to the CW A. The controls include measures to eliminate non-
stormwater discharges to the municipal separate storm sewer; control discharges to the municipal storm
sewer from spills, dumping, or disposal of materials other than stormwater; protect watercourses from
modifications to natural flow; and reduce pollutants in stormwater discharges to the maximum extent
practicable.
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Chapter 14.08 (Water Qualitv)
Chapter 14.08 sets forth requirements for direct and indirect contributors into the City's wastewater
collection and treatment system and enables the City to comply with all applicable state and federal laws
required by the CW A and the General Pretreatment Regulations. The objectives of Chapter 14.08 are the
following:
. To prevent the introduction of pollutants into the municipal wastewater system which will
upset or interfere with the operation of the system or contaminate the resulting sludge
. To prevent the introduction of pollutants into the municipal wastewater system which will
pass through the system, inadequately treated, into receiving waters or the atmosphere or
otherwise be incompatible with the system
. To improve the opportunity to recycle and reclaim wastewaters and sludges from the system
. To provide for equitable distribution of the cost of the municipal wastewater system
. To prevent the exposure of workers at the publicly owned treatment works and the collection
system to chemical hazards
This chapter provides for the regulation of direct and indirect contributors to the municipal waste- water
system through the issuance of permits to certain non-domestic users. Further, through enforcement of
general requirements for all users, the chapter authorizes monitoring and enforcement activities, requires
user reporting, assumes that existing customer's capacity will not be preempted, and provides for the
setting of fees for the equitable distribution of costs.
Under this chapter, the superintendent of the WQCP is responsible for administering, implementing, and
enforcing the provisions of Chapter 14.08.
Chapter 14.12 (Sewer Rates)
Under this chapter, the City establishes a system of sewer rentals and charges for all domestic,
commercial, and industrial uses of the municipal sewer system. This chapter also contains the charges for
sewer service and facilities as provided by the City.
Chapter 13.16 (UndeTf!round Utilitv Installations)
Under this chapter, the City Council may call public hearings to determine whether existing overhead
utilities should be relocated underground. It is the responsibility of the person owning, operating, leasing
or renting the property with the utility in question to follow the provisions set forth as a result of the
public hearing.
Chapter 15.08 (California Buildim! Code)
Under Chapter 15.08, the City adopts and modifies the 2001 California Building Code for application to
developments within the City. This chapter contains construction standards for weather protection,
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foundations, drainage, and grading. Grading activities require a permit from the City Engineer. To obtain
the grading permit, a soils engineering report and engineering geology report must be approved by the
City Engineer. Recommendations in these reports must be incorporated in the grading plans or
specifications. Under Section 15.08.170, construction work is restricted during the rainy season
(November 1 to May 1) so as to minimize erosion.
ENVIRONMENTAL IMPACTS
Methodology
Thresholds of Significance
The following thresholds of significance are based on Appendix G of the 2006 CEQA Guidelines. For
purposes of this Draft EIR implementation of the proposed project could result in potentially significant
impacts to utilities ifthe proposed project would result in any ofthe following:
. Create or contribute runoff water which would exceed the capacity of existing or planned
stormwater drainage systems or provide substantial additional sources of polluted runoff.
. Require or result in the construction of new water treatment, distribution, or conveyance
facilities or expansion of existing facilities, the construction of which could cause significant
environmental effects.
. 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.
. Have insufficient water supplies available to serve the project from existing entitlements and
resources or are new or expanded entitlements needed.
. Result in a determination by the wastewater treatment provider that serves or may serve the
project that it has inadequate capacity to serve the project's projected demand in addition to
the provider's existing commitments.
. Be served by a landfill with insufficient permitted capacity to accommodate the project's
solid waste disposal needs.
. Fail to comply with federal, state, and local statutes and regulations related to solid waste.
Project Impacts
Impact IV.N-l: The proposed project would create or contribute runoff water which would exceed the
capacity of existing or planned stormwater drainage systems or provide substantial additional sources
of polluted runoff.
Surface and stormwater runoff in the project area is collected by the City's storm drainage system and is
discharged to San Francisco Bay east of the project area. The existing storm drainage system in the
project area is designed to accommodate flows from office development and the amount of existing
impervious surfaces in the area. The proposed project would remove existing buildings on the site and
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redevelop the area with similar uses. The project consists of the phased removal and replacement of
existing buildings on the 22.6 acre project site and construction of five to six new office buildings and
two to four parking structures. As a result of increased traffic, increased stormwater pollutants, such as
copper and zinc from break pads23 or oil from leaking engines, may result in a potentially significant
change in storm water quality.
To comply with the Clean Water Act (CW A), STOPPP was formed. STOPPP holds a joint municipal
NPDES permit from the San Francisco Bay RWQCB. The permit includes a comprehensive plan to
reduce the discharge of pollutants to creeks, San Francisco Bay, and the ocean to the maximum extent
possible.
The San Mateo Countywide STOPPP has a Site Design Standards Checklist to evaluate proposed projects
against guidelines intended to reduce stormwater pollution. These guidelines are regulated by the
SSFMC, General Plan, or other best management practices guidelines.
The project site is divided into three separate sub-drainage areas: North (Portion of Building 1000),
Central (Portion of Buildings 800 and 1000) and South (Buildings 700, 750, 850, 900 and a portion of
Building 800). The on-site storm drainage system varies in size from 12-inch to 30-inch in diameter.
The three sub-drainage areas discharge to the City's public storm drainage system as follows: North Sub-
Drainage Area, Central Sub-Drainage Area, and South Sub-Drainage Area. The North sub-drainage area
discharges to the existing 18-inch to 24-inch public storm drainage system on Oyster Point Boulevard.
The Oyster Point Boulevard storm drainage system outfalls to the San Francisco Bay at the Oyster Cove
Marina (north of the Master Plan Area) via a 24 by 30-inch box storm drain line. The Central sub-
drainage area discharges to the existing 18-inch public storm drainage line on Gateway Boulevard. The
existing 18-inch Gateway Boulevard line connects to the Oyster Point Boulevard public storm drainage
system at the intersection of Oyster Point and Gateway Boulevard. The South sub-drainage area
discharges to the existing 30-inch public storm drain line on Gateway Boulevard. The Gateway Boulevard
public storm drainage system collects and conveys storm runoff from the site and outfalls south of the site
to Colma Creek. The outfall is located east of the intersection of Harbor Way and Mitchell Avenue. The
Gateway Boulevard public system varies in size from 30-inch to 72-inch.
Construction impacts to water quality are mitigated through soil stabilization and erosIOn control
techniques as described in Mitigation Measure IV.H-1.1 and IV.H-1.2 in Section IV.H (HydrologylWater
Quality) of this Draft EIR. However, operation of the proposed project could contribute to polluted
stormwater runoff. This would be a potentially significant impact. However, as described below,
mitigation measures, such as the installation of a storm drain interceptor to capture oil and heavy
particulates before entering stormwater drainage systems, would minimize pollutant contributions to
stormwater drainage systems. Therefore, implementation of Mitigation Measures IV.N-l.l through IV.N-
1.4 would reduce operation impacts associated with polluted runoff to a less-than-significant level.
23
Woodward-Clyde Consultants, Contribution of Heavy Metals to Storm Water From Automotive Disc Brake Pad
Wear, Woodward-Clyde Santa Clara Valley Urban Runoff Program, City of Palo Alto Public Works
Department, 2501 Embarcadero Way, Palo Alto, CA 94303,1994.
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Mitigation Measure IV.N-1.1 Operational SWPPP
The project applicant shall develop an operational SWPPP for all drainage to the Central and South Sub-
Drainage areas prior to construction of the Precise Plan and for the North Sub-Drainage area prior to
construction of the subsequent phases of the Master Plan to protect water quality after construction. These
project SWPPPs shall include, but not be limited to, the following measures for project operation:
. Description of potential sources of erosion and sediment at the project site for each phase of the
Master Plan. Industrial activities and significant materials and chemicals that could be used for
each phase of the Master Plan at the proposed project site shall be described. This shall include a
thorough assessment of existing and potential pollutant sources.
. Identification of BMPs to be implemented for the Precise Plan and for each phase of the Master
Plan at the project site based on identified industrial activities and potential pollutant sources.
Emphasis shall be placed on source control BMPs, with treatment controls uses as needed.
. Development of a monitoring and implementation plan for the Precise Plan and for each phase of
the Master Plan. Maintenance requirements and frequency shall be carefully described including
vector control, clearing of clogged or obstructed inlet or outlet structures, vegetation/landscape
maintenance, replacement of media filters, regular sweeping of parking lots and other paced
areas, etc. Wastes removed from BMPs may be hazardous; therefore, maintenance costs shall be
budgeted to include disposal at a proper site. Parking lot areas shall be cleared on a daily basis of
debris that may enter the storm drain system.
. The monitoring and maintenance program shall be conducted at the frequency agreed upon by the
RWQCB and/or City of South San Francisco. Monitoring and maintenance shall be recorded and
submitted annually in coordination with the STOPPP. The SWPPP shall be adjusted, as
necessary, to address any inadequacies of the BMPs.
. The project applicant shall prepare informational literature and guidance on industrial and
commercial BMPs for the Precise Plan and each phase of the Master Plan to minimize pollutant
contributions from the proposed development. This information shall be distributed to all
employees at the project site. At a minimum, the information shall cover: (1) proper disposal of
commercial cleaning chemicals; (2) proper use of landscaping chemicals; (3) clean-up and
appropriate disposal of hazardous materials and chemicals; and (4) prohibition of any washing
and dumping of materials and chemicals into storm drains.
Mitigation Measure IV.N-1.2 Storm Drain Interceptors
The project applicant shall install a storm drain interceptor (also known as an oil/water or oil/grit
separator) on-site to remove oils and heavy particulates from stormwater at appropriate storm drains for
the Precise Plan and each phase of the Master Plan. Appropriate sizing of the unit relative to the
impervious surface drainage area is important and should be taken into consideration when choosing the
interceptor unit model and size.
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Mitigation Measure IV.N-l.3 Impervious Area Drainage Retention Devices
The project applicant shall incorporate alternative drainage solutions around surface parking lots and near
large areas of impervious surfaces such as public plazas to increase pervious surfaces on the site and
increase infiltration. This shall be done for the Precise Plan and each phase of the Master Plan. Such
solutions may include, but are not limited to, vegetated swales, bioretention areas, planter/tree boxes, and
ponds.
Mitigation Measure IV.N-l.4 Rooftop Retention Devices
The project applicant shall incorporate rooftop or downspout retention into all building plans proposed by
the Precise Plan and each phase of the Master Plan to capture all roof runoff.
Impact IV.N-2: The proposed project would require or result in the construction of new water
treatment, distribution, or conveyance facilities or expansion of existing facilities, the construction of
which could cause significant environmental effects.
The project consists of the phased removal and replacement of existing buildings on the 22.6 acre project
site and construction of five to six new buildings and two to four parking structures. The project would be
constructed in five or fewer phases from 2011 to 2020, resulting in a gradual increase the project's
impacts related to the need for new water facilities or the expansion of existing facilities. The proposed
project would involve increasing density at the site by developing the site up to an FAR of 1.25. This
change in FAR translates to an increase in development at the site from approximately 284,000 sf to
approximately 1,230,570 sf., or a net change of 946,570 sf. As a result, the proposed project could have a
potentially significant impact on the water system that delivers the required fire flows.
Water for fire flow would be provided in 12 inch mains that would be constructed with the Precise Plan
and each phase of the project. The water distribution system is owned and operated by CWSc. The water
system consists of a network of 12- and 10-inch lines which should be adequate to serve the required
flows?4 To avoid impacts to the water system's ability to serve peak flow demands, fire flow testing as
well as analysis and certification by fire protection personnel as described in Mitigation Measures IV.N-5
through IV.N-2.l below would reduce the impacts associated with increased fire flow demands to a less-
than significant level.
Mitigation Measure IV.N-2.1 Fire Flow Analysis Report
In order to assure that the water system has the ability to serve peak flow demands including for fire flow,
prior to first building permit for all buildings constructed for the Precise Plan and each phase of the
Master Plan, the project applicant shall consult a NCEES certified Fire Protection Engineer to prepare an
analysis of the proposed project and determine the required design fire flow and fire duration. A certified
report shall be submitted to the South San Francisco Fire Department for review and comment to ensure
that all required design fire flow and fire duration requirements are met.
24
Brady and Associates for the City of South San Francisco, East of 101 Area Plan, July, 1994.
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Mitigation Measure IV.N-2.2 Fire Flow Testing
In order to assure that the water system has the ability to serve peak flow demands including for fire flow,
prior to receiving a building permit for all buildings constructed for the Precise Plan and each phase of the
Master Plan, the project applicant shall perform fire flow tests for all hydrants within 500 feet of the
project site pursuant to American Water Works Association filed testing standards25 to verify if adequate
fire flows defined in Mitigation Measure N-5 are achieved. Any deficiency measured shall be corrected
and retested prior occupancy.
Mitigation Measure IV.N-2.3 Fire Protection Water Supply
In order to assure that the water system has the ability to provide water supply for fire protection, prior to
occupancy of all buildings constructed for the Precise Plan and each phase of the Master Plan, California
Water Service Company shall certify that reservoir storage, beyond their operational and emergency
allotments, required for adequate protection identified in Mitigation Measure IV.N-2.l will be maintained
at all times.
Impact IV.N-3: The proposed project would not 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.
The drainage system in the East of 101 Area is generally designed and constructed for industrial
development and the associated large areas of impervious surfaces. The project would connect to existing
drainage lines that drain directly to San Francisco Bay. All stormwater drainage is regulated by the
RWQCB. The proposed project would redevelop an area of the project area that is already populated by
buildings and impervious surfaces. The project would require new drainage structures and localized on-
site storm drain systems. As construction proceeds through the Precise Plan and each phase of the Master
Plan, impervious area would be incrementally reduced. Ultimately, the amount of stormwater created in
the project area would decrease from existing conditions because the amount of impervious area would be
reduced from approximately 70 percent to approximately 61 percent. Because no additional stormwater
runoff would be created, no additional stormwater would need to be accommodated in existing
stormwater drainage facilities, and no expansion of stormwater drainage facilities would be warranted.
Therefore, the impact would be less than significant and no mitigation measures are required.
Impact IV.N-4: The proposed project would have sufficient water supplies available to serve the project
from existing entitlements and resources and no new or expanded entitlements are needed.
The project consists of the phased removal and replacement of existing buildings on the 22.6 acre project
site and construction of five to six new buildings and two to four parking structures. The project would be
constructed in five or fewer phases from 2011 to 2020, resulting in a gradual increase the project's
demand on water supply.
25 AWWA .1989. AWWA M17-Installation, Field Testing, & Maintenance of Fire Hydrants, American Water
Works Association.
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At completion of construction of all buildings constructed for the Precise Plan and each phase of the
Master Plan, the project would result in a net area increase of 946,570 square feet. It is assumed that use
of the existing 284,000 square feet will be the same in the new development. Therefore, the only change
in water demand will be that due to the net increase in building space over each phase of the project. For
the period from July 2007 through June 2008, the total internal metered water use for the five existing
buildings (700, 1000, 750, 800 and 850) was 3,392,180 gallons (approximately 9,294 gpd) for an area of
234,013 square feet. Therefore, overall average daily water use was 0.04 gpd per square foot. For the
proposed development project, it is assumed that water usage rates for new office space, new R&D
laboratories and landscape irrigation will remain the same (.036 gpd per square foot for office space and
.063 gpd per square foot for biotechnology research and development laboratory space use).
For the July 2007 through June 2008 period, total landscape irrigation water use was 7,219,192 gallons
for an area of 250, 143 square feet. Therefore, average daily irrigation water use was 0.079 gallons/day/ft2.
The existing landscaped area, mainly grass, is 295,100 square feet. The proposed build out landscaped
area will be mainly drought tolerant plantings. The landscaped area is expected to increase by 88,500
square feet to a total area of 383,500 square feet. This is an increase in area of 30 percent. The landscape
architect estimates a reduction in irrigation rate of at least .33 percent due to conversion from grass to
drought tolerant plants. Hence, in the WSA it is assumed that there is no change in total quantity of water
use for irrigation due to proposed project.
The project proposes office uses on the site. The WSA was prepared using the assumptions that
approximately 40 percent of the proposed new building space will be used for offices and the remaining
60 percent of space for biotechnology research and development laboratories. R&D uses typically
consume more water than office uses. Therefore, the estimated increase in water demand due to the
proposed project of 49,411 gpd is more conservative than what would be demanded under full buildout of
the Precise Plan and all subsequent phases of the Master Plan?6
The project would employ a Leadership in Energy and Environmental Design (LEED)-equivalent
standard for the design of the new buildings and would use water consumption. In addition, Cal Water
concluded that for the next 20 years, the SSF District will have adequate water supplies to meet projected
demands associated with the proposed project along with those of all existing customers and all other
anticipated future users for normal, single dry year and multiple dry year conditions. Therefore, the
impact would be less than significant and no mitigation measures are required.
While the proposed project's effect on water supply is not a significant effect under CEQA, there are
measures that the City could encourage the project applicant to implement or impose as conditions of
approval. Measures such as the installation of water-conserving appliances including dishwashers,
washing machines, toilets, and faucets and the use of drought-resistant plants in landscaping would
minimize the project site's water demand. Therefore, Mitigation Measure IV.4.l below would reduce the
proposed project's contribution to the total water demand.
26
This calculation is based on the following equation: 0.036 gallons/day/sq ft x 946,570 sq ft x 0.40 + 0.063
gallons/day/sqft x 946,570 sqft x 0.60 = 13,631 + 35,780 = 49,411 gallons/day.
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Mitigation Measure IV.N-4.1 Water Conservation
In order to reduce water demands of all phases of the proj ect, the proj ect applicant shall include methods
of water conservation in the proposed proj ect' s buildings and landscaping for the Precise Plan and each
phase ofthe Master Plan. These methods shall include, but not be limited, to the following:
. Install water-conserving dishwashers and washing machines, and water-efficient centralized
cooling systems in all new buildings (this method would not apply to process development or
research development laboratory equipment);
. Install water-conserving irrigation systems (e.g., drip irrigation and evaportranspiration-based
irrigation controllers);
. Design landscaping with drought-resistant and other low-water-use plants; and
. Install water-saving devices such as water-efficient toilets, faucets, and showerheads.
Impact IV.N-5: The proposed project would not result in a determination by the wastewater treatment
provider that serves or may serve the project that it has inadequate capacity to serve the project's
projected demand in addition to the provider's existing commitments.
The project consists of a Precise Plan and Master Plan, which would result in the phased removal and
replacement of existing buildings on the 22.6 acre project site and construction of five to six new
buildings and two to four parking structures. The project would be constructed in five phases from 2011
to 2020, resulting in a gradual increase the project's impacts related to wastewater treatment. There are no
uses proposed for the site that would use or produce wastewater containing contaminants that cannot be
treated at the WQCP or that would require on-site treatment.
An addendum to the 2002 East of 101 Sewer System Master Plan27 recalculated demands based on the
planning assumptions that have changed. These changes include land use, development densities and
intensities, and population growth rates assumptions. The wastewater flows were set equal to the water
demands estimated in the WSA included as Appendix I to this Draft EIR. Therefore, the average dry
weather flow from the project site is estimated to increase by 49,411 gpd (0.049 mgd) for a total of 58,705
gpd (0.058 mgd).28 Current average dry weather flows east of Highway 101 are approximately 1.7 mgd.
Several deficiencies identified in the 2002 East of 101 Sewer System Master Plan have been remedied
including: Harbor Trunk, Swift Subtrunk, and Pump Station 3. Additional improvements were identified
in the 2002 Sewer System Master Plan and are included in a capital improvement plan that would allow
for capacity up to 5.5 mgd average dry weather flow. Based on a capacity of 5.5 mgd and a current flow
27
Carollo Engineers for the City of South San Francisco, Addendum to the City of South San Francisco East of
Highway 101 Sewer Master Plan, May 2007.
This calculation is based on the following equation: 49,411 gallons/day + (3,392,180 gallons /365 days) =
58,705 gallons/day.
28
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of 1.7 mgd, the remaining capacity in the east of Highway 101 collection systems is 3.8 mgd. As a result,
the incremental increase of 0.049 mgd to the collection system is less than significant.
As discussed previously, current flows to the WQCP are approximately 9 mgd, while the permitted
capacity of the plant is 13 mgd. As shown in Table IV.N -1, no water quality violations have occurred
within the last two years, and as a result, the projected 0.049 mgd percent increase in dry weather flows
from the proposed project to the WQCP would not exceed the WQCP capacity. Therefore, the impact
would be less than significant and no mitigation measures are required.
Impact IV.N-6: The proposed project would be served by a landfill with sufficient permitted capacity to
accommodate the project's solid waste disposal needs.
The project consists of a Precise Plan and Master Plan, which would result in the phased removal and
replacement of existing buildings on the 22.6 acre project site and construction of five to six new
buildings and two to four parking structures. The project would be constructed in five or fewer phases
from 2011 to 2020, resulting in a gradual increase in the project's impacts related to solid waste
generation.
The Scavenger Company is contracted by the City of South San Francisco as the sole hauler of solid
waste and operator of recycling services for the City. The Scavenger Company transports all solid waste
from the master plan area to the Blue Line Transfer facility. The Blue Line Transfer facility has a
permitted capacity of 2,000 tons per day, but currently receives an average of approximately 800 tons per
day. Once the useable materials have been separated at the Blue Line Transfer facility, the remaining
trash is then transported to the Ox Mountain Sanitary Landfill. The landfill has a permitted maximum
disposal of 3,598 tons per day?9 As of 2000, the landfill has exceeded its permitted capacity of 37.9
million cubic yards by approximately 6.7 million cubic yards (17.8 percent). However, the closure date is
planned for 2018.
Because the proposed project would roughly quadruple in size the development at the site, the project
would result in an approximate quadrupling of solid waste to the Blue Line Transfer facility and Ox
Mountain Sanitary Landfill from the master plan area?O Development under the proposed project would
result in an additional 3,731,379 pounds (1,866 tons) of solid waste per year (approximately 10,223
pounds [5 tons] per day), representing approximately 0.25 percent and 0.14 percent of the permitted
maximum amount accepted daily at the Blue Line Transfer facility and Ox Mountain Sanitary Landfill,
respectively. The remaining capacity of the Blue Line Transfer facility would be able to accommodate the
29
California Integrated Waste Management Board, Active Landfills Profile for Ox Mountain Sanitary Landfill
(41-AA-0002), website:
http://www.ciwmb.ca.gov/Profiles/F acility/Landfill/LFProfile 1. asp ?COID= 7 &F ACID =41-AA -0002, accessed
September 4, 2008.
30 According to the Guidelines for Preparation of Environmental Assessments for Solid Waste Impacts (Ventura
County Solid Waste Management Department, May 1998), a solid waste generation rate of O. 01 08 pounds per
square foot per day is applicable to office, manufacturing, and eating/drinking establishments sectors. Thus, if
this rate is applied to the project, the solid waste generation rate would directly relate to the increase in
development proposed under the project.
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additional solid waste?! Furthermore, the Scavenger Company has stated that a quadrupling of the
development at the project site and subsequent increase in solid waste generation would not impact
Scavenger's current available capacity?2 While the Ox Mountain landfill is currently in excess of its
permitted capacity, BPI continues to accept waste as the landfill gradually settles and new space becomes
available. As discussed previously, BPI is permitted until 2016 to expand the Ox Mountain landfill. Thus,
the increase in solid waste generated under the proposed project would be sufficiently served by the Blue
Line Transfer facility and the Ox Mountain Landfill. Therefore, the impact would be less than significant
and no mitigation measures are required.
Impact IV.N-7: The proposed project would comply with federal, state, and local statutes and
regulations related to solid waste.
Solid waste disposal and recycling in the City of South San Francisco is regulated by the City's SSFMC,
particularly Chapters 8.16 and 8.28. As neither of these chapters establishes quantitative disposal or
recycling rates, the project site, under the Gateway Business Park Master Plan, would not be subject to
diversion requirements. However, under the SSFMC, the project would be required to have its solid
waste, including construction and demolition debris, and recyclable materials collected by the Scavenger
Company. The master plan area currently complies with this provision and would continue to do so under
the implementation of the proposed proj ect. Additional health and sanitation requirements set forth in the
SSFMC would be met by the Scavenger Company.
As described in the Regulatory Framework, AB 939 requires that local jurisdictions divert at least 50
percent of all solid waste by 2000. Prior to 2004, the City of South San Francisco was not been able to
meet the AB 939 requirement.33 However, the CIWMB has repeatedly granted the City time extensions to
achieve the 50 percent diversion goal. Between 2004 and 2006, the City met the AB 939 requirement. The
results for 2007 are not yet available. As analyzed above, the master plan area is not a substantial
contributor to the City's generation of solid waste disposal at the Ox Mountain Sanitary Landfill.
Implementation of the proposed project could quadruple the master plan area's solid waste contribution to
Blue Line Transfer facility and Ox Mountain Sanitary Landfill, but the master plan area's contribution
would remain relatively small. Consequently, because the proposed project would not impede the City's
compliance with AB 939, there would be no impact and no mitigation measures are required.
CUMULATIVE IMPACTS
The geographic context for a discussion of cumulative impacts to utilities is the service area of the utility
in question. For instance, the geographic context for cumulative impacts to water supply is the CWSC and
SFPUC service areas; to wastewater, it is the East of 101 Area; and to the storm drainage system, the
geographic context is the local watershed. The cumulative impacts analysis for each utility includes all
31
Formosa, Paul, Chief Financial Officer, South San Francisco Scavenger Company, phone conversation with
CAJA staff, July 28, 2008.
32 Ibid.
Formosa, Paul, Chief Financial Officer, South San Francisco Scavenger Company, phone conversation with
CAJA staff, September 25, 2008.
33
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cumulative growth within its respective service area, as identified by the providers' demand projections.
Growth and utility demand forecasts for each utility are presented above.
The existing drainage system in the East of 10 1 Area is generally designed and constructed for industrial
development, which has a high ratio of impervious surfaces?4 The project site's storm drainage system
consists of underground pipes and outfalls that empty to drain lines on Oyster Point Boulevard and
Gateway Boulevard. Stormwater point and non-point source discharges are a major source of pollution in
San Francisco Bay from the City, as the City's storm drainage system discharges to the Bay. As
redevelopment in the East of 101 Area continues, industrial and commercial development could degrade
water quality through industrial pollutant discharges or simply as a result of increased traffic.
To combat this problem, the STOPPP has prepared a BMPs plan to control pollutants in their stormwater
system. Compliance with the permit requirements for non-point source stormwater discharge under the
NPDES also requires the property owner of all construction projects over one acre in size to obtain a
stormwater discharge permit. The WQCP operates under STOPPP's Joint Municipal NPDES Permit.
Cumulative impact and redevelopment may result in a significant increase of pollutant load in the runoff.
The proposed project represents 22.6 acres or approximately 2 percent of the 1,177 acres in the East of
101 Area. Therefore, the proposed project would not be cumulatively considerable. However, compliance
with Mitigation Measures IV.N-1.1 through IV.N-1.4 would ensure that the project's contribution to
stormwater pollutants flows would be minimized and would help reduce the amount of potentially
harmful toxins on City streets.
The 2002 East of 10 1 Sewer System Master Plan35 required sewer system upgrades and allocated
construction costs to existing and future users. Projected flow rates were calculated to a 2020 planning
horizon based on redevelopment of 32 parcels to research and development. An addendum to the 2002
East of 101 Sewer System Master Plan36 recalculated demands based on the planning assumptions that
have changed. These changes include land use, development densities and intensities, and population
growth rates assumptions. Current average dry weather flows in the East of 101 Area are approximately
1.7 mgd. The recalculated sewer flow rates assume the wastewater flow rates are equal to the water
demands. The recalculated average dry flows were 2.4 mgd in 2015 and 3.2 mgd in 2030. The previous
flow projections were 12.1 mgd in 2020, 3.8 times greater than the revised flow.
Deficiencies in the collection identified in 2002 East of 101 Sewer System Master Plan still need to be
repaired to provide for future capacity,37 but the lower projected flows may result in a larger connection
charge per unit of capacity. Since planned improvements to the collection will adequately the serve the
cumulative growth, the impact to the collection systems is less than significant.
34
35
Brady and Associates for the City of South San Francisco, East of 101 Area Plan, July, 1994.
Carollo Engineers for the City of South San Francisco, City of South San Francisco East of Highway 101 Sewer
Master Plan, September 2002.
Carollo Engineers for the City of South San Francisco, Addendum to the City of South San Francisco East of
Highway 101 Sewer Master Plan, May 2007.
37 Ibid.
36
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Current flows to the WQCP are approximately 9 mgd, while the permitted capacity ofthe plant is 13 mgd.
No water quality violations have occurred within the last two years. Projected growth for the East 101
Area is 3.2 mgd, an increase of 1.5 mgd. The resulting increase for the East of 101 Area does not exceed
the capacity of the WQCP, as the cumulative impact would be less than significant.
Table IV.N-2
SSF District Supply Versus Demand (AFY)
Normal Total Supply 8,830 9,070 9,370 9,690 10,030
Hydrologic Annual Ave Day Demand 8,830 9,070 9,370 9,690 10,030
Year Difference 0 0 0 0 0
Total Supply 8,830 9,070 9,370 9,690 10,030
One Dry Year Annual Ave Day Demand 8,830 9,070 9,370 9,690 10,030
Difference 0 0 0 0 0
Multiple Dry Total Supply 7,140 7,330 7,570 7,825 8,100
Year Period Annual Ave Day Demand 7,064 7,256 7,496 7,752 8,024
Difference +76 +74 +74 +73 +76
I Assessment or Gatewa Business Park Pro 'ect, December 2, 2008
Table IV.N-2 demonstrates the supply reliability and projected future demands by varying hydrologic
conditions over the 20-year planning horizon through 2028 as required by SB 610. The analysis of supply
and demand shows that Cal Water has sufficient water supplies to meet normal year, single dry year, and
multiple dry year periods
With respect to either the 5-year or 20-year forecasts, the project does not represent a significant
percentage in the projected increase in SSF District demand. For 2013, it leaves 94 percent of the
projected increase in demand for other projects and general growth within the District. For 2028, it leaves
95.5 percent for other projects and general growth. Therefore, the proposed project would not be
cumulatively considerable.
SFPUC and Cal Water are dedicated to implementing conservation and water recycling measures. In
addition, Cal Water is a member of the California Urban Water Conservation Council (CUWCC). The
CUWCC was created to increase efficient water use statewide through partnerships among urban water
agencies, public interest organizations, and private entities. The Council's goal is to integrate urban water
conservation BMPs into the planning and management of California's water resources. Implementation of
water conservation BMPs will help limit water demand from customers within the SSF District's service
area and reduce water supply requirements. However, compliance with Mitigation Measure IV.N-4.1
would ensure that the project's contribution to water supply demand would be minimized.
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LEVEL OF SIGNIFICANCE AFTER MITIGATION
Implementation of Mitigation Measures IV.N -1.1 through IV.N -4.1 identified in this section would
adequately mitigate all potential impacts related to utilities and service systems. These impacts would also
be reduced to a less than significant level.
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