HomeMy WebLinkAboutISND 901 Larch
CITY OF SOUTH SAN FRANCISCO
901 LARCH AVENUE SOUTH SAN FRANCISCO
DRAFT INITIAL STUDYAND NEGATIVE DECLARATION
PREPARED FOR:
CITY OF SOUTH SAN FRANCISCO
DEPARTMENT OF ECONOMIC AND COMMUNITY DEVELOPMENT
PLANNING DIVISION
315 MAPLE AVENUE, SOUTH SAN FRANCISCO , CA 94083
www.ssf.net
PREPARED BY:
KNAPP PLANNING AND ENVIRONMENTAL CONSULTING
Allisonknappconsulting.com
February 5, 2016
CITY OF SOUTH SAN FRANCISCO
901 LARCH AVENUE SOUTH SAN FRANCISCO
DRAFT INITIAL STUDYAND NEGATIVE DECLARATION
Submitted to:
STATE OF CALIFORNIA
GOVERNORS OFFICE OF PLANNING AND RESEARCH
STATE CLEARINGHOUSE
P.O. BOX 3044
SACRAMENTO, CALIFORNIA 95812-3044
Submitted by:
CITY OF SOUTH SAN FRANCISCO
DEPARTMENT OF ECONOMIC AND COMMUNITY DEVELOPMENT
PLANNING DIVISION
Ms. Adena Friedman, Senior Planner
315 MAPLE AVENUE,
SOUTH SAN FRANCISCO, CALIFORNIA 94083
February 5, 2016
TC
ABLE OF ONTENTS
C P
HAPTERAGE
C1: LF 1-1
HAPTEREGISLATIVE RAMEWORK
1.1Initial Study/Legislative Framework 1-1
1.2Project Applicant/Team/Contact1-2
1.3Documents Incorporated by Reference 1-3
1.4City of South San Francisco Project Review Process 1-3
1.5Standard Conditions of Approval Required by Law Addressing Envir1-4
Impacts
1.6Environmental Determination 1-13
C2:PD2-1
HAPTERROJECT ESCRIPTION
2.1Project Location and Setting 2-1
2.2Proposed Project 2-4
2.3Environmental Mitigation Measures Proposed as Part of the Project2-6
2.4General Plan and Zoning 2-16
2.5Required Entitlements 2-16
C3:EC 3-1
HAPTER NVIRONMENTAL HECKLIST
3.1Aesthetics3-2
3.2 Agriculture and Forest Resources 3-9
3.3Air Quality 3-11
3.4Greenhouse Gas Emissions 3-20
3.5Biological Resources 3-26
3.6Cultural Resources 3-40
Geology and Soils
3-7 3-42
3-8 Hazards and Hazardous Materials 3-55
3-9 Hydrology and Water Quality 3-61
3-10 Land Use and Planning 3-67
3-11 Mineral Resources3-69
3-12 Noise 3-70
3-13 Population and Housing 3-80
3-14 Public Services3-82
3-15 Recreation 3-84
3-16Transportation and Traffic3-85
3-17 Utilities and Service Systems 3-88
3-18 Mandatory Findings of Significance and Summary of Findings3-93
LF
IST OF IGURES
Chapter 2 Project Description
Figure 1 Project Area 2-2
Figure 2 Project Site and Vicinity 2-3
Figure 3 Site Plan and Approximate Location of Sound Barrier and 2-4
Chapter 3 Environmental Checklist
Figure 1 Aesthetics Back Wall of Multi-Family 3-3
Figure 2 Single-Family Northwest of Project 3-4
Figure 3 Single-Family Adjacent to project with Project in Foreground 3-4
i
AA
PPENDIX
A-1
AQ
IR UALITY
Construction and Operational Emission Modeling, RCH Group. November 2015.
CalEEmod Output Files, RCH Group. November 2015.
A
PPLICANT
Environmental Mitigation Measures [proposed by Applicant], Vinal Nand. December 2, 2015.
B
IOLOGY
Michael Marangio, Biological Resources Assessment Prepared for Allison Knapp Wolla
Consulting, Proposed Residence, 901 Larch Avenue, South San Fran. November
10, 2015.
G
EOLOGY
Applicants Reports-GeoTrinity
GeoTrinity Consultants, Inc., Geotechnical and Geologic Investigation, Residential Development
901 Larch Avenue, South San Francisco, California. May 1, 2015.
GeoTrinity Consultants, Inc., Supplemental Letter for May 2015 Report and August 6, 2015
Plans. August 18, 2015.
GeoTrinity Consultants, Inc., Response to Peer Review Letter. September 23, 2015.
City Peer Review-Cotton Shires Associates
Cotton Shires Associates, Inc., Geotechnical Peer Review, Nand New Residence, 901 Larch
Avenue. May 26, 2015.
Cotton Shires Associates, Inc., Supplemental Geotechnical Peer Review, Nand New Residence,
901 Larch Avenue. October 2, 2015.
ii
1
I
NTRODUCTION
1.1IS/LF
NITIAL TUDYEGISLATIVE RAMEWORK
This Initial Study has been prepared in accordance with the Cali
Act (CEQA), which can be found in the California Public Resourcesections21000
et seq., and the CEQA Guidelines found in California Code of Reg
sections15000 et seq., as amended(CEQA Guidelines). This Initial Study identifies the
potential environmental impacts associated with demolition, grading, construction,and future
occupancy of the Project which includes any reasonably foreseeable impacts associated with the
Project in its entirety. CEQA (PRC section 21065) defines a Project as:
An activity which may cause either a direct physical change in the environment, or a
reasonably foreseeable indirect physical change in the environme
the following:
a)An activity directly undertaken by a public agency.
b)An activity undertaken by a person which is supported, in whole ,
through contracts, grants, subsidies, loans, or other forms of a
or more public agencies.
c)An activity that involves the issuance to a person of a lease, p
certificate, or other entitlement for use by one or more agencie
The Applicant is seeking design review entitlement as well as grading and building permits in
order to construct a single-family detached residence at 901 Larch Avenue in South San
Francisco, California.Other required permits may include an encroachmentpermit to conduct
work in the public right-of-way to construct curb and gutter, and potential street repairs as may
be required on Larch Avenue.
The proposed project (Project) meets criteria c, identified above, and therefore is
considered a project under CEQA. Because the Project requires discretionary design review
entitlements, environmental review is required by CEQA. Unless exempted, preparation of an
environmental analysis and subsequent environmental determinatioquired prior to or
simultaneously with entitlement review. Environmental review do
approval, but is an independent analysis of potential Project im
The Lead Agency may, after review of the entirety of the record, find that the environmental
analysis is adequate and approve, disapprove, or conditionally approve the Project based upon
environmental and merits review.
The Lead Agency for this document is the City of South San Franc
Commission will hold a study session to take public comments and will make the final
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determination on the environmental documentand on the discretionary entitlements. These
actions will take place in legally-noticed public hearings.
Typically,the construction of one single-family residence in a residential zone with utilities and
infrastructure in place is categorically exempt from the CEQA re CEQA Guidelines
section 15303, Class 3 New Construction or Conversion of Small St However,there
are exceptions to exemptions as stated in CEQAGuidelines section 15300.2,subsection (a).
Subsection (a) clearly states Class 3 exemptions are qualified b
would be located. The subsection further notes a project that initself is ordinarily insignificant
in its impact on the environment may in a particularly sensitive
Therefore, if a project might be located in a biological habitat, or on steep or potentially unstable
slopes, or on properties known to have environmental contamination (hazardous , the
exception to the exemption noted above requires the lead agency to conduct an initial study,
which may be satisfied by utilizing the sample forms provided in Appendices G and H of the
CEQA Guidelines.
The Project site contains several geological constraints, including a very steep slope, shallow
slope instability on-site (i.e., two-foot deep and six-foot wide earthflow scars) and another off-
site, and an upslope fill prism. The site is also adjacent to Sign Hill, a known biological resource
within the City of South San Francisco. Therefore, the City of South San Francisco has prepared
an initial study for the Project, based upon the known geotechnical constraints, along with
unknown and potential biological issues.
Therefore, this Initial Study is prepared for City Project Number P15-0037, located at 901 Larch
Avenue in South San Francisco, California (APN: 012-015-020). The Project would include the
construction of a 2,500 square foot single-family residence (inclusive of a two-car garage) on a
7,500 square foot lot. The lot contains a 44.7% slope (Architectural Plans, Sections and Details,
Sheets A1-A6, GeoTrinity Consultants, April 21, 2015).
1.2 PAT/LAT
ROJECT PPLICANT EAMEAD GENCY EAM
PAAT
ROJECT PPLICANT ND EAM
The property owner and applicant (Applicant)is Mr. Vinal Nand.
Mr. Vinal Nand
585 Villa Street, #10
Daly City, CA 94014
(650) 455-6374
The consulting team for the Applicant is GeoTrinityConsultants, Inc. Mr. Jerry Yang is the
representative for GeoTrinity.
Mr. Jerry Yang, P.E. G.E.
7770 Pardee Lane, Suite 101
Oakland, CA 94621
(510) 383-9950
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LAECT
EAD GENCY AND NVIRONMENTAL ONSULTANT EAM
The Lead Agency for this Initial Study is the City of South San Francisco (City). The
administrative record for the Project is on file at the Citys P
person has been assigned as the custodian and Case Planner/Proje
Agency:
Ms. Adena Friedman, Senior Planner
Department of Economic and Community Development-Planning Division
315 Maple Avenue
South San Francisco, CA 94080
(650) 877-8535
The Lead Agencys Environmental Consultant is Knapp Planning and Environmental
Consulting,represented by Ms. Allison Knapp.
Allison Knapp Wollam, Environmental Consultant
511 Linden Street, Suite B
San Francisco, CA 94102
(415) 902-3238
Allison Knapp will serve as Project Manager, preparer of the initial study, andrepresent the
CEQA document in all hearings and meetings. The air quality, greenhouse gas, hazard risk, and
noise assessments will be prepared by Mr. Paul Miller and Mr. Mike Ratte of the RCH Group.
Mr. Michael Marangio of Marangio Biological Consulting will conduct the biological resource
assessment and Mr. Aaron Stessman of CSS Environmental Consultants will serve as th
hazards and hazardous materials consultant.
1.3 DIBR
OCUMENTS NCORPORATED Y EFERENCE AND
IAA
NCLUDED IN PPENDIX
AQ
IR UALITY
Construction and Operational Emission Modeling, RCH Group. November 2015.
CalEEmod Output Files, RCH Group. November 2015.
APM
PPLICANTS ROPOSED ITIGATION MEASURES
Environmental Mitigation Measures [proposed by Applicant], Vinal Nand. December 2, 2015.
B
IOLOGY
Michael Marangio, Biological Resources Assessment Prepared for Allison Knapp Wollam, Consulting,
Proposed Residence, 901 Larch Avenue, South San Francisco, Calif. November 10, 2015.
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G
EOLOGY
Applicants Reports GeoTrinity
GeoTrinity Consultants, Inc., Geotechnical and Geologic Investigation, Residential Development 901 Larch
Avenue, South San Francisco, California. May 1, 2015.
GeoTrinity Consultants, Inc., Supplemental Letter for May 2015 Report and August 6, 2015 Plans
August 18, 2015.
GeoTrinity Consultants, Inc., Response to Peer Review Letter. September 23, 2015.
City Peer Review Cotton Shires Associates
Cotton Shires Associates, Inc., Geotechnical Peer Review, Nand New Residence, 901 Larch Avenu. May
26, 2015.
Cotton Shires Associates, Inc., Supplemental Geotechnical Peer Review, Nand New Residence, 901 Larch
Avenue. October 2, 2015.
1.4CSSFPR
ITY OF OUTH AN RANCISCO ROJECT EVIEW
P
ROCESS
As a matter of law, the Project is required to comply with feder, and local laws and
regulations. These regulations are verified as satisfied and incorporated into the
matter of demolition, grading,and/or building permit issuance,or the permits will not be issued
by the City of South San Francisco. As such, these requirementspart of the
Project, not a separate and distinct requirement levied through CEQA review.
The Citys project processing requires that applications for projects are f
Citys Technical Advisory Group (TAG). TAG is comprised of repr
Building, Police, Fire, Engineering, Parks and Recreation, and Wtrol. TAG
review identifies changes and additions to a project that are required for the project to comply
with local, state,and federal laws that are implemented through the Citys Municip
Citys Planning Division, subsequent to TAG review, issues a letter to the applicant identifying
the changes in project plans and supporting materials necessary to comply with p
pursuant to site development, construction,and land use. The applicant is requestedto revise
the plans and supporting documentation or the application may not be certified as complete.
Revised plans and documentation are submitted to the Planning Direcirculated to all
affected City departments and divisions in order to evaluate the application in light of earlier
comments and requirements. The process results in an application that can be certified
complete as well as identification of the recommended Conditions of Approval (COAs) that
would be required should the Project be approved by the Planning Commission. Many of these
COAs implement environmental mitigation measures that were historically identified through
the environmental review process and now have become a part of the Citys legislative
requirements, through its general, specific and/or area plans, municipal code, special district
regulations, or memoranda of understanding (i.e., its police power).
After a project application is complete it is subject to environ, and discretionary
review through and by the Citys Planning Commission and/or City Council, depending upon
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the type of project, as defined by the Citys Municipal Codeand state law. The COAs identified
through staff review of the project, and any additional ones ide
process become required of the project as a matter of law pursuant to the South San Francisco
Municipal Code. Prior to the City issuing a building, grading,and/or demolition permit,all City
departments and divisions (identified above) review the project
identified COAs and any additional conditions added pursuant to the public review process.
Permits are not issued by the Citys Building Division in the absence of authorization from City
staff or in the absence of the identified requirements being incorporated into the Project plans.
1.5 SPCR
TANDARD ROJECT ONDITIONS EQUIRED BY
ELAE
XISTING AWTHAT DDRESSESNVIRONMENTAL
I
SSUES
The following project requirements are designed and implemented as part of the Project
Description to reduce environmental impacts and are required through the City of South
San Franciscos standard review and permitting procedures. There, these measures
are not separately identified as mitigation measures in this Initial Study. Failure of the
Applicant to meet the required measures and/or elements of their Project Description
relating to environmental issues could result in environmental impacts and require
subsequent or supplemental CEQA review. In summary, the Project as proposed
coupled with the Project requirements is the baseline from which environmental impacts
are evaluated for the Project as described in Chapter 2 (Project Description).
1. A
ESTHETICS
ALG:Project signage is required to be reviewed by staff, and, in
ESTHETICS IGHT AND LARE
some instances, the Citys Design Review Board and the Planning Commission. Lighting, size
color, placement, design, and compatibility with surrounding land uses is addressed and assured
through this process. The Citys sign regulations as set forth in Chapter 20.360 of the South San
Francisco Municipal Code are intended to preserve and improve appearance, protect from
visual clutter and blight, protect property values and enhance community appearance, minimize
diversion of vehicle operators attention, and safeguard life, health, property, and public welfare.
Potential environmental impacts and the need,or lack thereof,for environmental clearance is
also addressed and undertaken as a part of the Sign Permit procedure. The Planning Division
implements and monitors this requirement.
Projects are reviewed by the Citys Design Review Board consisti
and landscape architects. The Planning Commission, and in some cases the City Council, adds
design elements to projects. Projects that are within a state o
addressed through the CEQA process.
2. AQGGE
IR UALITY AND REENHOUSE AS MISSIONS
AQDC:All construction projects are required to comply with the Bay
IR UALITY UST ONTROL
Area Air Quality Management Districts (BAAQMD) dust control mea
are imposed by the Citys Engineering Division on all projects as a condition of building permit
issuance and are monitored for compliance by staff and/or City consultants. The measures
include all the Basic Fugitive Dust Emissions Reduction Measures, Basic Exhaust Emissions Reduction
Measures,and some of the Additional Fugitive Dust Emissions Reduction Measures identified by the
BAAQMD as of May 2011. The City requires projects to:
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a)Water all active construction sites at least twice daily.
b)Cover all trucks hauling soil, sand, and other loose materials,or require all trucks to
maintain at least two feet of freeboard.
c)Pave, apply water three times daily, or apply (non-toxic) soil stabilizers on all unpaved
access roads, parking areas, and staging areas at construction s
d)Sweep daily (with water sweepers) all paved access roads, parking areas and staging areas
at construction sites.
e)Sweep streets (with wet power vacuum sweepers),if visible soil material is carried onto
adjacent public streets,at least once per day. The use of dry power sweeping is
prohibited.
f)Hydroseed or apply (non-toxic) soil stabilizers to inactive construction areas (previous
graded areas inactive for ten days or more).
g)Enclose, cover, water twice daily, or apply non-toxic soil binders to exposed stockpiled
materials.
h)Install sandbags or other erosion-control measures to prevent silt runoff to public
roadways.
i)Replant vegetation in disturbed areas as quickly as possible.
j)Watering should be used to control dust generation during the br-up of pavement.
k)Cover all trucks hauling demolition debris from the site.
l)Use dust-proof chutes to load debris into trucks whenever feasible.
m)Water or cover stockpiles of debris, soil, sand, or other materials that can be blown by
the wind.
n)All construction equipment shall be maintained and properly tuned in accordance with
manufacturers specifications. All equipment shall be checked b
and determined to be in proper running order prior to operation.
o)Diesel powered equipment shall not be left inactive and idling fre than five
minutes, and shall comply with applicable BAAQMD rules.
p)Use alternative fueled construction equipment, if possible.
q)All vehicle speeds on unpaved roads shall be limited to 15 miles per hour and slower,
should wind and dust conditions necessitate.
r)All roadways, driveways, and sidewalks to be paved shall be comp
possible. Building pads shall be laid as soon as possible after, unless seeding or
soil binders are used.
s)Idling times shall be minimized either by shutting equipment off when not in use or
reducing the maximum idling time to five (5) minutes (as require
airborne toxic control measure detailed in Title 13, Section 2485 of the California Code
of Regulations). Clear signage regarding this requirement shall be provided for
construction workers at all access points.
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t)Post a visible sign with the telephone number and person to cont
regarding dust complaints. This person shall respond and take c
twenty-four (24) hours. The applicable Air District phone number shall also be visible to
ensure compliance with applicable regulations.
AQTAC: The potential for toxic air contaminants
IR UALITY OXIC IR ONTAMINANTS
(asbestos and lead-based paint) to be released into the environment is regulated an
through the Citys Building Division in compliance with federal, local and BAAQMD regulations
in particular BAAQMD Regulation 11, Rule 2 pertaining to asbestos. The BAAQMD regulates
the demolition and renovation of buildings and structures that m
manufacture of materials known to contain asbestos. The BAAQMD shall be notified at least
10 business days before: (1) Any renovation involving the removal of 100 square feet or more,
100 linear feet or more, or 35 cubic feet or more of asbestos; and (2) Every d
1
regardless of asbestos content.
1
The Code of Federal Regulations (CFR), 40 CFR 61, Subpart M, National Emissions Standards for Hazardo
Pollutants (NESHAP) and Federal Occupational Safety and Health A-
containing material (ACM) as any material or product that contai greater than 1% asbestos. Nonfriable ACM is
classified by NESHAP as either Category I or Category II materia: Category I asbestos-
containing packings, gaskets, resilient floor coverings, and aspCategory II all remaining
types of nonfriable asbestos-containing material not included in Category I that when dry, ca
pulverized, or reduced to powder by hand pressure. Regulated asb-containing material (RACM), a hazardous
waste when friable, is classified as any material that contains greater than 1 % asbestos by dry weight and is: Friable:
or Category I material that has become friable; or Category I ma subjected to sanding grinding,
cutting or abrading; or Category II nonfriable material that has a high probability
Activities that disturb material containing any amount of asbestos are subject to certain requirements of the
Cal/OSHA asbestos standard contained in Title 8, CCR Section 152 Typically, removal of disturbance of more
than 100 square feet of material containing more than 0.1% asbestos m
abatement contractor, but associated waste labeling is not requi
When the asbestos content of a material exceeds 1%, virtually all requirements of the standard bec
Materials containing more than 1% asbestos are also subject to N
RACM (friable ACM and nonfriable ACM that will become friable duing demolition operations) must be removed
from buildings prior to demolition. Certain nonfriable ACM and materials containing 1% or less asbes
remain in buildings during demolition: however, there are waste rk
requirements that may make it cost ineffective to do so. Contractors are responsible for segregating and
characterizing waste streams prior to disposal.
With respect to potential worker exposure, notification, and regfines asbestos-
containing construction material (ACCM) as construction material
CCR 341.6).
For a solid waste containing lead, the waste is classified as Ca
equals or exceeds the respective Total Threshold Limit Concentrat
(Mg/kg); or 2) the soluble lead content equals or exceeds the re
(STLC) of 5 milligrams per liter (mg/l) based on the standard Waste Extraction Test (WET). A waste has the
potential for exceeding the lead STLC when the wastes total lea
respective STLC value since the WET uses a 1:10 dilution ratio. Hence, when total lead is detected at a
concentration greater than or equal to 50 mg/kg, and assuming th
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The BAAQMD allows a shorter notification period for certain structures. Th BAAQMD may
be notified 72 hours in advance of demolition with the payment o
applications to demolish residential buildings of four or fewer BAAQMD
issues a J Number or J Permit to the applicant and in turn tcant presents J
Number/Permit to the Citys Building Division as a condition of
demolition permit (Jim Kirkman, (then) Chief Building Official, meeting with Allison Knapp,
October, 16, 2008 and Phil Perry, Senior Building Inspector, telephone conversation January 21,
2016). The purpose of the permitting process is to assure that
compliance with procedures that assure asbestos is not released
The J-Number/Permit is required to be posted on the job site. Through this process, the
BAAQMD and the Citys Building Division ensure that asbestos is handled, removed,
encapsulated, and disposed of in accordance with prevailing law requisite to p
environment, the people conducting the work and nearby sensitive receptors.
Lead contamination is regulated through a myriad of laws on the
Lead is a pollutant regulated by many laws administered by the E
Agency (EPA), including the Toxic Substances Control Act (TSCA), Residential Lead-Based
Paint Hazard Reduction Act of 1992 (Title X), Clean Air Act (CAA), Clean Water Act (CWA),
Safe Drinking Water Act (SDWA), Resource Conservation and Recovery Act (RCRA), and
Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) among
others.
Lead is also regulated by many California laws including the tra
programs and certification of individuals that conduct lead-related construction activities
(California Health & Safety Code 105250). The California Labor Code 6716 to 6717 establishe
standards that protect the health and safety of employees who engage in le-related
construction work, including construction, demolition, renovatio.
lead analysis is required.Lead-containing waste is classified as resource, Conservation, and Ry Act (RCRA)
hazardous, or Federal hazardous, when the soluble lead content e
mg/l based on the Toxicity Characteristic Leaching Procedure (TC
The above regulatory criteria are based on chemical concentrations. Wastes may also be classified as hazardous
based on other criteria such as ignitability; however, for the p
concentrations) is the primary factor considered for waste classgenerated during the
construction activities would not likely warrant testing for ign Waste that is classified as
either California hazardous or RCRA hazardous requires managemen
Potential hazards exist to workers who remove or cut through LCP coatings during demoliti Dust containing
hazardous concentration of lead may be generated during scraping-containing
paint. Torching of these materials my produce lead oxide fumes. Therefore, air monitoring and/or respiratory
protection may be required during the demolition of materials co Guidelines regarding regulatory
provisions for construction work where workers may be exposed to Title 8, CCR, Section
1532.1.
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California Health & Safety Code 17961, 17980, 124130, 17920.10deems a building to be in
violation of the State Housing Law if it contains lead hazards, and requires loca
agencies to enforce provisions related to lead hazards and criminalizes specified acts related to
lead hazard evaluation, abatement, and lead-related constructions unless certified or accredited
by the California Departmentof Public Health Childhood Lead Poisoning Prevention Branch.
The law permits local enforcement agencies to order the abatement of lead
cease and desist order in response to lead hazards. Chapter 3, Air Quality describes many of the
laws implemented through the air district.
The removal of buildings suspected of lead based paints (typical
constructed prior to 1978 when laws were promulgated to remove lother
volatile organic compounds) requires surveys and removal of lead-based paints by licensed
contractors certified in the handling methods requisite to prote
health and safety. The City Building Division requests information and certification from
persons applying for demolition, scaffolding and building permits (Jim Kirkman, previous
Building Official, October 16, 2008).
AQVE: The potential for air quality degradation from vehicle
IR UALITY EHICLE MISSIONS
emissions is regulated to some extent by the Citys Transportation Demand Management (TDM)
program, contained in Chapter 20.400 of the South San Francisco Municipal Code. Table
20.400.003 in the South San Francisco Municipal Code establishes specific program
requirements for a project generating one hundred or more vehicltrips per day or a project
seeking a floor area ratio (FAR) bonus. The required alternative (mode shift) use for all
projects is twenty-eight percent below standard trip rates modeled for the project without TDM
measures in place. Projects with an increased FAR are required to increase their alt
use accordingly. The Planning Division implements and monitors this requirement..
AQHE: The BAAQMD adopted Regulation 6, Rule 3: Wood-
IR UALITY EARTH MISSIONS
Burning Devices, to reduce the harmful emissions that come from wood smoke. The R
requires cleaner-burning (e.g., natural gas or propane) U.S. EPA-certified stoves and inserts in
new housing construction.
SSFCAP: The City adopted a Climate Action Plan
OUTH AN RANCISCO LIMATE CTION LAN
(CAP) on February 12, 2014. The CAP identifies strategies and actions to reduce gre
gas (GHG) emissions by 15 percent below baseline (2005) levels by 2020. The City has and
continues to implement GHG reduction measures. Some examples include the installation of
solar facilities at City buildings; requiring bioswales in private development; adopting and
enforcing a construction and demolition waste recycling ordinance; adopting and implementing
a TDM program, and providing electrical car charging stations at City facilities. The City actively
participates in the San Francisco International Airport noise in
reduces heat loss and hence GHG emissions in older buildings. The City also spearheads
educational programs to reduce GHG emissions.Through conditions of approval, development
projects are required to implement a variety of GHG reduction me
include use of renewable and alternate energy including solar an
facilities, water conservation, and waste reduction.
3. GS
EOLOGY AND OILS
CBSCT24: All construction projects are required
ALIFORNIA UILDING TANDARDS ODE ITLE
to comply with the California Building Code (CBC), as periodically amended. Design
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specifications are identified and required for projects located on sites subject to liquefaction,
differential settlement, and severe groundshaking. These requirementsare enforced and
monitored by the Citys Engineering Division. Compliance with the CBC is also implemented
and monitored by the CitysBuilding Division.
GSGR:The City Engineering Division also requires
EOLOGY AND OILS EOTECHNICAL EPORTS
geotechnical reports as a part of the permit package for project
land, for demolition and rebuilding and for additions to buildings that require grading and
additional loading (Sam Bautista, City Engineer, meeting July 22, 2009; conditions of project
approval, see Chapter 3, Geology and Soils; and SSFMC20.170.002). The geotechnical reports
are required to be prepared by a licensed geologist, geotechnical engineer or engineering
geologist. The geotechnical reports address design and construction specifications for the
project including grading, site drainage, utility and infrastruct, and
placement and building design. The geotechnical reports are peer reviewed by the Citys
geotechnical consultant, and are modified as recommended by the Citys consultant.
Geotechnical approval by the Citys geotechnical consultant and the City is required prior to
issuance of a building permit. The geotechnical professional of
project drawings. The Citys geotechnical consultant provides construction inspecti
oversight and monitoring for the City. The Engineering Divisionnts and monitors this
requirement.
4. HM
AZARDOUS ATERIALS
Properties suspected of containing hazardous materials, due to t,are
required by local, state, and federal law to undergo site characterization and if necessar
remediation. Permits from the South San Francisco Fire Department, San Mateo County
Environmental Health Division (SMCEHD), and/or BAAQMD are required. The following
table identifies thestandard, industry-accepted protocol for site characterization and
remediation.
Media Hazardous Materials Approach
Reuse on Site (if concentration is less than 100 ppm).
Soil Remediation (ex-situ) Fuels
Haul and Dispose at appropriate landfill.
Capping and vapor barrier.
Treat on site (see below).
Consult the SMCEHD for requirements.
Soil Remediation (ex-situ) Volatile Organic
Haul and Dispose.
Compounds
Aeration requires a notification to BAAQMD, daily
(VOCs) (gasoline
volumes are limited.
fuels, solvents)
Vapor Stripping apply vacuum system to covered
piles, notify BAAQMD.
Bioremediation - apply bio-treatment materials,
moisture and work soil piles.
Thermal Desorption various vendors provide mobile
treatment units.
Capping and vapor barrier.
Consult BAAQMD and SMCEHD for requirements.
Soil Remediation Inorganics
Haul and Dispose.
(ex-situ) (metals)
Chemical Stabilization.
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Media Hazardous Materials Approach
Sorting reduce waste volume by screening to target
contaminant particle size.
Consult SMCEHD for requirements.
Soil Remediation VOCs
Soil Vapor Extraction apply vacuum to vapor wells,
(in-situ)
notify BAAQMD.
In-situ chemical oxidation.
In-Situ Vitrification use electricity to melt waste and
surrounding soils.
Consult SMCEHD for requirements.
Soil Remediation Semivolatile Organic
Bioremediation saturate soils with bio-treatment
Compounds
(in-situ)
materials.
(SVOCs)
Chemical Stabilization saturate soils with chemicals to
immobilize contaminants.
In-Situ Vitrification.
Capping.
If contaminants are detected in the 20-foot below
Groundwater -InvestigationAll
ground surface soil sample an additional boring should
be completed to groundwater.
Analyze sample for contaminants detected in soil.
Report results to the SMCEHD and consult on
remedial alternatives.
Consult BAAQMD and SMCEHD for requirements.
Groundwater Remediation VOCs
Pump and Treat pump from wells, treat and discharge
treated water.
Air Sparging inject air to volatilize contaminants and
create aerobic groundwater conditions suitable for
natural bioremediation. Generally applied in
conjunction with Soil Vapor Extraction to control
released volatiles.
Bioremediation inject bio-treatment materials into
affected groundwater.
Chemical Oxidation inject oxidation chemicals into
affected groundwater.
Consult BAAQMD for requirements.
Groundwater Remediation SVOCs
Pump and Treat.
Bioremediation.
Chemical Oxidation.
Consult BAAQMD for requirements.
Groundwater Remediation Inorganics
Pump and Treat.
Chemical Immobilization inject chemicals to
precipitate or chemically fix contaminants to soil
particles.
5. HWQ
YDROLOGY AND ATER UALITY
HWQ:The following is a summary of applicable requirements
YDROLOGY AND ATER UALITY
in Provisions C.3.b.ii and C.3.c.i.2 of the San Francisco Bay Region Municipal Regional
Stormwater National Pollutant Discharge Elimination System Permi
Permit or MRP).
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All projects that are required to treat stormwater will need to t-specified amount
of stormwater runoff with low impact development methods. These methods include rainwater
harvesting and reuse, infiltration, evapotranspiration, or biotr (filtering stormwater
through vegetation and soils before discharging to the storm dra. However,
biotreatment will be allowed only where harvesting and reuse, infiltration,and
evapotranspiration are infeasible at a project site. Vault-based treatment will not be allowed as a
stand-alone treatment measure. Where stormwater harvesting and reuse, infiltration, or
evapotranspiration are infeasible, vault-based treatment measures may be used in series with
biotreatment, for example, to remove trash or other large solids
MRP).
Projects that create and/or replace 5,000 square feet or more of i
auto service facilities, retail gasoline outlets, restaurants, and/or surface parking are required to
provide low impact development treatment of stormwater runoff. This requirement appliesto
uncovered parking that is stand-alone, or included as part of any other development project, and
it applies to the top uncovered portion of a parking structure,
uncovered portion is connected to the sanitary sewer (see Provision C.3.b.ii.1 of the MRP). For
all other land use categories, 10,000 square feet is the regional threshold for requiring low impact
development, source control, site design, and stormwater treatme
have the authority to require treatment to the maximum extent pra
The new requirements are built into the following (see below) standard requirements.
HWQSRP
YDROLOGY AND ATER UALITY TORMWATER UNOFF REVENTION
(O): All Projects are required to comply with the San Mateo Countywide
PERATIONAL
Water Pollution Prevention Program (STOPPP), an organization of
Association of Governments (C/CAG) of San Mateo County holding a
Discharge Elimination System (NPDES) Storm Water Discharge permit. The City requires t
implementation of Best Management Practices (BMPs) for new devel
as part of its storm water management program, as levied through
requirements are implemented and monitored by the Engineering and Water Qu
Divisions.
The measures address pollution control and management mechanisms
e.g. structure construction, material delivery and storage, soliagement, employee and
subcontractor training. Stormwater pollution prevention measure
and operations in order to prevent pollution due to Project occu
quality protection measures include:
a)Walking and light traffic areas shall use permeable pavements where feasi
pervious pavements include pervious concrete, porous asphalt, tu
natural stone pavers, concrete unit pavers, crushed aggregate (g
mulch.
b)Parking lots shall include hybrid surfaces (pervious material fo
medians with biofilters (grassy swales), and landscaped infiltra
feasible.
c)Landscape design shall incorporate biofilters, infiltration, and retention/detention basins
into the site plan as feasible.
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d)Outdoor work areas including garbage, recycling, maintenance, st
applicable storm water controls include siting or set back from
ways, provision of roofing and curbs or berms to prevent run on and run off. If the a
has the potential to generate contaminated run off, structural t
contaminant removal (such as debris screens or filters) shall be
design.
e)Roof leaders and site drainage shall be filtered and directed to the Ci
system and harvesting of rainwater shall occur.
f)Drainage from paved surfaces shall be filtered through vegetated
strips before discharge to the Citys storm drain system.
HWQSRP
YDROLOGY AND ATER UALITY TORMWATER UNOFF REVENTION
(C): The City of South San Francisco requires, through COAs, project
ONSTRUCTION
compliance with the State Water Quality Control Boards general
require the applicant to secure a Construction Activities Storm Water Ge
a Notice of Intent (NOI) and prepare and obtain approval of a St
Prevention Plan (SWPPP). The state issues a Waste Discharge Idethin 10
days of receipt of a complete NOI and SWPPP. The applicant is t
of the NOI and SWPPP to the City of South San Franciscos Techni
within the Water Quality Control Plant of the Public Works Deparent prior to issuance of
building and/or grading permits. The requirements are implementthe
Citys Water Quality Control personnel. Typical construction stormwate
include:
a)Identify all storm drains, drainage swales, and creeks located near construction sites and
prevent pollutants from entering them by the use of filter fabri
wattles, slope hydroseeding, cleaning up leaks, drips or spills
cleanup methods to clean up spills, use of berms, temporary ditches, and check dams to
reduce the velocity of surface flow.
b)Place rock bags at all drain inlets to filter silt and along cur
before the drain inlets.
c)Place straw wattles and hydroseed the sloped areas.
d)Place straw matting at the temporary sloped areas for erosion co
e)Place drain systems to filter and then drain into drain inlets.
f)Use silt fencing with straw mats and hand broadcast seed for ero
g)Construct temporary drainage systems to filter and divert water
h)Construct temporary rock and asphalt driveways and wheel washers
streets from dirt and mud.
i)Use part- and full-time street sweepers that operate along public streets and roads.
j)Cover all stockpiled soils to protect from erosion. Use berms ar
k)Cover and protect from erosion plaster, concrete and other powde
amounts of suspended solids.
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l)Store all hazardous materials (paints, solvents, chemicals) in accordance with secondary
containment regulations and cover during wet weather.
m)Use terracing to prevent erosion.
n)Through grading plan review and approval, phase grading operatio
areas during wet weather, limit vegetation removal, delineate clearing limits, setbacks,
easements, sensitive or critical areas, trees, drainage courses
unnecessary disturbance and exposure. Limit or prohibit grading
thth
season, October 15to April 15.
o)Prevent spills and leaks by maintaining equipment, designating s
such activities that are controlled and away from water courses,and perform major
maintenance off-site or in designated areas only.
p)Cover and maintain all dumpsters, collect and properly dispose of all pain
wastes, clean up paints, solvents, adhesives, and all cleaning solvents properly. Recycle
and salvage appropriate wastes and maintain an adequate debris d
q)Avoid roadwork and pavement stormwater pollution by following manufacture
instructions.
6. N
OISE
IAN: The City of South San Francisco regulates noise exposure
NTERIOR MBIENT OISE
through state law and its General Plan and East of 101 Area Plan, for projects located in the
East of 101 area. A chapter of the CBC, collectively known as Title 24, contains acoustical
requirements for interior sound levels in habitable rooms for mu-family residential land uses.
Title 24 contains requirements for construction of new hotels, motels, apartment houses, and
dwellings other than detached single-family dwellings intended to limit the extent of noise
transmitted into habitable spaces. The standard specifies the e
floor-ceiling assemblies must block or absorb sound between units and the amount of
attenuation needed to limit noise from exterior sources. The st
noise level of 45 dBA (CNEL or L) in any habitable room with all doors and windows closed.
dn
The code requires an acoustical analysis demonstrating how dwelling units
to meet this interior standard where such units are proposed in
greater than 60 dBA (CNEL or L). Title 24 requirements are enforced as a condition of
dn
building permit issuance by the Citys Building Division.
The City, through its General Plan, adopted the Noise Guidelines of the State Department of
Health Services in its Noise Element (1999). Table 9.2-1, Land Use Criteria for Noise Impacted
Areas, (General Plan, page 280) guides land use decisions based upon noise thresholds
correlating to land use classifications, acoustical analyses, and mitigations.
The City implements the Federal Aviation Administration adopted noise contours, participates
in an aircraft noise insulation program and City/County Association of Governments (C/CAG)
airport noise planning efforts. Figure 9-1 of the General Plan Aircraft Noise and Noise Insulation
Program(General Plan, page 279) identifies the noise contours and program areafor these
planning efforts.
C/CAG updated the San Francisco International Airport noise impa
2012. The new boundaries for South San Francisco are on page 11 Comprehensive Airport
Land Use Compatibility Plan for the Environs of San Francisco In
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Association of Governments of San Mateo County, Redwood City, Ca(Ricondo Associates, Jacobs
Consultancy, Clarion Associates. October 2012) (ALUP). Therefore the maps contained in
the South San Francisco General Plan must be used in conjunctionALUP.
The Eastof 101 Area Plan requirement for interior ambient noise for comm
retail is 45 dBA, L, echoing state law. Residential land uses in the East of 101 are prohibited.
eq
The Noise Guidelines are implemented by the Planning Division th
NEAN: The City of South San Francisco regulates exterior noise
OISE XTERIOR MBIENT OISE
levels through the South San Francisco Municipal Code (Chapter 8.32). The Municipal Code
identifies maximum noise exposure corresponding with land use and time of day. Low density
residential maximum noise exposure (excluding vehicle horns and emergency vehicl
restricted to 50 dB from 10 P.M. to 7 A.M. and 60 db from 7 A.M. to 10 P.M. Higher density
residential and commercial land use noise exposure is restricted to 55 dB from 10 P.M. to 7
A.M. and 65 db from 7 A.M. to 10 P.M. Industrial land uses are restricted to 70 dB anytime of
the day. These noise standards are implemented largely through etions (i.e., citizen
complaint and governmental response). The Citys Fire Departments Code Enforcement
Officer implements these regulations. The following text and table are excerpted from Section
8.32.030.
(a) It is unlawful for any person to operate or cause to be operated
source of sound at any location within the city or allow the creation of any
noise on property owned, leased, occupied or otherwise controlle
person, which causes the noise level when measured on any other
exceed:
(1) The noise level standard for that land use as specified in Table
8.32.030 for a cumulative period of more than thirty minutes in
any hour;
(2) The noise level standard plus five dB for a cumulative period of
more than fifteen minutes in any hour;
(3) The noise level standard plus ten dB for a cumulative period of
more than five minutes in any hour;
(4) The noise level standard plus fifteen dB for a cumulative period
of more than one minute in any hour; or
(5) The noise level standard or the maximum measured ambient
level, plus twenty dB for any period of time.
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Table 8.32.030
NOISE LEVEL STANDARDS
Land Use CategoryTime PeriodNoise Level (dB)
R-E, R-1 and R-2 zones or 10 p.m.7 a.m.50
any single-family or duplex
7 a.m.10 p.m. 60
residential in a specific plan
district
R-3 and D-C zones or any 10 p.m.7 a.m. 55
multiple-family residential or
7 a.m.10 p.m. 60
mixed
residential/commercial in
any specific plan district
C-1, P-C, Gateway and 10 p.m.7 a.m. 60
Oyster Point Marina specific
7 a.m.10 p.m. 65
plan districts or any
commercial use in any
specific plan district
M-1, P-1 Anytime 70
Source: City of South San Francisco Municipal Code
Construction noiseexposureis also regulated by the Municipal Code (Section 8.32.050(d),
provided below). Hours of construction are exempt from the standards identifi
preceding paragraph and are limited to 8 A.M. to 8 P.M. Monday t
P.M. on Saturdays and 10 A.M. to 6 P.M. on Sundays and holidays.
enforces and monitors these regulations. Exceptions to the hours oand
maximum temporary noise levels may be granted by the Chief Building Official.
(a) Sound Performances and Special Events. Sound performances
and special events not exceeding eighty dB measured at a
distance of fifty feet from the loudest source are exempt from
this chapter when approval therefore has been obtained from
the appropriate governmental entity.
(b) Vehicle Horns. Vehicle horns, or other devices primarily
intended to create a loud noise for warning purposes, shall be
used only when the vehicle is in a situation where life, health
property are endangered.
(c) Utilities and Emergencies. Utility and street repairs, street
sweepers, franchised garbage services and emergency response
warning noises are exempt from this chapter.
(d) Construction. Construction, alteration, repair or landscape
maintenance activities which are authorized by a valid city
permit shall be allowed on weekdays between the hours of eight
a.m. and eight p.m., on Saturdays between the hours of nine a.m.
and eight p.m., and on Sundays and holidays between the hours
of ten a.m. and six p.m., or at such other hours as may be
authorized by the permit, if they meet at least one of the
following noise limitations:
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(1)No individual piece of equipment shall produce a noise
level exceeding ninety dB at a distance of twenty-five feet. If the
device is housed within a structure or trailer on the property,
measurement shall be made outside the structure at a distance as
close to twenty-five feet from the equipment as possible.
(2) The noise level at any point outside of the property
plane of the project shall not exceed ninety dB.
CGSBC
7.
ALIFORNIA REEN TANDARDS UILDING ODE
New California Green Building Code Standards became effective on January 1, 2014. The
mandatory and voluntary measures for residential, non-residential, and mixed use buildings are
designed to reduce our carbon footprint and promote environmental sustainability; i.e., decrease
impacts incumbent upon the environment resulting from human activities. The collection of
regulations is contained in the California Building Standards Code. The regulations prescribe
measures to reduce water consumption, reduce building constructireduce energy
consumption in both the construction and operation of buildings
The regulations prescribe methods to test, report, maintain, and
to promote environmental sustainability.
The Green Building Code also regulates the exposure (i.e., off gassin
compounds), aerosols, and formaldehyde, and moisture and dust penetration in the use and
application of building materials. Regulations address the typents, coatings, finishes,
flooring (wood, carpet, particle board), and architectural finishes that are not permitted based
upon the performance and potential toxicity of the substances. , as
appropriate, prohibit the amount of building heat loss and light pollution incident upon adjacent
properties. Standards address the use of potable, grey, and recycled water for interior and
exterior, residential, and non-residential uses.
Maximum Sound Transmission Class (STC) ratings are also identified and apply to interior
exposure levels and noise levels at property lines. Distance t
additional STC ratings for buildings within prescribed proximity, and 65 dB
exceedances at property lines.
Amenities to support people using bicycles are identified and in, and
secure lock-up areas. Provision of preferential parking spaces for low-fuel vehicles at a
percentage of overall parking provided on a site is also specified.
1.6 EFPA
NVIRONMENTAL ACTORS OTENTIALLY FFECTED
This Initial Study evaluates the Project which is defined as tha
Applicant and as modified by the City of South San Franciscos standard COAs,
identified above. Therefore, any impacts identified by the following Initial Study are
those that could exceed the impacts that would be mitigated by the Citys standard
permitting process and as such will require additional mitigation and/or additional
environmental review.
Environmental factors that may be affected by the Project, as defined by CEQA and as
described in Chapter 3, are listed below. Factors identified with shading have been determined
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to have the potential for significant impacts as discussed in Chapter 3. These factors wouldbe
addressed in an Environmental Impact Report or EIR. Factors which are unshaded have been
determined to pose no potential for significant impacts.
There are no potentially impacted areas therefore an EIR will no
following page.
Aesthetics Hazards &Hazardous Materials Public Services
Agriculture & Forest ResourcesHydrology and Water QualityRecreation
Air Quality Land Use and PlanningTransportation
Greenhouse Gas Mineral ResourcesUtilities &Service Systems
Biological Resources Noise Cumulative Impacts
Cultural Resources Population &Housing
Geology &Soils
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ROJECT ESCRIPTION
2.1PLS
ROJECT OCATION AND ETTING
PL
ROJECT OCATION
The Project site is located in the northern portion of the City of South San Francisco (City), in an
area known as the Paradise Valley/Terrabay planning sub area (South San Francisco ,
page 118, - SSF GP, 1999). The Project is in the western portion of the planning area in a single-
family neighborhood known as Sterling Terrace. 901 Larch Avenue is located at the terminus of
Lincoln Street where it intersects Larch Avenue. Lincoln Street is an approximate 600 foot
north/south trending neighborhood street connecting to Hillside Boulevard. Hillside Boulevard
provides access to both the western and eastern portion of the City. To the east, Hillside Boulevard
connects to and veers south of Sister Cities Boulevard. Sister Cities Boulevard in conjunction with
Airport and Oyster Point Boulevards form a leg of the Oyster Point Flyover. The Oyster Point
Flyover provides access to north and southbound U.S. Highway 101, as well as the East of 101 Area.
Hillside Boulevard provides access to the western and central portions of the City
of local, connector and arterial streets. Hillside Boulevard intersects Chestnut Avenue. Chestnut
Avenue turns into Westborough Boulevard when it crosses El Camino Real. Westborough
Boulevard provides access to Interstate 280, Skyline Boulevard and the City of Pacifica. Hillside
Boulevard also forms the boundary between the Town of Colma and South San Francisco
approximately 1,000 north of the Project site (Google Earth, 2015).
Sign Hill abuts the Project site to the southeast. The northern and northeastern facing slopes of Sign
Hill, consisting of approximately 46 acres, are in private ownership. Sign Hill Park is located on the
south facing slopes of the hill, is owned by the City and is public park and recreation land. Sign Hill
Park consists of 27 acres of open space with approximately two miles of hiking trailSign Hill is
home to the Mission Blue and Callippee Silverspot Butterflies both federally listed endangered
species. The park gets its name from the sign, South San Francisco the Industrial City which was listed
on the National Historic Register in 1996. The Project is on the north facing side of Sign Hill (s ee
Figures 1 Project Area and 2 Project Location).
Paradise Valley/Terrabay Planning Sub-Area
The Paradise Valley/Terrabay planning sub-area spans the northern slope of Sign Hill to the City
boundaries with the Town of Colma and City of Brisbane, and San Bruno Mountain County Park to
the north; Bayshore Boulevard to the South; and Hillside School
and Hillside Boulevards are within the planning area. The planning area is largely residential. Older
residential development, circa 1940-50, single family development is located south of Sister Cities
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and Hillside Boulevards. The townhouse, single-family detached, duplex and condominium
development associated with Terrabay Phases I and II are north of Sister Cities and Hillside
Boulevards.
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ROJECT ESCRIPTION IGURE
PA
ROJECT REA
The Hillside and Martin Schools are within the planning area. T
800 feet northwest and Martin School is approximately 4,000 feet souroject. Hillside
School was closed in 2005. Hillside Christian Academy is at 1415 Hillside Boulevard and Mil
Montessori School is located at 1400 on the north side of Hillside Boulevard. Hillside Chris
Academy is approximately 350 feet northwest of the Project site.Mills Montessori School is located
approximately 700 feet north of the Project site.A small pocket of commercial land useis located
southeast of the Project bounded by Hillside Boulevard, North SpAvenues.
Terrabay Phase III fronting Airport Boulevard is also in the planning sub area, consisting of research
and development, retail and office commercial land uses. Business commercial land uses are also in
the planning sub-area along Airport Boulevard.
The planning sub-area includes the Terrabay Fire Station, Terrabay Recreation CenHillside
Recreation Center, the Preservation Parcel associated with Terrabay Phase III now dedicated as part
of San Bruno Mountain County Park, the history trail on the Terrabay Phase III site, the shared use
performing arts facility located in the South Tower of Terrabay the linear park along Sister
Cities Boulevard, a pocket park on Linden Avenue, and open space and recreation uses associated
with the schools. Additionally, there is a proposed linear park along the PG&E transmission towers,
near Pecks Lane, in the eastern portion of the planning area (SSF GP, 1999, p 175). Adjacent to the
planning sub-area and within approximately 300 feet of the Project site is the parkland of Sign Hill.
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Project Site
The Project site is vacant with an approximate 44.7% slope (GeoTrinity Consultants, Inc.,
Geotechnical and Geologic Investigation, Residential Development 901 Larch Avenue
California. May 1, 2015). The site measures 150 feet in depth by 50 feet in width consisting o
square feet. The site is fronted by Larch Avenue and is situated in predominately a
northwest/southeast direction. Adjacent properties and boundari
th
northwest, a single-family mid-20 century residence on the northeast, privately owned open space
1
southeastand an undeveloped property on the southwest (see Figure 2).Multi-family housing
development is adjacent to the Project area to the west.
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ROJECT ESCRIPTION IGURE
PSV
ROJECT ITE AND ICINITY
The 46 acres of land on the northeastern slopes of Sign Hill aresignated open space on the Citys
1
General Plan Land Use Map, and zoned for one unit per acre. Development on these lands would require at a minimum
a biological assessment to determine if endangered or threatened s If endangered
species/habitat is present the formation of a Habitat Conservation Plan (HCP) would
protect habitat, require open space and direct and limit development areas to less sensitive land.
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2.2PP
ROPOSED ROJECT
PD
ROJECT ESCRIPTION
The Project proposes an approximate 2,500 square foot residence consisting of 2,038 square feet of
living area and an approximate 460 square foot garage. The lot slopes uphill from Larch Avenue.
The residence would consist of a partially subterranean garage,
square feet and a second floor consisting of 733 square feet (Sheets A-1 and A-2, Plan Drawings,
GeoTrinity, February 9, 2015). See Table 1 for setbacks and other data and Figure 3 for the site
plan.
rd
The structure is proposed on the front 1/3 of the lot. Landscaping is proposed in the front, side
and portions of the rear of the property. Planting of Japanese Maple, Winter Boxwood, Star
Jasmine, camellia, and lavender are proposed.
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ROJECT ESCRIPTION ABLE
PD
ROJECT ATA
CRITERIA MEASUREMENT CITY STANDARDS
Lot Coverage 18 % 50% maximum
Floor Area Ratio 0.330.50 maximum
Height (Maximum) 27-9.5 28 maximum
Setbacks
Front 15 15 minimum
Side 5/5 5 minimum
Rear 92.75 20 minimum
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ROJECT ESCRIPTION IGURE
SPAL
ITE LAN AND PPROXIMATE OCATION OF
SBRF
OUND ARRIER AND OCKFALL ENCE
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Geology and Biology
As noted in Chapter 1, Legislative Framework, the Project site contains geological constraints
including a very steep slope (40 to 70%)(Cotton Shires Associates, Inc., (CSA) City geotechnical
peer reviewer, Ted Sayre,Principal Engineering Geologist, September, 2015), shallow slope
instability (i.e., two foot-deep and six foot wide earthflow scars) one-on and one-off site, and an
upslope fill prism. The site is adjacent to Sign Hill, a known biological resource within the City o
South San Francisco. These issues are vetted fully in Chapter 3, Environmental Checklist and are
briefly described in the Project Description as they are the drion of this
2
initial study.
According to Ted Sayre, grading could involve 410 cubic yards of cut, or more. All the material
would require removal and disposal. Off-haul trucks (dump trucks) vary in capacity from five to 10
cubic yards per load. Earth material tends to fluff in volume when excavated; approximately
Therefore, 46 to 94 trips to and from the site would be required resulting in a round trip volume of
92-188 one-way truck trips, for grading alone.
The Project requires and proposes the construction of rockfall fencing or a similar catchment devi
to protect the residence adjacent to (northeast side) the Project, as identified in the Applicants
geotechnical report. According to GeoTrinity Consultants and CSA, it would be during the grading
and construction phase of the Project that the catchment device(s) would be required. Figure 3
shows the approximate location of the rockfalll fence.
The northern (front) portion of the site is approximately 404 feand the
rear 476 feet msl. Vertical cuts up to 22 feet in height would be required on the northeast, southeast,
and southwest sides of the residence. Retaining walls ranging from four to 19, and possibly 22 feet
in height would be required (GeoTrinity Consultants, Inc., Geotechnical and Geologic Investigation,
Residential Development 901 Larch Avenue, South San Francisco, C. May 1, 2015).
2
Typically, the construction of one single-family residence in a residential zone with utilities and infras
categorically exempt from the CEQA requirements (CEQA Guidelines section 15303, Class 3 New Construction or
Conversion of Small Structures). However, there are exceptions CEQA Guidelines section
15300.2, subsection (a). Subsection (a) clearly states Class 3 exemptionsupon where the project
would be located. The subsection further notes a project that in
environment may in a particularly sensitive environment be signited in a
biological habitat, or on steep or potentially unstable slopes,
contamination (hazardous materials), the exception to the exempt
initial study, which may be satisfied by utilizing the sample forms provided in App CEQA
Guidelines.
The Project site contains several geological constraints, includ-site (i.e.,
two-foot deep and six-foot wide earthflow scars) and another off-site, and an upslope fill prism. The site is also adjacent
to Sign Hill, a known biological resource within the City of Sou
Francisco has prepared an initial study for the Project, based upon the known geotechnical constraints,
unknown and potential biological issues.
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Air Quality, Greenhouse Gas, Hazard Risk and Noise Assessments
Given the amount of grading and geotechnical repair required for
Gas and hazard risk assessments were performed and are fully vetted in Chapter 3 Environmental
Checklist.
Earthmoving, pile drilling (not driving) and construction will increase noise levels in the Project area.
The Project area is residential and considered a sensitive recepA noise assessment was
performed and a temporary sound barrier is proposed on the north
noise impacts to the adjacent residence that is located five feet from the c
Figure 3 shows the approximate location of the temporary sound barrier. N
fully vetted in Chapter 3 Environmental Checklist.
Construction Schedule
The applicant indicates a 220 working day construction period, i.e., 32 if construction is seven days a
3
week to 44 weeks if it is five days a week. Table 2, below identifies the phases and anticipated
duration of construction activities. Phases 1 and 2, site preparation and grading would be the most
intrusive aspects of construction and would take approximately 35 days to complete.
PDT2
ROJECT ESCRIPTION ABLE
CS
ONSTRUCTION CHEDULE
WORKING
PHASE DESCRIPTION
DAYS
1 Site Preparation 5
2 Grading 30
3 Building Construction150
4 Paving 5
5 Architectural Coating 30
2.3EMMP
NVIRONMENTAL ITIGATION EASURES ROPOSED
PP
AS ART OF THE ROJECT
The following measures are included as part of the Project, and
drawings, in the Project application materials and in Appendix A (Environmental Mitigation Measures
[proposed by Applicant], Vinal Nand. December 2, 2015). These measures are in addition to the
Citys standard requirements identified in Chapter 1, Legislative Framework. Therefore, the
following measures are considered part of the Project for the CE
any of these measures may result in a significant environmental , and may require further
CEQA analysis.
As noted in Chapter 1, Legislative Framework, the Citys Noise O
3
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A.Biology
1. Tree Removal Within Nesting Season (approximately March 1 to August 31).
Applicantor designated representativewill retain a qualified biologist to conduct a preconstruction
survey for protected birds on the site and in the immediate viciif Project construction activities
occur during nesting season. The survey will be done no more than 15 days prior to the initiation of
tree removal and grading and other construction activities. In the event that nesting birds are fo
on the Project site or in the immediate vicinity, Applicant will notify the City, locate and map the
nest site(s) within three(3)days, submit a report to the City and the California Department of Fish
and Wildlife ("CDFW"), establish a no-disturbance buffer of 250-feet, and conduct on-going weekly
surveys to ensure the no-disturbance buffer is maintained. In the event of destruction of
eggs, or if a juvenile or adult raptor should become stranded from the nest, injured or ki
qualified biologist will immediately notify the CDFW. The qualified biologist will coordinate with
the CDFW to have the injured bird either transferred to a raptor, in the case of
mortality, transferit to the CDFW within 48 hours of notification; or,
2. Tree Removal Outside Nesting Season. Tree removal outside of the nesting season
would preclude the need for the measures identified in A.1, above. Per South San Francisco
Municipal Code Section 13.30.030 (Tree Preservation Ordinance), a permit is required pr
removal of a Protected Tree, defined in section 13.30.020 as: (1) Any tree with a circumference of
forty-eight inches or more when measured fifty-four inches above natural grade; or (2) A tree or
stand of trees so designated by the director based upon findings
to the public due to its unusual appearance, location, historica(3) A
stand of trees in which the director has determined each tree is
survival. Prior to removing trees, the applicant or designated representatwill contact the Parks
Division to determine if a removal permit is needed.
B. Geology and Soils
The conclusions and requirements presented in the following will be incorporated in the design
and construction of the Project to minimize possiblesoil,slope,andfoundationrelatedproblems.
The Geotechnical Consultant of Record (GCR) conducted the site work and developed the
parameters and requirements by which to construct the Project. T
consultant, Cotton Shires Associates (CSA), conducted peer review of GCRswork. The
grading and construction requirements are excerpted from the fol
as part of the Project. The reports are included in Appendix A in their entirety. Although the
geotechnical measures are summarized herein the following reports will also be reviewed,
understood, and implemented in full by Applicant and Contractor and shown on the grading and
construction drawings and practices in the field.
GeoTrinity Consultants, Inc., Geotechnical and Geologic Investigation, Residential Development 901
Larch Avenue, South San Francisco, California. May 1, 2015.
GeoTrinity Consultants, Inc., Supplemental Letter for May 2015 Report and August 6, 2015 Plans
August 18, 2015.
GeoTrinity Consultants, Inc., Response to Peer Review Letter. September 23, 2015.
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Cotton Shires Associates, Inc., Geotechnical Peer Review, Nand New Residence, 901 Larch Avenu.
May 26, 2015.
Cotton Shires Associates, Inc., Supplemental Geotechnical Peer Review, Nand New Residence, 90
Larch Avenue. October 2, 2015.
The following standards are taken directly from GCRs reports as
terms are presented as they appear in the original reports. The Appendix
A.
The stabilityofthe unsupported verticalcuts during construction is a concern. Stormwater runoff
and potential sloughing of surficial soil on the upslope sides of the Project will be managed.
Drainage improvements will be emplaced toprovide positive drainage away from the
buildings and to collect and channel surface waterrunoffto suitableoutlets.
Detailed earthwork and foundation requirements for use in design theroject
will be implemented. GCR (or qualified successor) will review the final design andspecifications to
assure quality control. GCR will be on site full time during the initial grading and intermittently during the
remaining site work. GCR will as necessary make changes to practices and methods to assur
and stability of the Project and adjoining properties. CSA will be present on the Project site intermittently
to oversee grading operations.
1.Earthwork
Excavation
Construction will be scheduled so that temporary vertical cuts are created andleftunsupported
(before placement of concrete) only during a dry time of year. GCR and CSA will observe the
excavations at frequent intervals asthey proceed in stages, e.g., every 5 vertical feet. As noted
(Cotton Shires Associates, Inc., Geotechnical Peer Review, Nand New Residence, 901 Larch Avenue. May
26, 2015 and GeoTrinity Consultants, Inc., Supplemental Letter for May 2015 Report and August 6, 2015
Plans. August 18, 2015) blocks of rock (eight inches or less in diameter) could come loo
bounce towards the adjacent house during this phase of grading (CSA, GeoTrinity). A catchment
fence will be constructed along the property line of the Project site adjacent to the southwestern
corner of 859 Larch Avenue (see Figure 3) to protect the adjacent house from spalling rocks
during slope cut operations. The rockfall fence will be a minimum of four feet in heig
constructed of biaxial geotextile and attached to steel fence po
of 9/23/15, p 3. (Note: This is a temporary protective structureed for placement
during the early excavation work. Once a flatter bench is excava
property then there will be no slopes to direct rockfall toward to adjacent residence).GCR will be
on site during excavation to observe conditions and modify the height or length of time the rock
fall fence is in place. GCR may modify cutslopes to be "laid back", where feasible due to property
line constraints, to reducepotentialinstability.
The contractor (Contractor) will observe the bedrockconditions exposed near the site and will
anticipate the possible presence of localizedconditionsharder than those exposed there, before
selecting equipment for the excavation work.
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Contractor will be aware of current Occupational Safety and Health Administration (OSHA)
Health and Safety Standards for Excavations,29 Code of Federal Regulations (CFR), Part 1926 and
implement the standards.
Thestabilityoftemporarycutslopesmayvaryfromoneplacetothenext,varywith
changing moisture (groundwater) conditions and may requiretemporary support. Contractor's
responsible person, as defined in 29 CFR, Part 1926, will evaluate the material exposed in the
excavations as part of Contractor's safety procedures.
Subgrade Preparation
After completion of clearing and stripping, soil exposed in areas to rslabson
grade, or pavements will be scarified to a depth of 6 inches, mo toslightly
above optimum water content, and compacted to the requirements for structural fill.
To achieve satisfactory compaction of the subgrade and fill materials, it may be necessary to
adjustthewatercontent atthe time of construction. This adjustment may consist of addingwater
to subgrade soils that are too dry or performing aeration and allowing for drying time in areas
where subgrade soils are too wet.
Fill Material
On-site soilbelow thestripped layer andhaving an organic content of less than 3 percent by
volume can be used as fill. All fill placed at the site, including on-site soils, will not containrocks
or lumps larger than 6 inches in greatest dimension, with no mor larger
Compaction
All fill and scarified surface soils in those areas to receive fslabs-on-grade will be compacted
to at least 90 percent relative compaction as determined by ASTM Designation01557, latest
edition, at moisture contentnear the laboratory optimum. Fill will beplacedinlifts no greater than
8 inches in uncompacted thickness. Each successive lift will be firm andnonyielding under the
weight of heavy construction equipment.
In pavement areas, the upper 6 inches of subgrade and full depth of aggregate base will be
compacted to at least 95 percent relative compaction(ASTM 01557-91). Aggregate base andall
importsoils will be compacted at moisture content near the laboratory optimum.
Trench Backfill
Bedding and shading materials around underground utility pipes wpredominantlygranular
and will be placed and compacted in accordance with Project specifications, localrequirements, or
other governing jurisdiction. General fill to be used above shad materialsbeplacedand
compacted inaccordance with local requirements or the recommendationspresented in this section,
whichever is more stringent.
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The surficial brown clayey sands encountered during site charactgeneral
fill above shading materials provided they meet requirements uFill Material.
General fill will be placed in lifts not exceeding 8 inches in uandbe
compacted to at least 90 percent relative compaction (ASTM 01557bymechanical
means only. Jetting of trench backfill will not occur. The upper 12 inches of general fill inbuilding
pad and pavement areas subject to wheel loads will be compacted to atleast 95 percent relative
compaction. Thicker lifts may be attempted, provided that the method ofcompaction is approved
by the geotechnical engineer and the required minimum degreeofcompactionisultimately
achieved.
The trenches will be backfilledby an impermeable plug at the exterior wall foundation whereutility
trenches backfilledwith sandenterbuilding pads. The plugs can be composed ofcompacted clayey
soil, compacted bentonite, or a bentonite-cement or sand-cement slurry mixture. The plugs will be
at least 2 feet thick and will extend at least 2 feet beyond theedges and bottom of the trench to
"key in" the plug. The plug will also extend verticallytowithin 1 foot of lowest adjacent grade.
Surface Drainage
Positive surface gradients will be provided adjacent to the struwateraway
from foundations and slabs toward suitable discharge facilities. Similarly, roof downspoutsbe
connected to solid collector pipes that discharge to appropriate surfacewater
will not beallowed adjacent to the structures or on pavements.
Guide Specifications
will Guide SpecificationsSite Earthwork (GeoTrinity
Consultants, Inc., Geotechnical and Geologic Investigation, Residential Development
San Francisco, California. May 1, 2015,
in GeoTrinity Consultants, Inc.,
Geotechnical and Geologic Investigation, Residential Development
California. May 1, August 6 and September 23, 2015 and Cotton Shires Associates, Inc., Geotechnical
Peer Review, Nand New Residence, 901 Larch Avenue. May 26, 2015 and October 2, 2015, found in
Appendix A.
2.Foundation Support
The foundations of the new residence and retaining walls will generally consist of piers andgrade
beams. Retaining walls no more than 4feet tall can be supported by spread footings.
Foundation Piers
The piers will be cast-in-drilled-hole, straight-shaft piers that develop their load-carryingcapacity by
side resistance between the pier concrete and surrounding materi thesite conditions
encountered, it is assumed that the excavations for the piers will generally exposethesandstone
bedrock. Geotechnicaldesign parameters for foundation piers arepresented in the
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PDT3
ROJECT ESCRIPTION ABLE
PDP
IER ESIGN ARAMETERS
PARAMETER VALUE
Minimum spacing center to centerThree pier diameters
Minimum pier diameter 16 inches
Maximum length 10 feet
Allowable skin friction, compression 400 pounds/square foot
The allowable skin friction values are for dead loads and may be-third forallloads
including wind or seismic. Eighty percent of side resistance can be used to resist uplift.Pier
reinforcingwill be based on structuralengineering requirements. Grade beams will bedesigned to
spanbetweenpiers.
Before selecting equipment for the drilling of the pier holes, Cbedrock
conditions exposed nearthesiteandanticipate the possible presence of localizedconditions harder
than those exposed. The bottomsofthe pier excavations will berelatively dryand free of
loose cuttings or slough prior to placing reinforcing steel and concrete.Anyaccumulated water inpier
excavationswill be removed prior to placing concrete. All retaining walls will be supported with pier
foundations to relieve surcharge loads adjacent to tall basement walls (CSA, May 26 and
2015 and GeoTrinity September 22, 2015).
Spread Footings
Retaining walls no taller than 4 feet will be supported on conventionalcontinuousandisolated
spread footings bearing on either undisturbed native soils or compactedfill. Footings will be at
least 18 inches wide and founded at least 18 inches belowlowest adjacent finished grade.
Footings locatedadjacentto other footingsor utility trenches bear below an imaginary 1.5:1
(horizontal to vertical) plane projected upward fromthebottom edge ofthe adjacent footingsor
utility trench.
All retaining walls exceeding 4 feet will utilize a pier supported foundation.
The footings will be designed for an allowable bearing pressure (pounds per square
foot) due to deadloads, 3,800 psf due todeadplus live loads, and 4,500 psf for all loads,
including wind or seismic. These allowable bearing pressures are net values; th
of the footingcan beneglected for design purposes.
Continuous footings will be designed with at least twobars,both top and bottom. This
#4
minimum reinforcing will provide structural continuity and permi localirregularities.
Any visiblecracksin the bottoms of the footing excavations will be closedby wettingprior to
construction ofthe foundations. GCR will observe the footing excavations prior toplacing
reinforcingsteel or concrete,to check thatfootingsare founded on appropriate material.
GCR estimates that post-constructiondifferential movement between adjacent columns will be
no greater than 1/2inch. GCR will be retained to review the final foundation plans and structural
loads to verify the above settlementestimates.
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Lateral Resistance
Lateral load resistance for the proposed structures and retainina
passiveresistanceof350psftoamaximumvalueof4,000psfactingagainsttwicetheprojected
area of the individual pier shafts be used for design; and aresistance coefficient of 0.35 betweenthe
foundation bottom and the supporting subgrade for spread footingalternative, a passive
resistance equal to an equivalent fluid weighing 400 pcf acting faceofthe
foundationscouldbeused.foundationsarepouredneatagainstthesoil,thefrictionandpassive
resistance can be used in combination. The uppermost one foot ofwill beneglected for
passive pressure design, unless the adjacent grade is directly oor pavement.
3.Interior Slabs on Grade
Interior slabs on grade, if used, will be supported on a minimum of 12 inches ofimported
nonexpansive compacted fill. Alternatively, if the slab is reinforcedwith a minimum of #4 bars on
18-inch centers both ways for shrinkage control, the slab could be supported on 6inches of
nonexpansive fill. Slab reinforcing will be providedinaccordance with the anticipated useand
loadingof the slab with either alternative.
A moisture barrier will be provided between theslab and subgrade below interior slabs-on-grade in
living spaces. Moisture barrier will consist of 4 inches of
10-mil thick impermeable membrane (or Moistop) placedbetween the subgrade soil and the slab.
The membrane will be covered with 2 inches of sandfor protectionduring construction. Thesand
will be lightly moistened just prior to placing theconcrete. The moisture barrier can be used in lieu
of the upper 6 inches ofrecommendednonexpansive fill. a wall or footing is not present at the
edge of the slab to provide a watercutoff for the moisture barrier, a minimum 12-inch wide
concrete barrier or "thickened edge"that is supported directly on the subgrade materials will be
provided at the perimeter of theslab.
Carpetsthat allow air to pass through them be will used over concrete floorslabs. vinyl or wood
floor tilesare to be used, the concrete floor slab will be given sufficient time to air dry before the
tilesare installed. Alternatively, a floor sealant could be applied o minimize
moisturefromaccumulatingunder the floortiles.
4. Exterior Slabs
The driveway and walkways will be supporteddirectlyon properlyprepared nativesoils or
compacted fill. Elimination of a rock base beneath slabs will mi for migration
of landscape irrigation water into subgrade soils below walkways an A few days
prior to placing concrete, subgrade soils will be moistened to yield a moisturecontent
approximately that of or slightly above the optimum moisture conTestMethod
D-1557, latest edition. The water content of subgrade soils will be verified by fieldtesting by the
geotechnical engineer priortoplacing concrete.
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5.RetainingWalls
the
All cutswill besupported by retainingwalls. In addition, the wall along the southwest side of
residence will be extended upward toprovide an additional 2 feet of "freeboard"to deflectsmall
debris flowsthat may emanate from the fill wedge on the neighboring property the southwest.
The walls will be supported by pier or footing foundations in accordance with the requirement
Retaining walls that are not restrained at the top will be designedto resist an active load due toan
equivalentfluidpressure of 40 pounds per cubic foot (pcf). Retaining walls that will be
restrained at the top will be designed to resist an equivalent fluid pressure of 55 pcf. Thesevalues
assume level backfill. Walls with inclined backfill will be designed for an additionalequivalent fluid
pressure of for every2° of slope inclination.
These lateral pressures assume a drained condition. To prevent a build-up of hydrostatic pressures,
each retaining wall will be provided with a permanent rear subdrain. The subdrain will consist of a
vertical blanket of ½--inch to ¾-inch crushed drain rock wrapped in filter fabric such as Mirafi l
40N orequivalent. Alternatively, Class 2 permeable material conforming to Section 68.1025 of the
State of California Standard Specifications may be used in lieu of the drain rockandfilter fabric. The
permeable material blanketwill be at least 12 inches thickand will beplaced from the base of the
retaining walltoabout 1 foot below finished grade at the top of the wall. As a third alternative,
Miradrain, Enkadrain matting, or similar drainage panels, subject to approval by the GCR, may be
used for wall drainage. Damp-proofing of the walls will be included in areas where interior wall
moisture would be undesirable. A 1-foot cap of compacted native soil will be placed over the
permeable material to achieve finished grade.
Each subdrain will be provided with a 4-inch-diameter perforated PVC pipe (SDR 35) (standards
of pipe). Theperforated pipe will be placed, perforations facing down, near the bottom of the wall
and be surrounded by a few inches of subdrain rock material or connepanel
material, whichever is used. The downstream end of the pipe(s) will be connected to thecollection
facilities described belowunder the heading
Surface Drainage.
Backfill behind the drainageblanket will consist of soil placed in level lifts about 8 inches inloose
thickness, moisture conditioned to about theoptimum moisture content, and mechanically
compacted to at least 90% relative compaction. Relative compacti-placedry
density of soil expressedas apercentage of maximum drydensityofthe samesoil, as determinedby
TestMethod latest version. In lieu of compacted backfill, the subdrain materialmay
ASTM 01557,
take up the entire space behind the retaining wall.
The tops of walls backfill subject to slope runoff, e.g., the wa (southeast,
upslope)and the wall on the southwest side of the residence, will be provided with aconcrete-
lined V-or U-ditch whose downstream end is connected to the collectionfacilitiesdescribed
belowunder the heading
Surface Drainage.
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6.SurfaceDrainage
All roof downspouts, any drainsin paved patiosor walkways, and the downstream ends of V- or U-
ditches will be connected to solid pipes (type-SOR35 or schedule40) to avoid infiltrationof thesite
soils. These pipes will be directed to appropriate discharge point(s) in the front of the
7.Seismic DesignFactors
GCR developed site-specific spectral seismic design parameters are based on the 201
International Building Code,which is based on U.S. Geological Survey hazard data available in
2008. These designparameters are for use by the structural engineer when addressin
seismic shakingindesigning theproposed residence, including retaining walls.
Based onthespecificsitelocation bylatitude and longitude, Ss and S1 are 2.092 g and 0.991 g,
respectively. GCR classifiedthesite as Site Class C,i.e., soft rock, based on itsdense fracture
pattern and an estimated average blow count value) of 90 in the 0-100-foot depthinterval
(N
below the site.
Based on the sitelocation andspecific Site Class C, GCR developedthe seismic designparameters,
summarized in Table 4, below:
PDT4
ROJECT ESCRIPTION ABLE
PSDP
ROJECT EISMIC ESIGN ARAMETERS
PARAMETER VALUE
S 2.092 g
MS for 0.2-second period
S1.288 g
M1 for1.0-second period
S1.394 g
DS for 0.2 -second period
S 0.859 g
D1 for 1.0-second period
8. CSA (October 2, 2015) notes and reinforces the following Project
will be implemented.The following is a direct quote from CSA Peer review letter Octo
2015 with citations added by the author of this report.
Final Design Plan Details
Final Project construction plans will include retaining walls w
freeboard on the downslope side of the existing fill wedge along the we
property and surface drainage ditches will be detailed atop reta
southwestern and southwestern sides of the residence (per GeoTrinity, September 23, 2015).
Prior to initiation of grading, a temporary catchment fence will
property line and downslope of the excavation work (per GeoTrinity direction).
Geotechnical Construction Inspections
The GCR will inspect, test (as needed), and approve all geotechnical aspects of Project
construction. The inspections will include, but not necessarily
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and grading, site surface and subsurface drainage improvements,
foundations and retaining walls prior to the placement of steel and concrete.
The results of these inspections and the as-built conditions of the Project will be described
by the GCR in a letter and submitted to the City Engineer for re
Certificate of Occupancy.
C. Noise
Applicant will employ the following mitigation measuresto comply with the Citys Noise Ordinance
(South San Francisco Municipal Code Chapter 8.32)and reduce noise impacts due to construction at
nearby sensitive receptors to the maximum extent feasible:
1.Secure an exception permit for noise levels that could temporari
line in order to comply with the Citys Noise Ordinance.
2.Construct a temporary noise barrier between the Project and 859 adjacent to the
site on the east (see Figure 3). The noise barrier will remain in place for the duration of
construction. The barrier will be constructed on the eastern pro
be long and tall enough to block the line of sight between construction activities and the
adjacent sensitive receptor. Temporary barriers will be constructed from materials such as
plywood lined with noise-absorbing material, commercial panels lined with sound absorbing
4
material, or noise blankets or curtainsand will have a Sound Transmission Class (STC) rating
of STC 30 or greater. Examples of noise control blankets and sound curtains as well as
installation of these features can be viewed on the following we
http://www.allnoisecontrol.com/outdoor-noise-control-blankets.cfm).
3.Enclosures for stationary equipment and movable barriers will be
sensitive receptors to the north and west of the Project site to
barriers will be located as close as possible to the noise sourcffective. Portable
panels and noise curtains are examples of movable temporary noise barrier systems that
might be feasible on the hillsides. Enclosures around stationary equipment can provide a 10
to 20 dB sound reduction and barriers or noise curtains can provide a 5 to 20 dB sound
reduction in noise levels.
4.Ensure that construction equipment is properly muffled according
5.Provide advance notification to surrounding land uses disclosing
including the various types of activities that would be occurring throughout the
construction period.
6.Designate a member of the construction team as an on-site construction noise contact who will
act as a Neighborhood Liaison for the duration of the Project. The Neighborhood Liaison will
4
Sound Transmission Class (STC) is a widely used rating for how well a building part
STC ratings are used to rate interior partitions, ceiling/floors
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respond to noise issuesand implement solutions, if feasible and necessary in additionthose
identified herein. For example, a neighbor may have a special event that requires
environment for a few hours or a day, such as a wedding, birthday party or memorial service,
and the construction schedule may be able to accommodate a breakafew hours.
7.Post signs around the Project site to inform persons of the cons
and phone number of the person or persons to notify in the event of
(Construction Team Neighborhood Liaison).
2.4 GPZ
ENERAL LAN AND ONING
GPD
ENERAL LAN ESIGNATION
The Project site is designated Low Density Residential (RL) permitting up to eight (8) units per acre.
th
The site is in within the Sterling Terrace neighborhood, constructed in the mid-20 century
consisting of single-family detached residences. The terminus of Larch Avenue (to th
abuts multi-family designated and developed properties.
ZC
ONING LASSIFICATION
The Project site is zoned Residential Low Density allowing a maximum of eight (8) units per acre
(RL-8).
2.5 RE
EQUIRED NTITLEMENTS
LAR
EAD GENCY EQUIREMENTS
Design Review
Grading and Building permits.
Encroachment permits to work in the public right-of-way.
OARP
THER GENCY EQUIRED ERMITS
Local and State approval of a Stormwater Pollution Prevention Pl
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3
EC
NVIRONMENTAL HECKLIST
EC
NVIRONMENTAL HECKLIST
The following checklist is consistent with CEQA Guidelines, Appe
response indicates that the Project would not result in an envir
of interest, either because the resource is not present, or the Project does not
cause an effect on the resource. A response indicates that, while there may
be potential for an environmental impact, the significance of thpact would not exceed
established thresholds and/or that there are standard procedures
apply to the Project and hence no mitigation is required, or tha
significant impact, feasible mitigation measures are available and have been agreed to and proposed
. A
by the Project to reduce the impact to a level of
response indicates that the Project could exceed established thresholds, no
mitigation is currently proposed or identified and therefore the impact will be analyzed in an
environmental impact report. A response indicates that
although the impact would be considered significant, measures are identified and required herein
that will reduce the impact to less than significant.
Citations for this chapter are contained within the relevant dis
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3.1A
ESTHETICS
PotentiallyLess ThanLess Than
Significant Significant Significant No
with
ImpactImpactImpact
Mitigation
Would the Project:
X
a) Have a substantial adverse effect on a scenic
vista?
X
b) Substantially damage scenic resources,
including, but not limited to, trees, rock
outcroppings, and historic buildings within a
state scenic highway?
X
c) Substantially degrade the existing visual
character or quality of the site and its
surroundings?
X
d) Create a new source of substantial light or
glare, which would adversely affect day or
nighttime views in the area?
S
ETTING
SSF
OUTH AN RANCISCO
South San Franciscos urban character is one of contrasts within-defined setting.
San Bruno Mountain to the north, the ridge along Skyline BoulevaUS 380 to the
south, and the San Francisco Bay to the east provide the City with distinctive edges. The
contained in almost a bowl-like fashion by hills on two sides. The Citys terrain ranges from the
flatlands along the water to hills east and north. Hills are vi of the City, and
Sign Hill and San Bruno Mountain are visual landmarks. Much of
rolling, resulting in distant views from many neighborhoods. Ge
relatively small, extending approximately two miles in a north-south direction and about five
miles from east to west. South San Franciscos industrial roots
character, especially in its eastern parts.
PAS
ROJECT REA AND ITE
The Project site is located in the northern portion of the City of South San Francisco, in an area
known as the Paradise Valley/Terrabay planning sub-area (South San Francisco General Plan,
1999, page 118 (SSF GP, 1999)). The Project site is in the western portion of the planning
sub-area in a single-family neighborhood known as Sterling Terrace. 901 Larch Avenue is
located at the terminus of Lincoln Street where it intersects Larch Avenue (see Figure 1 Project
Area and Figure 2 Project Location in Chapter 2). Lincoln Street increases in elevation from
Hillside Boulevard to Larch Avenue, 293 to 345 feet in elevation; a rise of 52 feet. Larch Avenue
also increases in elevation from Kearny to Lincoln Streets from 259 t
intersection of Lincoln Street and Larch Avenue; a rise of approximately 89 feet (Google Earth,
2015).
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Sign Hill abuts the Project site to the southeast. The northern and northeastern facing slopes of
Sign Hill, consisting of approximately 46 acres, are in private ownership. Sign Hill Park is
located on the south facing slopes of the hill, is owned by the City and is public park and
recreation land.Sign Hill Park consists of 27acres of open space with approximately two miles
of hiking trailsand along a ridge spur reaches approximately 600 feet in elevati. Sign Hill is
home to the Mission Blue and Callippe Silverspot butterflies, both federally-listed endangered
species. The park gets its name from the sign, South San Francisco The Industrial City which was
listed on the National Historic Register in 1996. The sign is outh facing slope of Sign
Hill. The Project is on the north facing side of Sign Hill(s eeFigures1 ProjectAreaand2
Project Location in Chapter 2).
Adjacent properties and boundaries include Larch Avenue to the n-family mid-
th
20Century residence on the northeast, privately owned open space on the southeast and an
undeveloped property on the southwest that once contained a water tower. Multi-family housing
is adjacent to the Project area to the west and southwest. One of the multi-family units can be
viewed at the terminus of Larch Avenue, a rather large structure comparatively speaking with a
solid wall rising approximately 50 feet above the elevation of L (see Aesthetics
Figure 1). Houses in the subdivision are predominately one-story over a garage on sloping lots
that result in more massing on the downhill portion of the struc Aesthetics Figures 2
and 3).
AF1
ESTHETICS IGURE
BWMF
ACK ALL OF ULTI AMILY
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AF2
ESTHETICS IGURE
SFNP
INGLE AMILY ORTHWEST OF ROJECT
AF3
ESTHETICS IGURE
SFAP
INGLE AMILY DJACENT TO ROJECT
PSF
ROJECT ITE IN OREGROUND
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The Project site is vacant with an approximate 44.7% overall slope (GeoTrinity Consultants,
Inc., Geotechnical and Geologic Investigation, Residential Developmentarch Avenue, South San
Francisco, California. May 1, 2015). The site measures 150 feet in depth by 50 feet
consisting of 7,500 square feet. Lots in this area of the single-family subdivision are
predominately oriented in a northwest/southeast direction.
Vegetation on the Project site consists of introduced grasses an
have spread from nearby garden landscaping including grasses andweeds. Three trees are on the
site: apine tree (Pinus sp.) about 11 inches diameter at breast height (dbh), a Monterey cypress
(Cupressus macrocarpa)) about 24 inches dbh and a deodar cedar (Cedrus deodara), about 18 inches
dbh (Michael Marangio, Biological Resources Assessment prepared for Allison Knapp Wollam,
Consulting, Proposed Residence, 901 Larch Avenue, South San Francisco, California.
1
November 10, 2015). The three trees would be removed to construct the Project.
South San Francisco Municipal Code Section 13.30.020 defines a P
circumference of 48 or more when measured 54 above natural grade; a tree or stand
designated by the Director of Parks and Recreation as one of uni
public due to its location or unusual appearance, historical sigor a stand
of trees that the Director of Parks and Recreation has determine
others for survival. The trees on the site are not protected by City definition. See Section 3.5
Biological Resources for more information on biological resources.
Project construction is proposed on the front one-third of the lot. Landscaping is proposed in
the front, side, and portions of the rear of the property. Japanese Maple, Winter Boxwood, Star
Jasmine, camellia, and lavender are proposed (see Figure 3 in Project Description). Table 1
Project Data from Chapter 2 is reproduced below for convenience. As shown in the table, the
Project meets or exceeds the minimum setbacks and is under the m,
and floor area ratio prescribed by City ordinance (SSFMC 20.080).
AT1
ESTHETICS ABLE
PD
ROJECT ATA
CRITERIA MEASUREMENT CITY STANDARDS
Lot Coverage18 %50% maximum
Floor Area Ratio 0.330.50 maximum
Height (Maximum) 27-9.5 28 maximum
Setbacks
Front 15 15 minimum
Side 5/55 minimum
Rear 92.7520 minimum
In all likelihood one tree, and not three, would be removed to construct the Pr
1
assumes three trees would be removed for a conservative evaluati
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RF
EGULATORY RAMEWORK
SMC
AN ATEO OUNTY
Comprehensive Airport Land Use Compatibility Plan for the Enviro
International Airport (ALUP)
The South San Francisco General Plan refers to the ALUP maximum height limits for structures
within the San Francisco International Airport impact zone and Figure 2-3 Special Area Height
Limitations (SSF GP, 1999, p. 35). The Project site is not within an airport-related height
restriction zone, and therefore is governed by the maximum height of 28 feet shown in
Aesthetics Table 1, above.
CSSF
ITY OF OUTH AN RANCISCO
Design Review Board
As identified in Chapter 1, Section 1.5.1, the Project is required by law to undergo review by
the Citys Design Review Board (DRB). Changes in design may be identified by DRB and may
also be identified by the Planning Commission. Design review regulates signage, site layout,
architecture, urban design, and lighting.
The Project underwent design review on August 18, 2015 (DR15-0033). DRB indicated
acceptance of the Project design and notes that Applicant may wa
landscaping and the use of gray water for irrigation (letter from Adena Friedman, Senior
Planner, to Applicant, September 9, 2015).
General Plan
Scenic vistas and corridors are identified in the South San Francisco General Plan. The Project site
is not identified as a site that is visible from at least one viewpoint and is not identified as a
viewpoint site (Figure 2-4 Viewshed, SSF GP, 1999, p. 36).
I
MPACTS
a) Scenic Vistas
Significance Criteria: For the purpose of assessing impacts of a proposed project on scenic vistas,
the threshold of significance is exceeded when a project would result in the obstruction of a
designated public vista, or in the placement of an arguably offensive or negat-appearing
project within such a vista. Any clear conflict with a general plan policy or other adopted
planning policy regarding scenic vistas would also be consideredicant adverse
environmental impact.
The view of Sign Hill is on the south-sloping portion of the mountain, not the north-facing
portion where the Project is located. The ridge of Sign Hill reaches approximately 600 feet in
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elevation. The Sterling Terrace subdivision ranges in elevation from approximately 200 to 450
feet. The historic portion of Sign Hill is not visible from the northern and western slopes of Sign
Hill. The Project would not block views of the historic sign.
The Project is not located within a formally designated public vista, nor would it result in th
obstruction of a formally designated public vista. The Project is not identified as a viewpoint
parcel or as one containing view value. The Project would not conflict with an adopted planning
policy regarding scenic vistas. The Project would have a less than significant impact with
respect to scenic vistas.
b) Scenic Resources and Scenic Routes
Significance Criteria: For the purposes of assessing impacts of the Project on scenic rs, the
threshold of significance is exceeded by any Project-related action that would substantially
damage scenic resources (i.e., trees, rock outcroppings, and his
local] scenic highway).
There are no state or local scenic highways within the Project area. Additionally, there are no
rock outcroppings, heritage, or historic trees or buildings on the Project site. Therefore, there are
no scenic resources or scenic route impacts associated with the Project, as defined by the
significance criteria. The Project would have no impact on scenic resources.
c) Visual Character
Significance Criteria: The Project would have a significant environmental impact if it
substantially degrade the existing visual character or quality of the site and its surroundings.
The Project would be located in an area which is single-family residential. As noted above,
th
adjacent properties include a single-family mid-20Century residence on the northeast, privately
owned open space on the southeast and an undeveloped property on the southwest that once
contained a water tower. Houses in the Sterling Terrace subdivision are predominately one-story
over a garage on sloping lots that typically result in more mass
lots.
Multi-family housing complexes are adjacent to the Project area(see Aesthetics Figure 1).One
of the multi-family complexes dominates the streetscape in the Project area, rising approximately
50 feet above the elevation of Larch Avenue.
The Project would be a two-story structure over a partially subterranean garagein keeping with
the predominate structural pattern of the Sterling Terrace neighborhood The maximum height
would be 27 feet 9.5 inches, under the permitted 28 foot maximum. Massing would be reduced
on the second story. The second story consisting of 733 square feet would be percent
than the ground floor, which would consist of 1,224 square feet. The Project would be built on
the portion of the lot that is the lowest in elevation, similar to other single-family structures in
the neighborhood. The Project would provide a transition from t mass of the back of the
multi-family structure to the south and the single-family structures within the subdivision. The
Project would have no impact on visual character or the quality of the site or its
surroundings.
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d) Light or Glare
Significance Criteria:Project related creation of any new source of substantial light
would adversely affect day ornighttime views in the area would be regarded as a significant
environmental impact.
The Projectsiteis a built-out residential neighborhood on one single vacant lot. The addition
light associated with one single-family detached residence is de minimus. Exterior lighting for
doorways, pathways, etc., would be downcast and task-oriented as required by the South San
Francisco Municipal Code (SSFMC)and described in Chapter 1 Introduction. As required to
be constructed per law, the Project would not substantially increase the light in the area and
would not produce glare. The Project would have a less than significant impact on light
and glare impacts.
Aesthetics Finding: The Project would not have an impact on the aesthetics or scenic qual
on the site or in the area. The Project is not located within a formally designated public vista, n
would it result in the obstruction of a formally designated publ
The Project is not identified as a viewpoint parcel or as one co (SSF GP,
1999). The Project would not conflict with an adopted planning policy regarding scen
The Project would be built on the portion of the lot that is the
other single-family structures in the neighborhood.
Massing would be reduced on the second story. The second story, consisting of 733 square feet,
would be 40 percent smaller than the ground floor, consisting of 1,224 square feet. The Project
would be built on the portion of the lot that is the lowest in engle-
family structures in the neighborhood. The Project would provide a transition from the mass of
the back of the multi-family structure to the south and the single-family structures within the
subdivision.
There would be no individual or cumulative impacts with respect to aesthetic, visual quality or
light and glare associated with the Project.
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3.2AFR
GRICULTURAL AND OREST ESOURCES
Potentially Less Than Less Than
Significant Significant SignificantNo
with
Impact Impact Impact
Mitigation
Would the Project:
II. AGRICULTURE RESOURCES: In determining
whether impacts to agricultural resources are significant
environmental effects, lead agencies may refer to the
California Agricultural Land Evaluation and Site
Assessment Model (1997) prepared by the California
Dept. of Conservation as an optional model to use in
assessing impacts on agriculture and farmland. In
determining whether impacts to forest resources,
including timberland, are significant environmental
effects, lead agencies may refer to the information
compiled by the California Department of Forestry and
Fire Protection regarding the states inventory of forest
land, including the Forest and Range Assessment
Project and the Forest Legacy Assessment Project; and
the forest carbon measurement methodology provided
in the Forest Protocols adopted by the California Air
Resources Board.
X
a) Convert Prime Farmland, Unique Farmland, or
Farmland of Statewide Importance (Farmland), as
shown on the maps prepared pursuant to the
Farmland Mapping and Monitoring Program of
the California Resources Agency, to non-
agricultural use?
X
b) Conflict with existing zoning for agricultural use,
or a Williamson Act contract?
X
c) Conflict with existing zoning for, or cause
rezoning of, forest land (as defined in the Public
Resources Code section 12220(g)), timberland (as
defined by Public Resources Code section 4526)
or timberland zoned Timberland Production (as
defined by Government Code section51104(g))?
X
d) Result in the loss of forest land or conversion of
forest land to non-forest use?
X
e) Involve other changes in the existing environment
which, due to their location or nature, could result
in conversion of Farmland, to non-agricultural use
or conversion of forest land to non-forest use?
S
ETTING
Vegetation on the Project site consists of introduced grasses an
have spread from nearby garden landscaping including grasses and weeds. Three trees are on the
site: a pine tree (Pinus sp.) about 11 inches diameter at breast height (dbh), a Monterey Cypress
(Cupressus macrocarpa) about 24 inches dbh and a deodar cedar (Cedrus deodara), about 18 inches
dbh (Michael Marangio, Biological Resources Assessment prepared for Allison Knapp Wollasulting,
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Proposed Residence, 901 Larch Avenue, South San Francisco, Calif. November 10, 2015). The
three trees would be removed.
I
MPACTS
a, b and e) Farmland Impacts
Significance Criteria: The Project would have a significant environmental impact if it would result
in the conversion of farmland to non-agricultural use, conflict with current zoning for
agricultural use or the provisions of a current Williamson Act c
environmental changes that could result in the conversion of farmland currently in agricultural
uses to non-agricultural uses.
The Project site contains no farmland, is not zoned agricultural or adjacent thereto, and as such
would not involve the conversion of Farmland, Unique Farmland, oide
Importance (Farmland), as shown on the maps prepared pursuant to
Monitoring Program of the California Resources Agency. The Proj
Act Contract. The Project site is not nearby or adjacent to any agricultural use and as
such would have no impact to farmland.
c, d and e) Forest Land Impacts
Significance Criteria: A significant impact would result from a conflict with existing zoning for, or
cause rezoning of, forest land (as defined in the Public Resources Code section 12220(g)),
timberland (as defined in Public Resources Code section 4526) or timberland zoned Timberla
Production (as defined by Government Code section 51104 (g)) or result in the loss of forest
land or conversion of forest land to non-forest use.
The site is not zoned for timberland production or in use as such, or in proximity to such a use.
Removal of three small trees to construct a single-family house would not cause rezoning of
forest land (as defined in the Public Resources Code section 12220(g)), timberland (as defined by
Public Resources Code section 4526) or timberland zoned Timberla
by Government Code section51104(g)).The Project is not nearby or adjacent to
timberland or forest lands and would have no impact on timberland production or
resources or forest lands.
Agriculture and Timber Resources Finding: The Project would not adversely affect any
existing agricultural operations as none exist on the site. The Project would not impact
agricultural resources individually or cumulatively and does not contain any Farmland, Unique
Farmland, Farmland of Statewide Importance (Farmland) nor land in a Williamson Act
Contract. The site is not zoned for timberland production or in use as such, and would not cause
rezoning of forest land (as defined in the Public Resources Code
(as defined by Public Resources Code section 4526) or timberland
Production (as defined by Government Code section 51104(g)).
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3.3AQ
IR UALITY
PotentiallyLess ThanLess Than
SignificantSignificant Significant No
Impact with Impact Impact
Would the Project: Mitigation
Where available, the significance criteria
established by the applicable air quality
management or air pollution control district may
be relied upon to make the following
determinations.
a) Conflict with or obstruct implementation of
X
the applicable air quality plan?
b) Violate any air quality standard or contribute X
substantially to an existing or projected air quality
violation?
X
c) 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)?
d) Expose sensitive receptors to substantial X
pollutant concentrations?
e) Create objectionable odors affecting a X
substantial number of people?
S
ETTING
M
ETHODOLOGY
This air quality analysis was performed using methodologies and
within the Bay Area Air Quality Management District (BAAQMD) CEQA Air Quality Guidelines
2
(dated June 2010, updated in May 2011, and revised in May 2012).This section describes
regional meteorology, existing air quality conditions, air quali
pollutant construction and operational impacts.
The Air Districts June 2010 adopted thresholds of significance n March 5, 2012, the Alameda
2
County Superior Court issued a judgment finding that the Air Dis
thresholds. The court found that the adoption of the thresholds was a projecir District to
examine whether the thresholds would have a significant impact obefore recommending their
use. The court did not determine whether the thresholds are or are no and thus valid on the merits.
The court issued a writ of mandate ordering the District to set e Air
District had complied with CEQA. The courts order permits the Air District to develop and dissem
Guidelines, as long as they do not implement the thresholds of significance. Although the BAAQMDs adoption of significance
thresholds for air quality analysis has been subject to judicial
BAAQMDs Revised Draft Options and Justification Report (October 2009), p
BAAQMD recommended thresholds. Therefore, the City of South San Francisco has determined the BA
thresholds are appropriate for use in this analysis. Californias First District Court of Appeal issued a decision in California Building
Industry Association v. Bay Area Air Quality Management District (Case No. A134335, August 13, 2013), laying the groundwork for t
reinstatement of the BAAQMDs air quality thresholds, including for greenhouse gas emi
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Analyzed air quality pollutants include: carbon monoxide (CO), r
(ROG), nitrogen dioxide (NO), particulate matter equal to or less than 10 micrometers (coar
2
particulates or PM10), and particulate matter equal to or less t
particulates or PM2.5). Diesel particulate matter (DPM) is also with regard to health
impacts. Greenhouse gas (GHG) emissions are addressed within Section 3.4.
The Air Quality Conditions of Approval identified in Chapter 1 Legislative Framework, are
required to be implemented as part of the Project pursuant to th of South San Franciscos
project review and building permit process. The conditions address dust control, combustion
exhaust control, control of toxic air contaminants, architectura
control, and hearth emission control.
RM
EGIONAL ETEOROLOGY
Air quality is affected by the rate, amount, and location of pol
meteorological conditions that influence pollutant movement and
conditions, including wind speed, wind direction, stability, and air temperature, in combination
with local surface topography (i.e., geographic features such as
Francisco Bay), determine the effect of air pollutant emissions
The peninsula region of the Bay Area Air Basin (Bay Area) extends from the area northwest of
San Jose to the Golden Gate. The Santa Cruz Mountains extend up
with elevations exceeding 2,000 feet at the south end, and gradun of
500 feet in South San Francisco, where it terminates. San Franci
peninsula and because most of the topography of San Francisco is
3
layer is able to flow across most of the city, making its climate relatively cool and windy.
However, the area of South San Francisco and San Francisco Inter
experience lower winds and a greater frequency of calm winds (ap
year), especially during the nighttime and cooler season, due to sheltering effect of terrain to the
west.
Meteorological data collected at the SFO, which is approximately2.5 miles south of the Project
site, are representative of general Project conditions. Average maximum and minimum winter
(i.e., January) temperatures at SFO are 56 and 42 degrees Fahrenhei
average summer (i.e., July) maximum and minimum temperatures areºFand 54 ºF,
4
respectively. Precipitation at SFO averages approximately 20 inc
Annual average wind speeds range from five to 10 miles per hour (mp
peninsula. The east side of the mountains has a westerly wind pa
by local topographic features. That is, a few hundred feet rise will induce flow
around that feature instead of over it during stable atmospheric
wind pattern by as much as 90 degrees over short distances. On m
pressure gradient, areas on the east side of the peninsula often experience eastern flow in the
surface layer, induced by upslope flow on the east-facing slopes and by the bay breeze. The bay
Bay Area Air Quality Management District. October 4, 2010, Bay A Peninsula
3
http://www.baaqmd.gov/Divisions/Communications-and-Outreach/Air-Quality-in-the-Bay-Area/Bay-Area-
Climatology/Subregions/Peninsula.aspx.
Western Regional Climate Center, Local Climate Data Summaries for San Francisco International Air.
4
http://www.wrcc.dri.edu/cgi-bin/clilcd.pl?ca23234.
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breeze is rarely seen in the afternoon because the stronger sea
5
pattern.
RC
EGULATORY ONTEXT
The Project site is located within the San Francisco Bay Area Ai,under the jurisdiction of
the BAAQMD. The BAAQMD monitors and regulates air quality pursua
Air Act, as amended, and the California Clean Air Act. The BAAQMdopts and enforces
controls on stationary sources of air pollutants through its per
Other BAAQMD responsibilities include monitoring air quality, pr
and responding to citizen air quality complaints. The BAAQMD has also published CEQA Air
Quality Guidelines, to assist lead agencies in evaluating air quality impacts of p
proposed in the Bay Area.
RAQ
EGIONAL IR UALITY MONITORING
The BAAQMD operates a regional monitoring network for ambient concentrations of six
criteria pollutants. Currently, the criteria pollutants of most
and particulate matter. The monitoring station closest to the Pr
Arkansas Street. This air quality monitoring station monitors levels of ozone, particulate matter
in the form of PM10, PM2.5, CO, NO, and sulfur dioxide (SO).
22
Air Quality Table 1 summarizes the most recent three years of data published by the
Air Resources Board (CARB) for the San Francisco, Arkansas Street air monitoring station,
which is approximately eight miles to the north of the Project s-hour PM10
standard and federal 24-hour PM2.5standard were each exceeded once in 2012. The federal 1-
hour NOstandard was exceeded once in 2012. The federal 24-hour PM2.5standard was
2
exceeded twice in 2013. No exceedances of the air quality standa
other State or federal air quality standards were exceeded durin
The Bay Area is considered a nonattainment area for ground-level ozone and PM2.5 under both
the Federal Clean Air Act and the California Clean Air Act. The
nonattainment for PM10 under the California Clean Air Act, but nan Air Act.
The area has attained both State and National Ambient Air Qualit, and
2
NO. As part of an effort to attain and maintain ambient air qualit
2
particulate matter, the BAAQMD has established thresholds of significance for these air
pollutants and their precursors. These thresholds are for ozone
nitrogen oxides [NOx]), PM10 and PM2.5, and apply to both constr
operational period impacts.
Bay Area Air Quality Management District. October 4, 2010, Bay Area Climatology Peninsula
5
http://www.baaqmd.gov/Divisions/Communications-and-Outreach/Air-Quality-in-the-Bay-Area/Bay-Area-
Climatology/Subregions/Peninsula.aspx.
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AQT1
IR UALITY ABLE
AQDS
IR UALITY ATA UMMARY
SF,AS,SF,CA20122014
AN RANCISCO RKANSAS TREETAN RANCISCO
PollutantStandardDays Standard Exceeded
2012 2013 2014
OzoneState 1Hour0 0 0
OzoneFederal 8Hour0 0 0
OzoneState 8Hour0 0 0
PM10Federal 24Hour000
PM10 State 24Hour 1 0 0
PM2.5 Federal 24Hour 1 2 0
Carbon Monoxide State/Federal 8Hour0 0 0
Nitrogen DioxideState 1Hour000
Nitrogen Dioxide Federal 1Hour1 0 0
Sulfur Dioxide State 24-Hour 0 0 0
Source: Bay Area Air Quality Management District, Annual Bay Area Air Quality Summaries,
http://www.baaqmd.gov/Divisions/Communications-and-Outreach/Air-Quality-in-the-Bay-Area/Air-Quality-Summaries.aspx,
2015.
I
MPACTS
a)Conflicts with the Current Air Quality Plan
Significance Criteria: Any project that would not support the goals of the 2010 Bay A
Plan (Bay Area CAP) would not be considered consistent with the 010 Bay Area CAP.
On September 15, 2010, the BAAQMD adopted the 2010 Bay Area CAP.
CAP updates the Bay Area 2005 Ozone Strategy in accordance with
California Clean Air Act (CCAA) to implement all feasible measurto reduce ozone; provide a
control strategy to reduce ozone, particulate matter, air toxics
integrated plan; and establish emission control measures to be a
2010 through 2012 timeframe. The primary goals of the 2010 Bay Area CAP are to:
Attain air quality standards;
o
Reduce population exposure and protect public health in the Bay
o
Reduce GHG emissions and protect the climate.
o
The recommended measure for determining Project support of thesegoals is consistency with
BAAQMD-approved CEQA thresholds of significance. As presented in the subsequent impact
discussions, the Project with Air Quality Conditions of Approval, identified in Chapter 1,
Legislative Framework which are required by law would not exceed the BAAQMD
significance thresholds; therefore, the Project would support th
There would be a less-than-significant impact associated with, conflicting with, or
obstructing implementation of the applicable air quality plan.
b and c) Violation of Standards and a Cumulatively Considerable
Significance Criteria: The Project would have a significant environmental impact if i
BAAQMDs construction and/or operational mass emission thresholdfor exhaust emissions
and/or if appropriate air pollutant control measures are not imp
thresholds are designated to assess whether the Project would po
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standard or contribute substantially to an existing or projected air quality violation. Projects with
impacts less than the significance thresholds with implementatio
presumed to not violate air quality standards. The BAAQMD CEQA Air Quality Guidelines
recommend that cumulative air quality effects from criteria air pollutants also be a
comparison to the mass daily and annual thresholds. These thresh
identify a cumulatively considerable contribution to a significat. The
thresholds of significance applied to assess project-level air quality impacts are:
Average daily construction exhaust emissions of 54 pounds per da
o
or PM2.5 or 82 pounds per day of PM10; and
Average daily operation emissions of 54 pounds per day of ROG, NOx, or PM2.5 or
o
82 pounds per day of PM10; or result in maximum annual emissions
year of ROG, NOx, or PM2.5 or 15 tons per year of PM10
Construction Related Impacts
The Project includes the construction of a two-story, single-family residence with a two-car
garage (totaling approximately 2,500 square feet) on a 7,500-square-foot lot. Site preparation
would include the removal of vegetation and grading would includ
yards of soil export. Soil export was assumed to require approximately 50 haul truck trips (based
on haul truck capacity of 8 cubic yards) to Baylands Soil Proces
from the Project site. Construction activities would require app to 44 weeks to
complete. Construction, as permitted by City ordinance, could take place Monday through
6
Friday from 8AM to 8 PM with some work on Saturdays and Sundays.
Project construction would generate short-term emissions of criteria pollutants, including
fugitive dust and equipment exhaust emissions. The BAAQMD CEQA Air Quality Guidelines
recommend quantification of construction-related exhaust emissions and comparison of those
emissions to significance thresholds. Therefore, this analysis i
construction emissions and comparison of the emissions to the BAAQM
significance thresholds. The CalEEMod (California Emissions Esti
2013.2.2) was used to quantify Project construction emissions of
Appendix A for CalEEMod output data).
Air Quality Table 2 provides the estimated short-term construction emissions that would be
associated with the Project and compares those emissions to the
construction exhaust emissions. As the construction phases (site preparation, grading, building
construction, paving, and coatings) are sequential, the average
emissions were compared to the BAAQMD significance thresholds. A-related
emissions would be well below the BAAQMD significance thresholds.
This analysis assumes a worst case analysis that the Project wou
6
permitted by ordinance. Construction activities would likely beht-nine hours weekdays.
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AQT2
IR UALITY ABLE
PCCPE
ROJECT ONSTRUCTION RITERIA OLLUTANT MISSIONS
()
POUNDS PER DAY
ROGNOxPM10PM2.5CO
Project Construction<1.09.20.20.27.1
Significance Thresholds54548254---
Significant Impact?No No NoNo No
Source: CalEEMod Version 2013.2.2
Notes: Refer to Appendix A for CalEEMod output data. Values reflect rounding.
Construction activities, particularly during site preparation an
generate fugitive dust in the form of PM10 and PM2.5. Sources of fugitive dust would include
disturbed soils at the construction site. Unless properly contro
would deposit mud on local streets, which could be an additional
dries. Fugitive dust emissions would vary from day to day, depen
magnitude of construction activity and local meteorological cond
would also depend on soil moisture, silt content of soil, wind s the amount of
equipment operating. Larger dust particles would settle near the
would be dispersed over greater distances from the construction
receptors could be adversely affected by dust generated during construction activities.
BAAQMDs CEQA Air Quality Guidelines provides a number of Construction Mitigation Measures
(related to fugitive dust and combustion exhaust emissions) for
required of the Project through the Citys standard review and approval. The Applicant would
also use low ROG coatings and finishes, as required by the BAAQM
7
through the City Building Division. All construction emissions would be below the BAAQMD
significance thresholds with the implementation of these measures that are required
the Air Quality Conditions of Approval. Project impacts that would be associated with
construction related fugitive dust and combustion exhaust emissi
significant with implementation of the standard Air Quality Conditions of Approvalas
required by law, identified in Chapter 1, Legislative Framework.
Operational Impacts
The CalEEMod was also used to estimate emissions that would be a
such as space heating, water heating, and landscape maintenance Appendix A for
CalEEMod output data). Operational emissions associated with mot
were also estimated. As part of the Project design, fireplaces, osed for installation in
8
residential units, would use natural gas or propane only.
Emissions of volatile organic compounds (VOC as ROG) due to the
7
contained in Regulation 8: Organic Compounds, Rule 3: Architectu-3). Rule 8-3 was recently revised to
include more stringent VOC limit requirements. The revised VOC ary
1, 2011, are projected to result in a 32 percent reduction of VOectural coating
applications. The applicant shall use paints and solvents with a150
grams per liter or less for exterior surfaces.
On July 9, 2008, the BAAQMD adopted Regulation 6, Rule 3: Wood-Burning Devices to reduce the harmful emissions that
8
come from wood smoke. The Rule requires cleaner-burning (e.g., natural gas) USEPA-certified stoves and inserts in new housing
construction.
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Estimated operational daily and annual emissions that would be a
presented in Air Quality Tables 3 and 4 and are compared to BAAQMDs thresholds of
significance. The estimated operational emissions that would be associated wit
operations would be below the BAAQMDs significance thresholds.
impacts that would be associated with operational emissions woul
significant.
AQT3
IR UALITY ABLE
PDOCPE
ROJECT AILY PERATIONAL RITERIA OLLUTANT MISSIONS
()
POUNDS PER DAY
ROGNOxPMPMCO
102.5
Project Operation 0.1 0.1<0.1 <0.10.4
Significance Thresholds 54 54 82 54 ---
Significant Impact?No No No NoNo
Source: CalEEMod Version 2013.2.2
Notes: Refer to Appendix A for CalEEMod output data. Values reflect rounding.
AQT4
IR UALITY ABLE
PAOCPE
ROJECT NNUAL PERATIONAL RITERIA OLLUTANT MISSIONS
()
TONS PER YEAR
ROGNOxPM PM CO
102.5
Project Operation <0.1 <0.1<0.01 <0.01 <0.1
Significance Thresholds 10 10 15 10 ---
Significant Impact?No No No No No
Source: CalEEMod Version 2013.2.2
Notes: Refer to Appendix A for CalEEMod output data. Values reflect rounding.
Operational CO Impacts
The BAAQMD has identified preliminary screening criteria for determining whether CO
emissions would be exceeded. The screening criteria provide a co
whether the implementation of the Project would result in CO emi
significant. This methodology includes the following:
1.Project is consistent with an applicable congestion management p
established by thecounty congestion management agency for designated roads or
highways, regionaltransportation plan, and local congestion management agency
plans.
2.The Project traffic would increase traffic volumes at affected i
more than 44,000 vehicles per day.
3.The Project traffic would increase traffic volumes at affected i
more than 24,000 vehicles per day where vertical and/or horizontal mixing is
substantially limited (e.g., tunnel, parking garage, bridge unde
urban street canyon, below-grade roadway).
The Project traffic would not cause the daily traffic volumes to
shown in items 1 through 3 based on the circulation infrastructure and
volumes. A single-family home typically generates nine vehicle trips per day (Institute of Traffic
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Engineers). Impacts that would be associated with long-term operationalCO exhaust
emissions would be less than significant.
Cumulative Impacts
The BAAQMD CEQA Air Quality Guidelines recommend that cumulative air quality effects from
criteria air pollutants also be addressed by comparison to the B
significance thresholds. Project-related emissions would be below the significance thresholds
with implementation of the Air Quality Conditions of Approval, identified in Chapter 1, as
required by law (see Air Quality Tables 2 through 4). Therefore, the Project would not be
cumulatively considerable and cumulative impacts would be less t
d) Impacts to Sensitive Receptors
Significance Criteria: The significance of impact to sensitive receptors is dependent
of contracting cancer from exposure to toxic air contaminants (TACs) such as DPM or
having adverse health effects from exposure to non-carcinogenic TACs. A project is considered
to be significant if the incremental cancer risk at a receptor e
For cumulative analysis of cancer risk, BAAQMD recommends that the ri
within a 1,000 foot radius of the Projects impact area (i.e., c
residence located to the northwest of the Project) be assessed ato a cumulative
increased risk threshold of 100 in one million. The non-cancer hazard index significance
threshold of 1.0 is defined in the BAAQMD CEQA Air Quality Guidelines. For cumulative
analysis of non-cancer hazard index, BAAQMD requires that the hazards from all sources within
a 1,000 foot radius of the Projects impact area be assessed and
index threshold of 10.
Emissions of PM2.5are associated with health risks. The BAAQMD has established a s
significance threshold for PM2.5to protect public health. For individual projects, the BAAQMD
significant threshold for PM2.5 impacts is an average annual inc
3
cubic meter (µg/m). For cumulative analysis, BAAQMD recommends that the PM2.5
concentrations from all sources within a 1,000 foot radius of the Proj
3
assessed and compared to a cumulative threshold of an average an.
People within the general population that are more susceptible tf air pollution
include children, elderly, and those that suffer from certain il
schools, convalescent homes, and hospitals are considered to be
pollution. Residential areas are also considered sensitive to poor air quality because people
usually stay home for extended periods of time, which results in greater exposure to localized air
pollutants.
The Project site is a vacant lot in an existing residential subd
located to the north, northeast,and east of the Project site, while multifamily residences are
located to the west and southwest. Sign Hill Park is located to Hillside
Christian Academy is at 1415 on the south side of Hillside Boulevard and Mills Montessori
School at 1400 on the north side of Hillside Boulevard, approximately 700 feet from the Project
site. Hillside Christian Academy is approximately 350 feet northwes. Hillside
School is approximately 1,000 feet north of the Project site, and was closed in 2005. The nearest
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sensitive receptor is the adjacent property to the east of ProjeHillside ChristianAcademy
is located approximately 300 feet northwest of the site.
Construction activities would entailthe use of diesel equipment that generate emissions of DPM,
which the CARB has categorized as a human carcinogen. Typically,
based on a lifetime exposure period of 70 years. Because exhaust emissions associated with
construction activities of the Project would be very low and short-term in nature (approximately
32 weeks), it is anticipated that exposure to construction-related DPM would not result in an
elevated health risk. The health risk and hazard impacts to sensitive receptors from
Project construction would be less than significant with impleme
Quality Conditions of Approval, as required by law.
BAAQMD has developed a geo-referenced database of permitted emissions sources throughout
the San Francisco Bay Area, and has developed the Stationary Source Risk & Hazard Analysis Tool
(dated May 2012) for estimating cumulative health risks from per
source is located within 1,000 feet of the Project.
BAAQMD has also developed a geo-referenced database of roadways throughout the San
Francisco Bay Area and has developed the Highway Screening Analysis Tool (dated May 2011) for
estimating cumulative health risks from roadways. US 101 is incl
this roadway is greater than 1,000 feet from the Project site. BAAQMD CEQA Air Quality
Guidelines also require the inclusion of surface streets within 1,000 feet
average daily traffic (AADT) of 10,000 or greater. Upon review oide
9
Boulevard (15,600 AADT) meets the criteria. The cumulative cancer risk for the proposed
receptor due to Hillside Boulevard is 0.5 per million persons, w
per million persons. The cumulative PM2.5 concentration for the osed receptor due to
33
Hillside Boulevard is 0.02 µg/m; well below the threshold of 0.8 µg/m.
As the cumulative impacts would be well below the BAAQMD significance thresholds
and the Project would not result in increased health impacts exctlevel
-
thresholds, the Project would also not result in a cumulatively
to localized health risk and hazard impacts. Therefore, the cumu
would be less than significant.
e) Odor Impacts
Significance Criteria: The BAAQMDs significance criteria for odors are more subjective a
based on the number of odor complaints generated by a project. G
considers any project with the potential to frequently expose me
objectionable odors to cause a significant impact. Projects that would site a
new receptor farther than the applicable BAAQMD-established screening distances from an
existing receptor or odor source, respectively, would not likelyficant odor impact.
An odor source with five more confirmed complaints per year aver
considered to have a significant impact on receptors within the
Typical odor sources of concern include wastewater treatment plants, sanitary landfills, transfer
stations, composting facilities, petroleum refineries, asphalt b
Bay Area Air Quality Management District County Surface Street Screening Tables, May 2011 and CEHTP Traffic
9
Linkage Service Demonstration, http://www.ehib.org/traffic_tool.jsp.
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manufacturing facilities, fiberglass manufacturing facilities, a
and coffee roasting facilities. Diesel-fueled construction equipment would generate some odors
associated with diesel exhaust. Diesel emissions typically dissipate quickly and would be unlikely
to affect a substantial number of peopleand the other types of odors are not present in the
Project area. Therefore, odor impacts associated with construction and operati
Project would be less than significant.
Air Quality Finding: Project impacts that would be associated with construction-related
fugitive dust and combustion exhaust emissions would be less than significant with
implementation of the Citysstandard Air Quality Conditions of Approval, identified in Chapter
1, Legislative Framework.
The Project traffic would not cause the daily traffic volumes to
based on the circulation infrastructure and the projected traffi-family house
typically generates nine vehicle trips per day. Therefore, impac
long-term operational CO exhaust emissions would be less than significant.
Odor impacts associated with construction and operation of the P
significant.
There would be a less-than-significant impact associated with, conflicting with, or obstruc
implementation of the applicable air quality plan.
The health risk and hazard impacts to sensitive receptors from P
less than significant with implementation of the Citysstandard Air Quality Conditions of
Approval, as required by law.
The cumulative impacts would well below the BAAQMD significance thresholds and
the Project would not result in increased health impacts exceedilevel
-
thresholds, the Project would also not result in a cumulatively
to localized health risk and hazard impacts. Therefore, the cumulative health impacts
would be less than significant.
3.4GGE
REENHOUSE AS MISSIONS
Potentially Less Than Less Than
SignificantSignificant Significant No
with
Impact Impact Impact
Mitigation
Would the Project:
X
a) Generate greenhouse gas emissions, either
directly or indirectly, that may have a
significant impact on the environment?
X
b) Conflict with an applicable plan, policy or
regulation adopted for the purpose of
reducing the emissions of greenhouse gases?
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S
ETTING
Gases that trap heat in the atmosphere are referred to as greenh
capture heat radiated from the sun as it is reflected back into
greenhouse does. The accumulation of GHGs has been implicated as the driving force for global
climate change. The primary GHGs are carbon dioxide (CO), methane (CH), nitrous oxide
24
(NO), ozone, and water vapor.
2
While the presence of the primary GHGs in the atmosphere are nat, CH,
24
and NO are also emitted from human activities, accelerating the rate
2
occur within earths atmosphere. Emissions of CO are largely by-products of fossil fuel
2
combustion, whereas methane results from off-gassing associated with agricultural practices and
landfills. Other GHGs include hydrofluorocarbons, perfluorocarbo
and are generated in certain industrial processes. GHG are typic-
10
equivalent measures (COe).
2
There is international scientific consensus that human-caused increases in GHGs have and will
continue to contribute to global warming. Potential global warmi
include, but are not limited to, loss in snow pack, sea level rit days per year,
more high ozone days, more large forest fires, and more drought
likely to include a global rise in sea level, impacts to agricul
11
changes in habitat and biodiversity.
In 2012, the United States emitted about 6.526 billion tons of COe or about 21 tons per year
2
per person. Of the four major sectors nationwide - residential, commercial, industrial, and
transportation electrical generation accounts for the highest fraction of GHG emissions
(approximately 32 percent); these emissions are entirely generat
combustion. United States GHG emissions decreased by 3.4 percent from 2011 to 2012. Recent
trends can be attributed to multiple factors including reduced emissions from electricity
generation, improvements in fuel efficiency in vehicles with red
year-to-year changes in the prevailing weather. GHG emissions in 2012 we
12
2005 levels.
Californias gross emissions of GHG decreased by 1.6 percent from 466.3 million metric to
COe in 2000 to 458.7 million metric tons in 2012, with a maximum o
2
in 2004. During the same period, Californias population grew by
million people. As a result, Californias per capita GHG emissio
13
the last 12 years from 13.7 in 2000 to 12.1 million metric tons e per person in 2012.
2
California has one of the lowest per capita GHG emission rates ithe country, due to the
success of its energy efficiency and renewable energy programs a
lowered the states GHG emissions rate of growth by more than ha
Because of the differential heat absorption potential of variousare frequently measured in carbon
10
dioxide-equivalents, which present a weighted average based on each gas
2006 Final Climate Action Team Report to the Governor and Legisl
11
http://www.climatechange.ca.gov/climate_action_team/reports/2006-04-03_FINAL_CAT_REPORT.PDF
USEPA, Inventory of U.S. Greenhouse Gas Emissions and Sinks: 19902012, April 2014,
12
http://www.epa.gov/climatechange/ghgemissions/usinventoryreport.
CARB, 2014 Edition California Greenhouse Gas Emission Inventory 2000 2012, May, 2014,
13
http://www.arb.ca.gov/cc/inventory/pubs/reports/ghg_inventory_00-12_report.pdf
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otherwise. Another factor that has reduced Californias fuel use and GHG emissions is its mild
climate compared to that of many other states.
The transportation sector remains the largest source of GHG emis
36 percent of Californias GHG emission inventory. Contributionsom the transportation
sector include emissions from on-road and off-road vehicles, aviation, rail and water-borne
vehicles, and some other minor sources. Transportation-related GHG emissions have dropped
12 percent since reaching a maximum in 2007. In 2012, emissions from the on-road category
14
decreased by 0.5 percent from the previous year.
The California Environmental Protection Agency Climate Action Te
composition of gross GHG emissions in California in 2002 (exprese) were
2
15
as follows:
CO accounted for 83.3 percent;
o
2
CH accounted for 6.4 percent;
o
4
NO accounted for 6.8 percent; and
o
2
Fluorinated gases (HFCs, PFC, and SF) accounted for 3.5 percent.
o
6
In the San Francisco Bay Area, the transportation sector and indl/commercial sector
represent the largest sources of GHG emissions, accounting for 3
Areas 95.8 million tons of COe in 2007. Electricity/co-generation sources account for about
2
15.9 percent of the Bay Areas GHG emissions, followed by residential fuel usage at about 7.1
percent. Off-road equipment and agricultural/farming sources currently accoun
approximately three percent and 1.2 percent of the total Bay Are
16
respectively.
The City of South San Francisco published a community-wide GHG emissions inventory for the
17
year of 2005. The inventory attributed the two largest sources of GHG emission
transportation (34.9 percent) and to commercial/industrial (34.7
Francisco emittedapproximately 560,414 metric tons of COe in 2005.
2
RF
EGULATORY RAMEWORK
California has increased focus on the need to control GHG emissi
and to prepare for adapting to the effects of global climate charizes
prominent regulations and initiatives in California that address
Senate Bill 1771 (Sher, Chapter 1018, Statutes of 2000), signed on September 30, 2000,
o
established the creation of the California Climate Action Regist (CCAR) as a non-
profit organization. SB 1771 required the California Energy Comm
update the state GHG emissions inventory and to develop data and
CARB, 2014 Edition California Greenhouse Gas Emission Inventory 2000 2012, May, 2014,
14
http://www.arb.ca.gov/cc/inventory/pubs/reports/ghg_inventory_00-12_report.pdf
California Environmental Protection Agency, Climate Action Team Report to Governor Schwarzenegger and the Ca,
15
December 2010, http://www.energy.ca.gov/2010publications/CAT-1000-2010-005/CAT-1000-2010-005.PDF
BAAQMD, Source Inventory of Bay Area Greenhouse Gas Emissions, F
16
http://www.baaqmd.gov/~/media/Files/Planning%20and%20Research/Em
shx?la=en
City of South San Francisco, 2005 Community-wide Greenhouse Gas Emissions Inventory, January 2011. Available
17
http://ca-southsanfrancisco.civicplus.com/DocumentCenter/Home/View/2472.
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climate change and to provide certain entities and interest groups with information
on the costs, technical feasibility, and demonstrated effectiven
reducing GHGs from in-state sources. SB 1771 required the inventory to be updated
every five years.
Senate Bill 527 (Sher, Chapter 769, Statutes of 2001), which amended SB 1771, was
o
signed on October 11, 2001. The bill revised the functions and d
and required the CCAR, in coordination with the CEC to adopt thi-party
verification metrics, develop GHG emissions protocols and qualif-party
organizations to provide technical assistance and certification of emis
and inventories.
Assembly Bill 32 (Núñez, Chapter 488, Statutes of 2006), the California Global Warming
o
Solutions Act of 2006, signed by Governor Arnold Schwarzenegger on September 27,
2006, required the CARB to lower GHG emissions to 1990 levels by 2020a 25
percent reduction statewide, with mandatory caps for significant
AB 32 directed CARB to develop discrete early actions to reduce
preparing a scoping plan (i.e., the Climate Change Scoping Plan) in order
how best to reach the 2020 limit.
Senate Bill 97 (Dutton, Chapter 187, Statutes of 2007), signed on August 24, 2007,
o
directed the Governor's Office of Planning and Research (OPR) to develop
guidelines to mitigate GHG emissions identified through the CEQA
including the effects associated with transportation and energy
directed by SB 97, the Natural Resources Agency adopted Amendmen
CEQA Guidelines for GHG on December 30, 2009. On February 16, 2010, the
Office of Administrative Law approved the Amendments, and filed
Secretary of State for inclusion in the California Code of Regul
Amendments to the CEQA Guidelines implementing SB 97 became effective on
March 18, 2010.
BAAQMD
AY REA IR UALITY ANAGEMENT ISTRICT
The BAAQMD is the primary agency responsible for air quality reg
San Francisco Bay Area Air Basin. As part of its role in air quation, BAAQMD has
prepared CEQA air quality guidelines to assist lead agencies in
proposed projects and plans. The guidelines provide procedures f
quality impacts during the environmental review process consistent with CEQA requirements.
The CEQA Air Quality Guidelines provide CEQA thresholds of significance for operational
GHG emissions from land use projects for the first time. The BAA
thresholds from construction activities, but recommends that significance be determined in
relation to meeting AB 32 GHG reduction targets. OPRs amendment
as well as BAAQMDs CEQA Air Quality Guidelines and thresholds of significance have been
incorporated into the analysis of potential GHG impacts associated with the Project.
SSFCAP
OUTH AN RANCISCO LIMATE CTION LAN
18
The City of South San Francisco prepared a Pedestrian Master Pla and a Climate
19
Action Plan (CAP). The City Council adopted the PMP and CAP on February 12, 2014. The
City of South San Francisco, Pedestrian Master Plan, February 13http://www.ssf.net/1531/Pedestrian-Master-Plan.
18
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CAP provides goals, policies, and programs to reduce GHG emissio
adaptation and support the goals of AB 32 and SB 375. The PMP pr-wide
plan providing for a network of sidewalks and paths to facilitatncreased walking to local
destinations. The PMP includes an inventory and assessment of th
a gap analysis, to identify and prioritize needed improvements a
measurable implementation measures. A key focus area is the Downtown Area and downtown
residential neighborhoods.
I
MPACTS
a) Generation of Greenhouse Gas Emissions
Significance Criteria: The BAAQMD CEQA Air Quality Guidelines identify a project specific
threshold of either a brightline threshold of 1,100 metric tons of COe per year or an efficiency
2
threshold of 4.6 metric tons of COe per year per service population (i.e., the number of
2
residents plus the number of employees associated with a new dev
cumulatively considerable contribution of GHG emissions and a cumulatively sign
Alternatively, a project that is found to be consistent with a Q
than significant impact to global climate change. This analysis metric tons of
COe per year or 4.6 metric tons of COe per year per service population significance criterion
22
while also reviewing the goals, policies, and measures within th
CalEEMod (Version 2013.2.2) was used to quantify GHG emissions associated with Project
construction activities (for informational purposes), as well as-term operations associated
with natural gas space and water heating, electricity, landscape
CalEEMod incorporates local energy emission factors and mitigation measures based on the
20
CAPCOAs Quantifying Greenhouse Gas Mitigation Measures and the California Climate Action Registry
21
General Reporting Protocol.
Estimated construction GHG emissions that would be associated wiProject are presented
in GHG Emissions Table 1. The estimated construction GHG emissions are 109 metric tons
of COe. The BAAQMD does not recommend a threshold for GHG emissions from
2
construction, so this analysis (similar to many other analyses pn the San Francisco Bay
Area Air Basin) amortizes the construction emissions over the li
and adds amortized construction emissions to the annual operatioThe 30-year
amortized annual construction related GHG emissions would be 3.6 metric tons of COe.
2
GHG Emissions Table 1 also provides the estimated operational GHG emissions that would
be associated with the Project. The GHG operational (plus construction) impacts with
would be approximately 17 metric tons of COe per year, which is below the BAAQMD
2
significance threshold of 1,100 metric tons and thus, would be a than significant
impact related to climate change.
City of South San Francisco, Climate Action Plan, February 13, 2http://www.ssf.net/1803/Climate-Action-Plan.
19
CAPCOA, Quantifying Greenhouse Gas Mitigation Measures, August 2010, http://www.capcoa.org/wp-
20
content/uploads/2010/11/CAPCOA-Quantification-Report-9-14-Final.pdf
California Climate Action Registry General Reporting Protocol, Mhttp://www.theclimateregistry.org/downloads/GRP.pdf
21
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b) Potential Conflicts with an Applicable Plan, Policy, or Regul
The City of South San Francisco has adopted a CAP regarding the reduction of GHG emiss
The City has established a baseline government and community-wide inventory of GHG
emissions. The Project would result in a significant impact if i
State goals and the goals, policies, and measures of the applicable
emissions. The assumption is that AB 32 and the CAP will be succ
emissions and reducing the cumulative GHG emissions statewide byState
have taken these measures, because no project individually could
positively or negatively) on the global concentration of GHG The Project has been reviewed
relative to the AB 32 measures and South San Francisco CAP and i has been determined
that the Project would not conflict with the goals of AB 32 and
GHGET1
MISSIONS ABLE
PRGGE
ROJECT ELATED REENHOUSE AS MISSIONS
GHG COe Metric Tons Per
2
Emission Source
Year
Construction (30-year amortized) 3.6
Operations
Area Sources 0.1
Energy 4.8
Mobile 8.0
Solid Waste 0.6
Water 0.2
Total Emissions (with Construction) 17.3
BAAQMD Significance Threshold 1,100
Potentially Significant? No
Source: CalEEMod Version 2013.2.2
Notes: Refer to Appendix A for CalEEMod output data. Values reflect rounding.
The principal State plan and policy adopted for the purpose of r
32. The quantitative goal of AB 32 is to reduce GHG emissions to
Statewide plans and regulations such as GHG emissions standards for vehicles and the LCFS are
being implemented at the statewide level, and compliance at the
not addressed. The Project does not conflict with AB 32 measures and South San
Francisco CAP and it has been determined that the Project would not conflict wit
goals of AB 32 and the applicable CAP (AB 32). Therefore the Project is in compliance
with the stated regulations contained in the applicable plans.
The Project would not result in an impact or contribute to a cumulative impact with
respect to GHG emissions. The Project would not conflict with th
regulations adopted for the purpose of reducing GHG emissions. T
would have a no impact on climate change.
Greenhouse Gas Finding:The Project has been reviewed relative to the AB 32 measures and
South San Francisco CAP and it has been determined that the Proj
the goals of AB 32 and the applicable CAP. Therefore the Project is also in compliance with the
stated regulations contained in the plans.
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The Project would not result in an impact or contribute to a cum
GHG emissions. The Project would not conflict with the plans, po
adopted for the purpose of reducing GHG emissions. Therefore, th-
than-significant impact on climate change.
The Project would not conflict with the plans, policies, and reg
of reducing GHG emissions. No impact would result and no mitigation is required.
3.5BR
IOLOGICAL ESOURCES
Potentially Less Than Less Than
Significant Significant SignificantNo
with
Impact Impact Impact
Mitigation
Would the Project:
a) Have a substantial adverse effect, either X
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
Wildlife or U.S. Fish and Wildlife Service?
b) Have a substantial adverse effect on any
X
riparian habitat or other sensitive natural
community identified in local or regional
plans, policies, regulations or by the
California Department of Fish and Wildlife
or US Fish and Wildlife Service?
X
c) Have a substantial adverse effect on federally
protected wetlands as defined by Section 404
of the Clean Water Act (including, but not
limited to, marsh, vernal pool, coastal, etc.)
through direct removal, filling, hydrological
interruption, or other means?
X
d) 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?
X
e) Conflict with any local policies or ordinances
protecting biological resources, such as a tree
preservation policy or ordinance?
X
f)Conflict with the provisions of an adopted
Habitat Conservation Plan, Natural
Community Conservation Plan, or other
approved local, regional, or state habitat
conservation plan?
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S
ETTING
I
NTRODUCTION
The biological assessment used to inform this section was prepar
Marangio Biological Consulting(Michael Marangio, Biological Resources Assessment Prepared for
Allison Knapp Wollam, Consulting, Proposed Residence, 901 Larch Avenue, South San Fran.
November 10, 2015). The complete assessment is contained in Appendix A. The purpose of
this biological resource assessment wasto review a site proposed for development in sufficient
detail to determine if the Project may affect threatened, endang
plant species as well as important habitats such as wetlands. Thebiological assessment provides
information that is intended for use in environmental documents .
PD
ROJECT ESCRIPTION
901 Larch Avenue is vacant and located at the terminus of Lincol
Larch Avenue, on the north facing slope of Sign Hill (see Figures 1 ProjectArea and2
Project Location in Chapter 2). The northern and northeastern facing slopes of Sign Hill,
consisting of approximately 46 acres, are in private ownership. Sign Hill Park is located on the
south facing slopes of the hill, is owned by the City and is public park and recreation land.
Sign Hill Park consists of 27 acres of open space with approximately two miles of hiking trail
and along a ridge spur reaches approximately 600 feet in elevati. Sign Hill is home to the
Mission Blue and Callippe Silverspot butterflies, both federally listed endangered species.
The Project would construct a single-family residence consisting of approximately 2,500 square
feet. Construction is proposed on the front third of the lot. Landscaping is proposed in the
front, side and portions of the rear of the property. Japanese Maple, Winter Boxwood, Star
Jasmine, camellia, and lavender are proposed (see Figure 2 in Project Description).
Vegetation on the Project site consists of introduced grasses and plants; escaped exotics that
have spread from nearby garden landscaping including grasses and weeds. Three trees are on the
site: one pine tree (Pinus sp.) about 11 inches diameter at breast height (dbh), one Monterey
cypress (Cupressus macrocarpa)) about 24 inches dbh and one deodar cypress (Cedrus deodara),
about 18 inches dbh (Michael Marangio, Biological Resources Assessment Prepared for Allison Knapp
Wollam, Consulting, Proposed Residence, 901 Larch Avenue, South Francisco, California. November
10, 2015). The three trees would be removed to conduct grading and
The Applicant proposes the following as part of the Project as noted in Chapter 2, Project
Description:
If Project construction activities occur during the nesting season (approximately March
to August 31), for birds protected under the California Fish and
(MBTA), the applicant will retain a qualified biologist to condu
survey for protected birds on the site and in the immediate vicinity. The survey
done no more than 15 days prior to the initiation to constructio
that nesting birds are found on the Project site or in the immed
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Applicant will locate and map the nest site(s) within three days and su
the City and California Department of Fish and Wildlife ("CDFW")-
disturbance buffer of 250-feet, and conduct on-going weekly surveys to ensure the no-
disturbance buffer is maintained. In the event of destruction of a nest w
juvenile or adult raptor should become stranded from the nest, i
qualified biologist will immediately notify the CDFW. The qualif
coordinate with the CDFW to have the injured bird either transferred
recovery center or, in the case of mortality, transfer it to th
notification or,
Conduct tree removal outside of the nesting season to completely avoid any potential
impacts to nesting birds.
The Applicant, during a meeting on December 1, 2015, indicated the preference to remove trees
outside nesting season (meeting attendees: Sailesh Mehra, Adena Friedman, Allison Knapp). The
analysis contained herein notes the removal of three trees to comply with a reasonable wor
case analysis under CEQA; in all likelihood only one tree would be required to be removed.
RF
EGULATORY RAMEWORK
Local, State, and federal regulations have been enacted to proviprotection and
management of sensitive biological and wetland resources. The f
key local, State, and federal regulations that apply to these re
F
EDERAL
The U.S. Fish and Wildlife Service (USFWS) is responsible for protection of terrestrial and
freshwater organisms through implementation of the federal Endan
the Migratory Bird Treaty Act (MBTA). The U.S. Army Corps of En
primary responsibility for protecting wetlands under Section 404 of the Clean Water Act (CWA).
The Corps also regulates navigable waters under Section 10 (33 U
Harbors Act.
S
TATE
The California Department of Fish and Wildlife (CDFW) is the responsible agency for
administration of the California Endangered Species Act (CESA), and for prote
and water bodies through the Streambed Alteration Agreement proc et
seq. of the California Fish and Game Code.
Certification from the California Regional Water Quality Control Board (RWQCB) is also
required when a proposed activity may result in discharge into n
Section 401 of the CWA and Environmental Protection Agency (EPA) Section 404(b)(1)
Guidelines. The RWQCB also has jurisdiction over waters of the State not regulated by the
Corps under the Porter-Cologne Act. The following discusses in more detail how State a
federal regulations address special-status species, wetlands and other sensitive natural
communities.
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S-SS
PECIALTATUS PECIES
Special-status species are plants and animals that are legally protected
federal ESAs, theMigratory Bird Treaty Act, the California Fish and Game Code (se
22
3503.5, 3511, 3513, 3515, and 4700), or other regulations. In addition, pursuant to CEQA
Guidelines Section 15380, special-status species also include other species that are considered
rare enough by the scientific community and trustee agencies to
particularly with regard to protection of isolated populations, nesting or denning lo
communal roosts and other essential habitat. Species with legal
State ESAs often represent major constraints to development; parre wide
ranging or highly sensitive to habitat disturbance and where pro
in a take of these species.
WOWUS
ETLANDS AND THER ATERS OF THE NITED TATES
Although definitions vary to some degree, wetlands are generallyd to be areas that are
periodically or permanently inundated by surface or ground water
adapted to life in saturated soil. Wetlands are recognized as i
national level due to their high inherent value to fish and wildlife, use as storage areas for storm
and flood waters, and water recharge, filtration and purificatio
and RWQCB have jurisdiction over modifications to river banks, l
other wetland features. Technical standards for delineating wetlands have been developed
the Corps and the USFWS, which generally define wetlands through
criteria: hydrology, soils, and vegetation.
The CWA was enacted to address water pollution, establishing regulations and permit
requirements regarding construction activities that affect storm
operations, and water quality standards. The regulatory program
surface waters be controlled under the National Pollutant Discharge Elimination System
(NPDES) permit program which applies to sources of water runoff,
public facilities.
Under Section 404 of the CWA, the Corps is responsible for regulof fill
material into waters of the United States. The term waters in-wetland
bodies of water that meet specific criteria as defined in the Co
three of the identified technical criteria must be met for an area to be identified as a wetland
under Corps jurisdiction, unless the area has been modified by h
permit must be obtained before fill can be placed in wetlands or
Special-status species include: designated (rare, threatened, or endangered) and candidate species
22
designated (threatened or endangered) and candidate species for
to be rare or endangered under the conditions of Section 15380 of the California Environmental Quality Act
those identified on lists 1A, 1B, and 2 in the California Native Inventory of Rare and Endangered Plants of
California (2001); and possibly other species which are considered sensitive due to limited distribution or
information to permit listing or rejection for state or federal Inventory or
identified as California Species of Special Concern (SSC) by the CDFW. Species designated as a SSC have no legal protecti
status under the California Endangered Species Act but are of co
populations and other factors.
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States. The type of permit is determined by the Corps depending on the amount of acreage and
the purpose of the proposed fill.
Certain activities in wetlands or other waters are automatical
nationwide permit which allows filling where impacts are considered minor. Eligibility for a
nationwide permit simplifies the permit review process. Nationw
and fill of waters of the U.S. for a variety of routine activiti
utility line crossings, streambank protection, recreational facilities and outfall structures. A
project must demonstrate that it has no more than a minimal adve
ecosystem, including species listed under the ESA to qualify for
this means that there will be no net loss of either habitat acreage o
appropriate mitigation where fill activities are proposed.
The Corps assumes discretionary approval over proposed projects
significant, requiring adequate mitigation and permit approval. To provi
EPA Section 404(b)(1) Guidelines, an applicant must demonstrate that
unavoidable and is the least environmentally damaging practicablthat will achieve
the overall project purpose. The 1990 Memorandum of Agreement b
Corps concerning the Determination of Mitigation under the Guide
with the first priority to avoid impacts, the second to minimize impacts, and the third to provide
compensatory mitigation for unavoidable impacts.
Jurisdictional authority of the CDFW over wetland areas is estab et
seq. of the Fish and Wildlife Code, which pertains to activities thatld disrupt the natural
flow or alter the channel, bed, or bank of any lake, river, or s
stipulates that it is unlawful to substantially divert or obstru
change the bed, channel, or bank of any river, stream or lake without notifying the CDFW,
incorporating necessary mitigation, and obtaining a Streambed Al
Wetlands Resources Policy of the CDFW states that the Fish and W
strongly discourage development in or conversion of wetlands, unless, at a minimum, pr
mitigation assures there will be no net loss of either wetland h
CDFW is also responsible for commenting on projects requiring Co
and Wildlife Coordination Act of 1958.
In addition, the RWQCB is responsible for upholding state water
Section 401 of the CWA, projects that apply for a Corps permit f
material, and projects that qualify for a Nationwide Permit must obtain water quality cer
from the RWQCB. The RWQCB is also responsible for regulating we-
Cologne Act, which may include hydrologically isolated wetlands
Corps under Section 404 of the Clean Water Act. Recent federal Su
limited the limits of Corps jurisdiction, but the RWQCB in some
jurisdiction over these features.
SNC
ENSITIVE ATURAL OMMUNITIES
Protecting habitat on an ecosystem-level is increasingly recognized as vital to the protection of
natural diversity in the State, in addition to species-oriented management. Protecting habitat on
an ecosystem-level is considered the most effective means of providing long-term protection of
ecologically viable habitat, and can include whole watersheds, e
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communities. Providing functional habitat connectivity between
sustaining healthy wildlife populations and allowing for the continued dispersal of native plant
and animal species.
Although sensitive natural communities have no protected legal s
Endangered Species Acts, they are provided some level of protecthe CEQA
Guidelines identify potential impacts on a sensitive natural com
criteria. As anexample, a discretionary project that is constructed on any ripa
grassland, valley oak woodland, or other sensitive natural community would normally be
considered to have a significant effect on the environment. Fur
community could be interpreted as substantially diminishing habi
abundance, quality,and degree of past disturbance, and the anticipated impacts to the spe
community type. Where determined to be significant under CEQA,
require mitigation through avoidance, minimization of disturbanc
compensatory mitigation when unavoidable.
CSSF
ITY OF OUTH AN RANCISCO
GeneralPlan
The Open Space and Conservation Element of the City of South San Francisco General Plan
contains a number of policies related to protection of sensitivend resources
that are applicable to the site. The following policies are excerpted from the Citys 1999 General
Plan.
7.1-G-1: Protect special status species and supporting habitats within
o
Francisco, including species that are State or federally listed as Endangered, Threatened,
or Rare.
7.1-G-2: Protect and, where reasonable and feasible, restore saltmarsh
o
7.1-I-2: As part of the Park, Recreation and Open Space (PROS) Master
o
institute an ongoing program to remove invasive plant species from ecologically sensitive
areas, including Sign Hill Park, Colma Creek Linear Park, Bayfro
other City-owned open space, as depicted in Figure 7-1.
7.1-I-3: As part of development approvals on sites that include ecologically sensitive
o
habitat designated in Figure 7-2, require institution of an on-going program to remove
and prevent the re-establishment of the invasive species and restore the native spe
7.1-I-4: Require development on the wetlands delineated in figure 7-1 to complete
o
assessments of biological resources.
7.1-I-5: Work with private, non-profit conservation, and public groups to secure funding
o
for wetland and marsh protection and restoration projects.
Municipal Code
South San Francisco Municipal Code Section 13.30.020 defines a Protected Tree as one with a
circumference of 48 or more when measured 54 above natural gra
designated by the Director of Parks and Recreation as one of uni
public due to its location or unusual appearance, historical significance o
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of trees that the Director of Parks and Recreation has determine
others for survival.
FLS
IELD AND ITERATURE TUDY
Field Survey
A field survey was conducted on November 3, 2015. Site location and features were reviewed
using local street maps, USGS 7.5 minute quad sheets (San Franci
maps.
The Project presently consists of a steep hillside with access from the north side of the lot from
Larch Avenue. Vegetation consists of introduced grasses and plan
have spread from nearby gardens. As noted above, Sign Hill abuts the Project site to the
southeast. The northern and northeastern facing slopes of Sign Hill, consisting of approximately
46 acres, are in private ownership. Sign Hill Park is located on the south facing slopes of the
hill, is owned by the City and is public park and recreation land.
The Project site is vegetated mainly with introduced grasses, weeds, and escaped exotics, and is
considered a mixture of Non-Native Annual Grassland and Ruderal (disturbed) habitats. Plant
that were observed on the northern portion of the site adjacent to the LarchAvenue roadway
are dominated by introduced rattlesnake grass (Briza maxima), wild-oat (Avena barbata),
perennial ryegrass (Lolium perenne), and English plantain (Plantago lanceolata). Scattered plants of
Italian thistle (Carduus pycnocephalus) covering an estimated areas of 40 square feet were also
noted. The upper slopes of the property are dominated by clumps of introduced Cotoneaster
(Cotoneaster sp.) as well as Algerian ivy (Hedera algeriensis), Pittosporum (Pittosporum sp.) and
scattered pampas grass (Cortaderia selloana) and fennel (Foeniculum vulgare). Native plants included
toyon (Heteromeles arbutifolia), California blackberry (Rubus californicus), and coyote brush (Baccharis
pilularis)
A pine tree (Pinus sp.) about 11 inches diameter breast height (dbh), deodar cedar (Cedrus
deodara), about 18 inches dbh and a Monterey cypress (Cupressus macrocarpa)) about 24 inches dbh
are located on the Project site. For purposes of the CEQA analysis we assume all three trees
would be removed, as a conservative estimate.
Very little wildlife was seen on the Project site. Burrows of Bott Thomomys
bottae) were present, generally scattered over the site. Birds that would be expected are those
adapted to residential areas such as house finch (Carpodacus mexicanus), American crows (Corvus
brachyrhynchos), Bushtit (Psaltriparus minimus), California towhee (and Anna's
Melozone crissalis)
hummingbird (Calypte anna). Several common species of salamander including slender
salamander (Batrachoseps attenuatus) and arboreal salamander (Aneides lugubris) would also be
expected to be present.
No ponded surface water or natural channels were observed on the Project site nor was there
any evidence for the pooling of water over the winter rainy seas
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Literature Survey
Special Status Species
On the basis of a review of the California Natural Diversity Datbase report from the California
Department of Fish and Wildlife for the Project area (CNDDB, 2015; CNPS, Rare Plant
Program, 2015) and general knowledge of special status species of plants and animals in the San
Francisco Bay area, a table was developed of the potential special status plants and animals
known from the vicinity of the Project (Appendix A,Michael Marangio, Biological Resources
Assessment Prepared for Allison Knapp Wollam, Consulting, Proposed Residence, 901 Larch Avenu
San Francisco, California. November 10, 2015, Tables A and B). All listed potential animal
species such as fishes requiring permanent aquatic habitats werempact
analysis since suitable aquatic habitat is not present on the Project site. Additionally, plants and
animals requiring marshlands were also eliminated from further analysis because such habitats
are also not present on the Project site.Most of the species on the lists have specialized habitat
requirements that are not present on the Project site, and therefore would not be expected to be
locatedon the site.
The issues of special status wildlife species, migratory birds, protected trees, and sensitive plant
species are evaluated for potential Project impacts. The following is a summary of the biology
of these species and issues, including a discussion of the potential for their presence withi
Project area and the potential impacts of the Project on these resources. To provide a more
thorough analysis, several special status wildlife species known-2 mile of the Project or
which are otherwise deemed to be potentially present in the Projalso discussed.
The San Francisco Forktail Damselfly
General Background. The San Francisco forktail damselfly, (Ishnura gemina), has no protection under
Federal or State statutes and is found in very localized urban areas. Several small populations
have gone extinct since their discovery.
Occurrence in the Project Vicinity. A documented location (CNDDB 2015) indicates its presence
about 3.0mi SSWof the Project site. Historically,some populations have been extirpated due
to urbanization and some habitat has naturally converted from small shallow ponds to dry pond
beds. The species is associated with marshy aquatic habitat, non
Project site. Therefore, the Project would not have any significant impact on this species.
California Red-legged Frog
General Background. The California red-legged frog (Rana draytonii) (CRLF) is listed by the USFWS
as Threatened and is classified by the CDFW as a Species of SpecThe frog breeds
primarily in ponds, but will also breed in slow moving streams, ools in intermittent
streams and is seldom found in brackish waters. Inhabited ponds are typically p
2 feet (0.6 meters) in depth, and contain emergent and shoreline
Occurrence in the Project Vicinity. CNDDB (2015) documents the presence of this protected species
about 3 miles south southeast of the Project site. Since no aquatic habitat is present on the
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Project site, nor is any suitable aquatic habitat nearby,the site would not provide suitable habitat,
either aquatic or upland. No impacts to the CRLF would result from the Project.
Callippe SilverspotButterfly
General Background. The Callippe silverspot butterfly(Speyeria callippe callippe) is listed as federally
endangered. The historic range of Callippe silverspot includes the inner Coast Ranges on the
eastern edge of the San Francisco Bay from northwestern Contra C
Valley in Alameda County and from San Francisco south to La Hond
the west side of the Bay. This butterfly has been found at San Bruno Mountain and Sign Hill in
San Mateo County, in the hills near Pleasanton in Alameda County
County, and in the hills between Vallejo and Cordelia in Solano
Callippe silverspot butterfly occurs mainly in native grassland. Female butterfl
on its larval foodplant, Johnny jump-up (Viola pedunculata). After one week, the larvae hatch
and shelter within ground litter where they spend the summer andthe spring the
larvae eat the leaves of Johnny jump-up, pupate, and emerge as butterflies between mid-May and
mid-July. The main causes of this species' decline is the loss and
urban development. Nectar sources include Italian thistle (Carduus pycnocephalus), milk thistle
(Silybum marianum), coyote mint (Monardella villosa), hairy false goldenaster (Heterotheca (Chrysopsis)
villosa), coast buckwheat (Eriogonum latifolium), mourning bride (Scabrosa atropurpurea), buckeye
(Aesculus californica), narrow leaf mule-ears (Wyethia angustifolia), and California Horkelia (Horkelia
californica).
Occurrence in the Project Vicinity. This species is known on Sign Hill (CNDDB 2015). However, the
habitat on the Project site is for the most part unsuitable for Callippe Silverspot butterflies.
Much of the site is dominated by non-native grasses, weedy annuals, and introduced vines and
non-native trees.
San Bruno Elfin Butterfly
General Background.The San Bruno Elfin Butterfly(Incisalia mossii bayensis) is federally endangered.
The butterflyinhabits rocky outcrops and cliffs in coastal scrub on the San Fr;
its patchy distribution follows the location of its host plant, s Sedum spathulifolium).
Adults of this butterfly emerge in early spring, in February and March. They m
thereafter and deposit eggs on the stonecrop plants. The eggs ty
June, most will have completed their larval development, at which timehost plant
to pupate in ground litter. They lie dormant as pupae until the
include common Lomatium (Lomatium utriculatum), buttercup (Ranunculus californicus), and Achillea
(Achillea millefolium).
Typical habitat includes steep, north-facing slopes in foggy locations. The San Bruno Elfin is
restricted to a few small populations, the largest of which occu
north of the Project. Its habitat has been reduced in the past b-road recreation,
and urban development. To protect this as well as the Mission Bl
Conservation Plan has been implemented on San Bruno Mountain, in
were opened for development while the higher areas were protecte
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Occurrence in the Project Vicinity.The closest known documentation of the presence of this butterfl
is about 2.8 miles to the north (CNDDB 2015). Suitable habitat conditions including host and
nectar plants are not present on the Project site. Therefore nosignificant impacts to this species
would resultfrom the Project.
Bay Checkerspot Butterfly
General Background. The Bay Checkerspot (Euphydryas editha bayensis)has a life cycle which may
include several different host plants. Following mating in mid-spring, the female butterflies lay
their eggs on a native plantain, Plantago erecta. If the plantain is not sufficient for development,
the larvae may move onto one of two species of owl's clover (Castilleja (Orthocarpus) densiflorus or
C. exserta). Generally, one season is insufficient for completion of development and
must enter dormancy until the following winter,when the rains allow plant growth to begin
again. The larvae then emerge to feed for a little longer, pupatults
emerge shortly thereafter.
Habitat is often found on outcrops of serpentine soil. Nectar plgoldfields (Lasthenia
californica), tidy tips (Layia spp.), serrated onion (Allium serra), seaside muilla (Muilla maritima), and
Lomatium (Lomatium spp). Populations of the Bay Checkerspot historically inhabited numero
areas around the San Francisco Bay including the San Francisco p
San Jose, the Oakland hills, and several locations in Alameda Coow
known only from San Mateo and Santa Clara counties. Changing dis
grazing) as well as introduced grassland plants have caused decl
Occurrence in the Project Vicinity. The closest known population is located about one mile north of
the Project. The Project site contains unsuitable habitat with no evidence of the presence of
habitat for host plants (owl's clover) or nectar plants. Therefore, the Project site is not suitable
habitat for Bay Checkerspot Butterflies and no impacts would result from the Project.
Mission Blue Butterfly
General Background.The Mission Blue butterfly (Icaricia icarioides missionensis) was formerly relatively
widespread on the San Francisco and Marin peninsulas. Now the Mission Blueis restricted to a
few sites in these areas. Approximately 2,000 acres of habitat for the butterfly is being managed
by the San Mateo County Department of Parks and Recreation on San Bruno Mountain.
The butterfly's required habitat is coastal scrub. Larvae of the Mission Blue emerge from a
dormant state in early spring. Host plants consist mainly of per Lupinus albifrons, L.
variicolor, and L. formosus). Nectar plants include Eriogonum latifolium and Brodiaea pulchella. The
larvae eventually enter the ground to pupate. Several weeks late
feed on lupine nectar, mate and lay eggs. The eggs hatch within
a few weeks before they enter dormancy until the following spring when they will complete their
development.
Occurrence in the Project Vicinity. The Mission Blue butterfly is documented to be present on Sign
Hill (CNDDB 2015) as well San Bruno Mountain to the north. Habitat providing suitable host
and nectar plants is not present on the Project site. The Project would not result in impacts to
this species.
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I
MPACTS
a)Special-Status Species
Significance Criteria:The Project would have a significant impact if were to result in
adverse effect on special-status species, as identified in 3.5 Biological Resources, section a,
above.
The disturbed nature of the site,resulting from previousgrading to construct Larch Avenue,
unstable soil conditions,and the spread of invasive weed species to the site from outside and
adjacent sources has resulted in the elimination of the original
consisted of grassland and coastal scrub. The spread of invasiv
construction activities on the site greatly reduces the potential for the presence of federal and
state protected plants. The lack of native vegetative cover als
the presence of federal and state protected animal life. None of the existing vegetation includes
any sensitive habitats.
Plant Species of Special Concern. The Project site is highly disturbed. The plants that dominate
site consist mainly of introduced invasive annual plants, along -native treesand shrubs.
A reconnaissance survey was conducted on November 3, 2015. No habitat for special status
species of plants were observed and would not be expected because of the general disturbed
nature of the site dominated by introduced plant species. No sensitive plant species would be
affected by the Project.
Animal Species of Special Concern. Suitable wildlife habitat on the site was limited to conditions that
could support introduced and species that tolerate human disturburban
conditions. The dominance of introduced non-native annual plants limits the value of the habitat
to only "generalist" species that can tolerate disturbed conditi
sources. As a result of the small size of the parcel (0.17 acres) and the dominance of non-native
annual plant species, the Project site would be highly unlikely to suppo
animal species (which are generally "specialist" species that require c
food that are not present). About 40 square feet of non-native Italianthistle plants that are a
nectar source for the Callippe Silverspot butterfly were observe
this small amount of potential nectar source would not result in The
Project would have no impact on special-species or species of concern.
b) and c) Jurisdictional Habitat
Significance Criteria: The Project would have a significant impact if it were to substa
sensitive natural communities or jurisdictional wetlandsandWaters of the U.S. as identified in
Biological Resources 3.5, sections b and c, above.
Generally speaking, wetlands are legally defined as areas that a
water, have soils that indicate the presence of water, and have he
presence of water. A formal protocol for wetland analysis was noconducted. General
observations revealed that the ground surface of the Project sit
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basins or other depressions were noted where water would likely ing the winter rainy
season. A constructed ditch presently draining water off the steep hillsevidence
of hydraulic processes that indicate wetland hydrology or vegetation. Therefore no federal or
state-protected wetlands are present. Further wetland analysis regarding jurisdictional evaluation
is not required.
There are no special plant or animal species of concern or habit
identified in section a, above. The Project would have no impact on any sensitive natural
communities or jurisdictional wetlands.
d) Native Fish and Wildlife Movement Opportunities, Nesting Habitat, and Native
Wildlife Nursery Sites.
Significance Criteria: The Project would have a significant environmental impact if it
interfere substantially with the movement of any native resident or migratory fish
species or with established native resident or migratory wildlife corrid
native wildlife nursery sites.
Wildlife movements include migration (i.e., usually one way per season), inter-population
movement (i.e., long-term genetic flow) and small travel pathways (i.e., daily moveme
an animals territory). While small travel pathways usually faci
range activities, such as foraging or escape from predators, they also provide connection
between outlying populations, permitting an increase in gene flo
These linkages among habitat types can extend for miles from pri
on a large scale throughout California. Habitat linkages facilitate movemen
located in small, discrete areas and populations located within larger habitat are
habitats found within a large-scale landscape results in wildlife populations that consist of
discrete sub-populations comprising a large single population, which is often
meta-population. The movement between wildlife populations is facilitated through
linkages, migration corridors and movement corridors even where patches of pristine habitat are
fragmented. Potentially low frequency genetic flow may lead to c
pressures promoting mortality are strong, potential extinction.
The Project would result in the construction of a residence on a 0.17 acre site where houses are
present immediately to the west, north, and east on similar-sixed lots with open space to the
southeast. The Project in its undeveloped state does not presently provide
suitable habitat since residential development generally surrounds the site to the west
east. Therefore the Project would have no significant impact on biolog
with regard to movement corridors.
The Migratory Bird Treaty Act (MBTA) protects all common wild birds found in the United
States except certain introduced species and certain game birds.
abandonment and/or loss of reproductive effort or the loss of ha
depend would be in violation of the MBTA. California Fish and Game (CFG) Code section
3503 also makes it illegal to destroy any birds nest or any bir
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the MBTA. CFG Code section 3503.5 further protects all birds of prey, such as hawks and owl,
and their eggs and nests from any form of taking.
Although no nesting birds were observed, the large trees and bruat the Project site may
provide suitable cover for nesting of birds, including birds of
summer seasons. Nest disturbance as a result of proposed tree and brush removal would be
considered a breach of MBTA regulations and would be a significa
The Project would remove the three trees on the site. There is the potential for raptors(birds of
prey) and other protected birds to nest on the site, and adjacent to the site. These birds are
protected under the federal Migratory Bird Treaty Act and California Fish and Game Code
section 3503.5. Disturbance of birds during the nesting season that results in loss of nestlings
would be a significant environmental impact. The Applicant, as identified in the Setting
Section above, Chapter 2 Project Description and Appendix A, proposes to remove the trees
outside of nesting season. The Applicant notes that if trees are removed during nesting season,
a biologist will survey the site no more than 15 days prior to t
be followed.
The Project would have a less than significant impact on biological resources with
regard to native wildlife movement opportunities or nursery sites because the Applicant
will either remove trees outside of nesting season or follow the
during nesting season. Tree removal may not commence until a qualified biologist
conducts a preconstruction survey for protected birds on the site and in the imme
vicinity. The survey will be done no more than 15 days prior to
construction activities. In the event that nesting birds are fo
the immediate vicinity, the Applicant will locate and map the nest site(s
days and submit a report to the City and California Department o
("CDFW"), establish a no-disturbance buffer of 250 feet, and conduct on-going weekly
surveys to ensure the no-disturbance buffer is maintained. In the event of destruction of
a nest with eggs, or if a juvenile or adult raptor should become
injured or killed, the qualified biologist will immediately notiified
biologist will coordinate with the CDFW to have the injured bird
raptor recovery center or, in the case of mortality, transfer i
hours of notification.
e) Local Policies and Ordinances
Significance Criteria: The Project would have a significant environmental impact if it
conflict with any local policies or ordinances protecting biolog
preservation policy or ordinance.
General Plan
The Open Space and Conservation Element of the City of South San Francisco General Plan
contains a number of policies related to protection of sensitive
that are applicable to the Project. These policies are implemented through the biological
resource assessment and this CEQA analysis. The biological resource assessment found no
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biological or wetlands resources on the site.The following contains an analysis of General Plan
policies identified in the Setting Section.
General Plan Open Space Policy 7.1-I-2: As part of the Park, Recreation and Open Space (PROS) Master
Plan update, institute an ongoing program to remove invasive pla
including Sign Hill Park, Colma Creek Linear Park, Bayfront Liner City-owned open space,
as depicted in Figure 7-1. The Project site does not contain habitat or ecologically sensitive areas,
and will not contain invasive plant species that could enter hab
General Plan Open Space Policy 7.1-I-3: As part of development approvals on sites that include ecolog
sensitive habitat designated in Figure 7-2, require institution of an on-going program to remove and prevent the re-
establishment of the invasive species and restore the native species. This policy does not directly apply to
the Project. The Project site is affected by invasive exotic pla
to be ecologically significant; therefore there is no habitat to protect. The Project site is
separated from Sign Hill Park by privately-owned land with an Open Space designation,
although the zoning designation could permit limited low-density development, as noted in
Chapter 2, Project Description.
The Project will be required by Fire Department Condition of Approval #12 (see Hazards and
Hazardous Materials, Section 3.6) to landscape with non-invasive plantings to minimize the
potential for brush fire. The condition also benefits the biolo
General Plan, Open Space Policies 7.1-G-1: Protect special status species and supporting habitats within
San Francisco, including species that are State or federally lis-G-2:
Protect and, where reasonable and feasible, restore saltmarshes and wetlands; 7.1-I-4: Require development on the
wetlands delineated in figure 7-1 to complete assessments of biological resources and 7.1-I-5: Work with private,
non-profit conservation, and public groups to secure funding for wetection and restoration
projects . There are no special status habitats, saltmarshes or wetlands present on the Project site
based upon the findings of the biological resource assessment.
Municipal Code
Three trees will be removed as a result of the proposed house construction. Since none have a
diameter greater than 48 inches dbh, South San Francisco Municipal Code Section 13.30.020
covering "Protected Trees" will not need to be considered. There are no trees on the site that
meet the Citys definition of protected tree, and no impacts are anticipated. Further,
preparation of a biological assessment and analysis of potential
may have on sensitive biological and wetlands resources is consi
and area plan policies. Therefore, the Project does not conflict with local policies or
ordinances protecting biological resources.
f) Conflict with any Habitat Conservation Plan or Community Cons
Significance Criteria: The Project would have a significant environmental impact if it were to
conflict with ahabitat or community conservation plan or other approved local,
habitat conservation plan protecting biological resources.
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The Project site is not within a habitat conservation plan area and contains no habit suitable for
conservation. The Project would not impact an adopted habitat conservation pla
Biology Finding: After review of CNDDB reports and map overlays for the general Project
area, and field evaluations of the site, the habitatwas found to be highly disturbed and isolated
from other areas containing sensitive habitat. The Applicant proposes tree removal outside of
nesting season or in compliance with biological protocol for proAs a
result, the site is considered to be of very low value for plants and wildlife ingeneral and as well
for sensitive species of plants and animals. No significant biol
full development of the Project site.
3.6CR
ULTURAL ESOURCES
PotentiallyLess ThanLess Than
SignificantSignificant Significant No
with
ImpactImpactImpact
Mitigation
Would the Project:
X
a) Cause a substantial adverse change in the
significance of a historical resource as
defined in §15064.5?
X
b) Cause a substantial adverse change in the
significance of an archaeological resource
pursuant to §15064.5?
X
c) Directly or indirectly destroy a unique
paleontological resource or site or unique
geologic feature?
X
d) Disturb any human remains, including those
interred outside of formal cemeteries?
S
ETTING
RF
EGULATORY RAMEWORK
CEQA relies on the criteria identified in California Code of Regulations, Title 14, Chapter 3,
Article 5, section 15064.5(3).In summary, these criteria include consideration ofwhether the
building:
A.Is associated with events that have made a significant contribution
of California history and cultural heritage;
B.Is associated with the lives of persons important in our past;
C.Embodiesthe distinctive characteristics of type, period, region or method of
construction, or represents the work of an important creative in
high artistic values; or,
D.Has yielded or may be likely to yield, information important in prehistory o
A lead agency does not have to rely solely on the above criterion and may
appropriateness of a potential resource based upon age. Commonl
basis by which to consider a structures potential historic signch a more
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detailed and rigorous analysis is required to determine actual osection
15064.5, California Code of Regulations). Archaeological resources are evaluated pursuant to
Public Resources Code section 21083.2. If it is determined that a project will cause damage to a
unique archaeological resource the lead agency may require reaso
resource to remain in situ. Plan construction to avoid the reso
conservation easement; cap the resource with a layer of soil prior to building; and plannin
park or open space to incorporate the resource are listed as app
(b). A mitigation plan is required if disturbance of the resourper subsection (c).
Subsection (e) identifies not-to-exceed mitigation cost maximums for archaeological resources.
I
MPACTS
a) Historic Resources
Significance Criteria: The Project would have a significant environmental impact if it
a substantial adverse change in the significance of a historical resource as defsection
15064.5.
There are no structures on the site. Consequently, there are no historical resources or structures
on the Project site. The Project would have no impact on historic resources.
b - d) Archaeological Resources
Significance Criteria: The Project would have a significant environmental impact if i
a substantial adverse change in the significance of an archaeolo
section 15064.5, directly or indirectly destroy a unique paleontological resource
geologic feature, or disturb any human remains, including those
cemeteries.
Native Americans, over 5,000 years ago, typically settled along the margins of
San Francisco Bay. The Project site is upland and remote, more than a mile from historic
baylands, and approximately two miles west of a known archaeological site along the historic
baylands.
Geotechnical borings conducted in 2000 (see Section 3.7, Geology and Soils) to a depth of 15
feet indicate subsurface soils consisting of native soil to a defollowed by bedrock.
The soil is clayey sand and the bedrock is sandstone with minor
of culturally significant soils in the sample such as shell, pottery, or bone fragments.
The geotechnical report (GeoTrinity, May 1, 2015) notes that soi
are present on the northeastern portion of site, as undocumentedhe grading
and paving associated with construction of the road and subdivision, would have destroyed
culturally significance soils in the unlikely event they had once been present in the area. Project
impacts associated with archaeological resources are less than significant due to the
location of the Project, more than a mile from the historic bayl
significant soils present in the geotechnical boring, and the grading that occurred in the
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1950s.The Project would have a less than significant impact on archaeological or
paleontological resources.
Cultural Resources Finding: There are no structures on the Project site. The Project would
have a less than significant impact on archaeological or paleontgiven it is more
than a mile from the historic baylands, contains no culturally significant soils in the geotechnical
boring, and the disturbance from the grading that occurred in the 1950s.
3.7GS
EOLOGY AND OILS
PotentiallyLess ThanLess Than
Significant Significant Significant No
with
Impact Impact Impact
Mitigation
Would the Project:
a) Expose people or structures to potential
substantial adverse effects, including the risk
of loss, injury, or death involving:
X
i) Rupture of a known earthquake fault,
as delineated on the most recent
Alquist-Priolo Earthquake Fault
Zoning Map issued by the State
Geologist for the area or based on
other substantial evidence of a known
fault? Refer to Division of Mines and
Geology Special Publication 42.
X
ii) Strong seismic ground shaking?
X
iii) Seismic-related ground failure,
including liquefaction?
X
iv) Landslides?
X
b) Result in substantial soil erosion or the loss
of topsoil?
X
c) 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?
X
d) Be located on expansive soil, as defined in
Table 18-1-B of the Uniform Building Code
(1994), creating substantial risks to life or
property?
X
e) Have soils incapable of adequately
supporting the use of septic tanks or
alternative waste water disposal systems
where sewers are not available for the
disposal of waste water?
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S
ETTING
The 901 Larch Avenue Project site contains geological constraints including a very steep slope,
shallow slope instability (i.e., two foot deep and six foot wide
one off site, and an upslope fill prism. The Project is located within the Sterling Terrace single-
th
family residential neighborhood. The subdivision was constructemid-20 century. The
Project site is one of the few remaining vacant lots in the area
B
ACKGROUND
Typically, the construction of one single-family residence in a residential zone with utilities and
infrastructure in place is categorically exempt from the CEQA re CEQA Guidelines
section 15303, Class 3 New Construction or Conversion of Small Sere
are exceptions to exemptions as stated in CEQAGuidelines section 15300.2, subsection (a).
Subsection (a) clearly states Class 3 exemptions are qualified b
would be located. The subsection further notes a project that inself is ordinarily insignificant
in its impact on the environment may in a particularly sensitive
Therefore, if a project might be located in a biological habitat
slopes, or on properties known to have environmental contamination (hazardous materials),
exception to the exemption noted above requires the lead agency
which may be satisfied by utilizing the sample forms provided in
CEQA Guidelines. The site contains steep and potentially unstable slopes, therefore the City has
prepared this initial study.
F
R
EGULATORY RAMEWORK
CPA
ONDITIONS OF ROJECT PPROVAL
Chapter 1, Legislative Framework, Sections 4 and 5 outlines the Citys standard review
process and conditions of project approval. The Citys Engineering Division is requiring the
following as conditions of Project approval should the Project be approved (Mr. Sam Bautista,
City Engineer, Memorandum to Ms. Adena Friedman, Senior Planner. November 14, 2015).
1.The building permit application plans shall conform to the stand
Divisions Building Permit Typical Plan Check Submittals requi
which are available from the Engineering Division.
2.The owner shall hire a licensed land surveyor or civil engineer authorized to practic
surveying to certify that the new foundation forms for the new s
conform with all setbacks shown on the approved building permit
from confirmed property lines and that any easements are verified
with recorded documents. A letter certifying that the foundatio
correctly shall be submitted to the Engineering Division for app
the proposed new buildings foundations.
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3.The owner shall, at his/her expense, repair any broken sidewalk,
curb, and gutter along the entire frontage of the property, prior to r
inspection for the new building.
4.The owner shall install a City Standard property line sewer cleano
City Standard Drawings, so that the building sewer lateral can b
work shall be accomplished at the applicants cost.
5.The owner shall, at his expense, design and construct a drainage system that will route
storm water run-off from the new buildings roof areas and shall be collected wi
property and directed towards the public street gutter. Downspouts must first discharge
to landscaping before directing it towards the public street and cannot be dire
plumbed to the storm water system. Storm water generated from th
into adjacent private property or across the public sidewalk.
6.Due to the geotechnical sensitivity of the Project, the owner shall contact the Citys
geotechnical consultant, Cotton Shires & Associates, to provide
and inspection services before and during the construction of th
shall place a $25,000 deposit forgeotechnical services rendered to the owner. Should the
cost of geotechnical services exceed the deposit, the owner shal
for any additional costs.
7.Prior to obtaining the building permit, the owner shall obtain ahe
owner shall pay all associated fees and deposits for the grading
8.Any work to be performed in the Citys right-of-way shall require an encroachment from
the Engineering Division. The owner shall apply for and pay all fees and deposits for the
encroachment permit.
GRRC
EOTECHNICAL EPORTS EQUIRED BY ITY
The City Engineering Division requires geotechnical reports as a
projects to be constructed on vacant land, demolition and rebuil, and additions to buildings
that require grading and additional loading (see Chapter 1, Section 5). Geotechnical reports are
required to be prepared by a licensed geologist, geotechnical en
The reports include a detailed site characterization study, an analysis of potential hazards and
design specifications to mitigate the potential hazards.The reports identify design and
construction specifications for (among other items) grading, site stabilization, drainage, utility
and infrastructure design and placement, foundation design, retaining wall specifications and
placement, and soil compaction requirements. The reports are peer reviewed by the Citys
geotechnical consultant and are often modified through this process. The final geotechn
report is required to incorporate the modifications recommended by the Citys consultant and
the project is required to be built as identified through this p. The types of grading and
construction methods that are required reduce geotechnical impacts (i.e., expansive soils,
liquefaction, differential settlement, severe ground shaking, etc.) to the maximum extent
technically feasible.
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The Applicants geotechnical consultant is GeoTrinity and the Citys is Cotton Shires Associates
(CSA). The site characterizationand methods by which to grade and construct the Project was
conducted by GeoTrinity and peer reviewed by CSA. CSA provided t
that the geotechnical issues were adequately characterized by Ge
methods necessary to reduce geotechnical hazards to the maximum extent technically feasible
will reduce geotechnical impacts to less than significant (Octob
Appendix A).
As excerpted from the October2, 2015letter by CSA:
The applicant proposes to construct a three-story, single-family residence on an
undeveloped hillside lot at the western end of Larch Avenue. The
daylighting basement including the garage. In our previous peer
May 26, 2015), we recommended that seven geotechnical comments be satisfactorily
addressed prior to geotechnical approval of site layout or build
time, revised site development plans for a somewhat smaller resi
prepared.
RECENT GEOLOGIC AND GEOTECHNICAL EVALUATIONS
The Project Geotechnical Consultant (GTC) has responded to all comments of our
previous geotechnical peer review. GTC has concluded that projec
the eastern property line will not affect the adjacent existing house. The Consultant has
recommended that proposed retaining walls to be located below th
fill wedge should include a minimum of 2 feet of freeboard (west
Final plans are to include surface drainage ditches atop retaining walls along the
southwestern and southeastern sides of the residence. Installati
catchment fence has been recommended along the eastern property
downslope of the excavation work. An estimated project construct of
April 2016 has been presented.
CONCLUSIONS AND RECOMMENDED ACTION
The Project Geotechnical Consultant has adequately responded to
recommendations of our previous geotechnical peer review. We rec
geotechnical approval of applications associated with proposed site development
with the following conditions:
1.Final Design Plan Details Final project construction plans shall include
retaining walls with a minimum of 2 feet of freeboard on the dow
side of the existing fill wedge along the western edge of the property and
surface drainage ditches should be detailed atop retaining walls
southwestern and southwestern sides of the residence (per GTC,
September 23, 2015). Prior to initiation of grading, a temporary
fence shall be installed along the eastern property line and downslope of
the excavation work (per GTC direction).
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2.Geotechnical Construction Inspections -The geotechnical consultant
should inspect, test (as needed), and approve all geotechnical a
project construction. The inspections should include, but not necessari
be limited to: site preparation and grading, site surface and s
drainage improvements, and excavations for foundations and retai
walls prior to the placement of steel and concrete.
The results of these inspections and the as-built conditions of the project
should be described by the geotechnical consultant in a letter a
submitted to the City Engineer for review prior to final (granti
occupancy) project approval.
The Applicant proposes all the requirements of both GTC and CSA as part of the Project. The
required measures are identified in Chapter 2, Project Description. Appendix A and contain a
document signed by Applicant attesting to understanding the meashey are proposed
as part of the Project, and they will be included on the building permit plan set that w
on the Project site from commencement to completion of grading and construction activities
(Environmental Mitigation Measures [proposed by Applicant], Vinal Nand. December 2, 2015).
Moreover, Ms. Adena Friedman, Senior Planner will also include a
requiring the Applicant to incorporate all the measures listed i
The letter addresses biology, geology, and noise measures to reduce Project impacts to less than
significant (as vetted in the Chapter 3 Sections 3.5, 3.7 and 3.13).
The Project geotechnical reports and peer review are listed below, used to analyze geologic and
soils impacts and located in full in Appendix A.
Applicants Reports GeoTrinity
GeoTrinity Consultants, Inc., Geotechnical and Geologic Investigation, Residential Development
901 Larch Avenue, South San Francisco, California. May 1, 2015.
GeoTrinity Consultants, Inc., Supplemental Letter for May 2015 Report and August 6, 2015
Plans.August 18, 2015.
GeoTrinity Consultants, Inc., Response to Peer Review Letter. September 23, 2015.
City Peer ReviewCotton Shires Associates
Cotton Shires Associates, Inc., Geotechnical Peer Review, Nand New Residence, 901 Larch
Avenue. May 26, 2015.
Cotton Shires Associates, Inc., Supplemental Geotechnical Peer Review, Nand New Residence,
901 Larch Avenue. October 2, 2015.
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SGC
ITE EOLOGIC HARACTERIZATION
Previous Site Characterization
As summarized by GeoTrinity (May 2015), Earth Mechanics Consulting Engineers (EMC)
performed a geotechnical investigationbased on a schematic site plan showing only the
footprint of a proposed residence on the site. EMCs investigation included a boring near the
center of the building site that was drilled andsampled to adepth of 15 feet. The subsurface
materials encountered consisted of native soil to a depth of two feet overlying bedrock to
the bottom of the boring. The soil consisted of clayeysand,andthe bedrock consisted of
sandstone with minor siltstone. The location of the boring byGruen(2000, see Appendix A)
is shown in Figure 3 in Appendix A, along with a copy oftheir boring log. CSA conducted a
2002 peer review on behalf of the City.
A 2003 report by Gruen and Peterson provided additional geologic conclusions,
including verbal and graphic descriptions of surficial condition
review letter by CSA presented geologic and engineering comments on the 2003 report by
Gruen and Peterson andon the gradingand construction thatwasproposed at that time.
2015 Site Characterization
The vacant site is located on a northwest-plunging ridge spur of Sign Hill. Elevations on the
property vary from 476 feet in the southern corner to 404 feet in thenorthern corner. (Note:
GeoTrinitys elevations are adjusted using mean sea level as the
north at an overall gradient of 2¼ H:lV but varies from2 ½ H:1V in the southern (uphill) half
of the property to approximately l H:1V in thecentralportion and 5H:1V in the northern
corner of the property, near Larch Avenue. GeoTrinity surmises t
property was steepened and lowered from the cut and grading ofLarchAvenue in the mid-
20th century. This onsite grading was blended into the cut for theneighboringproperties to
the southwest and northeast.
GeoTrinity observed surface evidence of two minor feet across by 2 feet
deep) recent earthflowscars at approximate 425 foot elevation, near the crest of the s
slope. A similar scar was mapped at approximately a 440 foot elevation on the neighboring lot
tothe southwest where once was located a water storage tank. Thesearthflows
evidently produced shallow earthflow deposits along the base of the slope; their limits are
obscured by vegetation and are conjectured by GeoTrinity. There of
water on the pad where the former water tank was located. GeoTried no evidence
of significant erosion aside from the aforementioned earthflow scars.
Bonilla (1998, see Appendix A) mapped the geology of a large area that includes the subject
site. The Project site is underlain by Cretaceous to Jurassicsandstone and shale bedrock of
the Franciscan Complex and associated rocks. The landslide map of the area by Bonilla (1960
shows no landslides on or appreciably near the site.
GeoTrinity observed six exposures of the bedrock in four artific
outcrops nearthe site. These exposures and the boring by Gruen (2000) also indicate that the
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bedrock consistsofCretaceous to Jurassic sandstone and siltstone. This bedrock underlies
the Project site above approximately a 430 foot elevation. GeoTrinity estimates that soft to
hard, massive (very thickly bedded) sandstone comprises approx
and very soft, thinly bedded siltstonecomprises theremainder. The northern third of the
site is generally underlain by the unitofPleistocene slope wash and ravine fill deposits of
Bonilla (1998). This material likely thickens downslope (to the north) to adepth of 5-10
feet below the ground surface in the northern comer of the site. The materialconsists of
dark yellowish (nearly reddish) brown, dense, silty sand with subangular rock fragments
up to two inches in diameter derived from older sandstone bedroc
material. GeoTrinity notes excavated blocks ½ foot in diameter w
several weeks; however their outer surfaces will melt (slake) whe
to 0.4 inches). Colluvium blankets the bedrock to a depth of app1½ feet consisting
of gray gravelwith sand and clay.
There is a wedge of fill on the neighboring propertytothe southwest. The fill was placed to
create a level pad for the former 50,000-gallonwater tank, is approximately 4 feet thick, and
presumably consists ofgravelly (angularfragmentsderived frombedrock), sandy soilthat was
placed atop the colluvium.
Thin earthflow deposits blanket the low lying part of the site. The lens of material consists of
loose gravellysandand is anestimated2feetthick. GeoTrinity observed no evidence of
landslide deposits on or appreciably near the site, and no such deposits were
documented intheprevious work based on the topography and subsurface exposures.
Free groundwater was not encountered in the boring drilled and logged by Gruen (2000), nor
wasany seepageobserved during GeoTrinity site visits inMarch, andApril, 2015. These
conditions, were observed during dry times of year, and it may be expected t
stormwaterrunoff may infiltrate the subsurface and saturate the ground, wh
filling of andconsequent seepage from fractures in the bedrock. Fluctuations in
groundwater levels willoccur due toseasonal changes, variations in rainfall, and other factors.
GeoTrinity documented rock discontinuities near the site at fourat
exposerelatively fresh rock. Additionally, two major discontinuities i
weredocumented in two outcrops nearby (see Appendix A). GeoTrinitys analysis focused
on potential adverse conditions and potentialeffects on the Project and neighboring
properties. Potential adverse conditions include wedge failures resulting from daylighting of
shears (faults), bedding, and other discontinuities joints in the proposed excavated cuts. No
shears were observed.
Fracturing throughout the site and area is generally intense to very intense, particularly in
the siltstone, although the siltstone beds are generally less than 1 foot thick
approximately 5% of the rock mass in general. The joint patterns are also such th
primary joints in agiven exposure can be traced more than a few feet and the remainare
essentially randomly oriented and discontinuous. The blocks of rock between
are cut by veryclosely spaced fractures thatextendno more thanafew inches and appearto
be randomlyoriented. Allofthe discontinuities generally display very thin coatings of iron and
manganese oxides and are otherwise tight. According to CSA, there is nearby competent
bedding exposed above the Project site and underlying the steep slope at Sign Hill. These
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bedded rock materials are fractured but not intensely fractured.
fractured intensely enough to cause settlement issues or other f
potential for unstable rocks at the site comes primarily from the intersection of joints with
bedding, and fractures may be induced into the rock as part of t(Ted Sayre
electronic mail, December 9, 2015).
SF
EISMIC AULTS
No active earthquake faults have been recognized within the immediate site area. Although the
site and vicinity is believed to be free of active faults, the S
within a seismically active region. The dominant fault in this
located about 2.9 miles northwest of the site. Other active faults in the area include the Sa
Gregorio fault located roughly 7.5 miles westand the Hayward-Rodgers approximately 15.7
miles northeast.
The Hillside fault, a northwesterly-trending escarpment aligned with a zone of sheared rocks on
the knoll of Point San Bruno just south of Oyster Point, has als
from the Project site. Until the late 1990s this fault was cons
Subsequent geophysical studies conducted in the late 1990s using a more accurate high-powered
deep-penetrating sonar system found no evidence suggesting that the H
active. Moreover, geologic observations of the Hillside fault eaded cuts
on San Bruno Mountain did not detect any recognizable offsets of
current fault rupture hazard. Therefore, there is no evidence t
within geologically recent time; however, it may be possible for sympathetic movements to be
imposed on this fault as a result of stress from major earthquak
San Andreas and Hayward-Rodgers faults.
I
MPACTS
Seismic Hazards
Seismic hazards are generally classified as two types, primary and secondary. Primary geologic
hazards include surface fault rupture. Secondary geologic hazard
liquefaction, dynamic densification and seismically induced grou
i)Surface Fault Rupture
Significance Criteria: The Project would have a significant environmental impact if it w
expose people or structures to potential substantial adverse eff
rupture of a known earthquake fault.
There are no active faults underlying the site and the nearest one is the San Andreas Fault,
located about threemiles southwest. The Hillside fault is located nearby, but there is no evidence
that this fault has been active within geologically recent time.The Project would have no
impact on exposing people or structures to danger from surface rupture of a known
earthquake fault.
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ii) Strong Seismic Ground Shaking; iii) Liquefaction; c) Geologic Instability and d)
Expansive Soils
Significance Criteria:
Strong Seismic Ground Shaking: The Project would have a significant environmental
impact if it were to expose people or structures to potential su
associated with strong seismic ground shaking.
Liquefaction: The Project would have a significant environmental
expose people or structures to potential substantial adverse eff
seismic-related ground failure, including liquefaction.
Geologic Instability: The Project would have a significant envir
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.
Expansive Soils: The Project would have a significant environmental impact if located on
expansive soil, creating substantial risks to life or property.
Given that there are no active faults within the Project site, d
likely to occur from the secondary impact of strong seismic groud shaking originating on a
nearby fault. Estimates of actual ground shaking intensity at a
according to the Modified Mercalli Intensity Scale, which accoun
and distance from the earthquake. For the Project site, Mercalli Intensity estimates indicate that
earthquake-shaking intensity would vary depending upon where the seismic ev
For the Maximum Credible Earthquakes (MCE) along the nearby San
Gregorio faults (Richter Magnitude 7.9 and 7.4, respectively) the shaking intensities would be IX,
violent and VIII, very strong, respectively, at the Project (Association of Bay Area
Governments, Seismic Hazard Maps).
GCR identified the following seismic requirements for the Project, CSA peer reviewed and
stated The Project Geotechnical Consultant has adequately respo
of our previous geotechnical peer review. (CSA October 2, 2015)
proposes the following measures GeoTrinity identified as part of the Project (see Appendix A),
excerpted from Chapter 2, Project Description.
GCR developed site-specific spectral seismic design parameters are based on the
2012 International Building Code,which is based on U.S. Geological Survey
hazard data available in 2008. Thesedesignparameters are for use by the structural
engineer when addressing potential seismic shaking indesigning theproposed
residence, including retaining walls.
Based on the specific site location by latitude and longitude, Ss and S1 are 2.092 g
and 0.991 g,respectively. GCR classified the site as Site Class C, i.e., softrock,
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basedonitsdensefracturepattern and an estimated average blow count value)
(N
of 90 in the 0-100-foot depth intervalbelow the site.
Based on thesitelocation andspecificSiteClass C,GCR developed the seismic design
parameters,summarized in Table 4, below:
PDT4
ROJECT ESCRIPTION ABLE
PSDP
ROJECT EISMIC ESIGN ARAMETERS
PARAMETER VALUE
S 2.092 g
MS for 0.2-second period
S1.288 g
M1 for1.0-second period
S1.394 g
DS for 0.2 -second period
S 0.859 g
D1 for 1.0-second period
The Project would result in a less than significant impact assocsevere
groundshaking with implementation of the measures required by law and proposed as
part of the Project.
Liquefaction is a secondary seismic hazard involving saturated cohesionless s
sediments located close to the ground surface. Liquefaction occurs when the strength of a soil
decreases and pore pressure increases as a response to strong seismic shaking and cyclic load
During the loss of strength, the soil becomes mobile, and can mo
vertically, if not confined. Soils most susceptible to liquefact
uniformly-graded, fine-grained sands.
The Project site would not likely experience seismically induced liq
According to GeoTrinity (May 2015), the potential for liquefaction is low based upon the
presence of bedrock and dense underlying soils. Project impacts associated with
liquefaction would be less than significant.
Expansive soils contain minerals such as smectite, bentonite, mo
vermiculite, attapulgite, nontronite, illite,and chlorite. There are also some sulfate salts that will
expand with changes in temperature. When a soil contains a large
it has the potential of significantexpansion. When the soil contains very little expansive
minerals, it has little expansive potential. The clays are capable of absorbing water and as they do
so they increase in volume. The more water they absorb the more
Expansions of ten percent or more are not uncommon. The change in volume can exert
enough force on a building or other structure to cause damage. Cracked foundations, floors and
basement walls are typical types of damage done by swelling soil Damage to the upper floors
of the building can occur when motion in the structure is signif Expansive soils will also
shrink when they dry out. This shrinkage can remove support from buildings or other struct
and result in damaging subsidence. Fissures in the soil can also develop. These fissures can
facilitate the deep penetration of water when moist conditions ounoff occurs. This produces a
cycle of shrinkage and swelling that places repetitive stress on.
The Project site would not likely experience impacts from expansive soils. According to
GeoTrinity (May 2015), the site does not contain expansive materials such as smectite,
bentonite, montmorillonite, beidellite, vermiculite, attapulgite, and
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chlorite or sulfate salts.Project impacts associated with expansive soils would be less
than significant.
As noted in Chapter 2, Project Description and in the site characterization study above
(GeoTrinity, May 2015),spalling rocks during construction could tumble down the site anon
to adjacent property. According to Ted Sayre, (CSA, Principal Engi
would likely be less than 8 inches in diameter. At the behest of CSA, GeoTrinity designed a
rockfall fence (catchment device) to catch rocks and protect theresidence at 859
Larch Avenue.The Applicant as shown in Chapter 2,Project Description and Appendix A
proposes the following as part of the Project.
Final Design Plan Details
Final Project construction plans will include retaining walls w
2 feet of freeboard on the downslope side of the existing fill w
western edge of the property and surface drainage ditches will be detail
retaining walls on the southwestern and southwestern sides of th
GeoTrinity, September 23, 2015). Prior to initiation of grading, a tempora
catchment fence will be installed along the eastern property line and downslope
of the excavation work (per GeoTrinity direction).
Geotechnical Construction Inspections
The GCR will inspect, test (as needed), and approve all geotechn
Project construction. The inspections will include, but not necessarily be limited
to: site preparation and grading, site surface and subsurface d
improvements, and excavations for foundations and retaining wall
placement of steel and concrete.
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The results of these inspections and the as-built conditions of the Project will be
described by the GCR in a letter and submitted to the City Engin
prior to City granting a Certificate of Occupancy.
Engineering Condition of Approval #6, above, also requiresCSA review, inspections and
recommendations, as necessary. The requirement for CSA to be on
Applicant and proposed as part of the Project as shown in the following (see Appendix A, page
2, Nand).
Detailed earthwork and foundation requirements for use in design and
construction of therojectwill be implemented. GCR (or qualified successor)
will review the final design andspecificationsto assure quality control. GCR will
be on site full time during the initial gradingand intermittently during the remaining
site work. GCRwill as necessary make changes to practices and methods to assur
safety and stability of the Project and adjoining properties. CSA will be present on the
Project site intermittently to oversee grading operations.
The Project would have less than significant impacts associated with a geologic unit
becoming unstable by implementing the measures identified by the Project geotechnical
engineer, as modified by the Citys geotechnical consultant and as proposed by the
Applicant.
iv) Landslides
Significance Criteria: The Project would have a significant environmental impact if i
expose people or structures to substantial hazards from landslid
A landslide is a mass of rock, soil and debris displaced down slope by sliding, flowing or
falling. As noted above, Bonilla (1998, see Appendix A, GeoTrinity, May 2105) mapped the
geology of a large area that includes the subject site. The Project site is underlain by
Cretaceous to Jurassic sandstoneand shale bedrock of the Franciscan Complex. Design
criteria for foundations, footings, retaining walls, soil compac
part of the Project; all serve to stabilize the site. The landslide map of the area by Bonilla
(1960) shows no landslides on or appreciably near thesite. The Project would have a less
than significant impact with respect to landslides.
b) Erosion or Loss of Topsoil
Significance Criteria: The Project would result in a significant environmental impact i were to
result in substantial soil erosion or in the loss of topsoil.
The Project would require grading, and export of soil as well asof piles. The Citys
requirements for a grading permit and material export (noted in conditions of approval #7
above) requires various vehicular and pedestrian safety measures
site (such as soil on tires or falling out of dump trucks). In absence of the NPDES C-3
requirements enforced by the City as a condition of building and grading permit issuance the
Project would have a potential to increase erosion during constrThe NPDES
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requirements are required and enforced by the CitysEngineering Division to reduce impacts
associated with soil erosion and water pollution during both construction and operation of
projects. These requirements are described in detail in Section 3.9, Hydrology and Water
Quality and in Chapter 1, Section 5.Erosion control measures are required as a matter of
law and as a result this impact is considered to be less than significant.
e) Capability of Soils to Support Septic Tanks
Significance Criteria: The Project would have a significant environmental impact if i
construction of septic systems in soils incapable of adequately he use of septic tanks
or alternative wastewater disposal systems.
The Project does not propose to build any new septic tank or alt
The Project site would be connected to the citys sanitary sewer system. The Project would
have no impact on soils due to septic systems as the Project would be connected to the
Citys wastewater system.
Geology and Soils Finding: There are no active faults underlying the site and the nearest
one is the San Andreas Fault, located about 2.9 miles southwest. Implementation of the
geotechnical measures required by law (the Citys standard permitting requirements for peer
review of all geotechnical reports and the final recommendations
Project) are proposed as part of the Project and identified in the CEQA document. Detailed
earthwork and foundation requirements for design and constructiowill be
implemented. GeoTrinity (or qualified successor) will review the final design and specif
to assure quality control. GeoTrinity will be on site full time during the initial grading and
intermittently during the remaining site workand will as necessary make changes to practices
and methods to assure the safety and stability of the Project an. CSA will
be present on the Project site intermittently to oversee grading
measures identified by GeoTrinity and CSA would reduce geologic instability to less than
significant. The Project would have no impact on soils due to septic systems as the Project
would be connected to the Citys wastewater system.
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3.8HHM
AZARDS AND AZARDOUS ATERIALS
Potentially Less Than Less Than
Significant Significant Significant No
with
Impact Impact Impact
Mitigation
Would the Project:
a) Create a significant hazard to the public or X
the environment through the routine
transport, use, or disposal of hazardous
materials?
b) Create a significant hazard to the public or
X
the environment through reasonably
foreseeable upset and accident conditions
involving the release of hazardous materials
into the environment?
c) Emit hazardous emissions or handle
X
hazardous or acutely hazardous materials,
substances, or waste within one-quarter mile
of an existing or proposed school?
d) Be located on a site which is included on a
X
list of hazardous materials sites compiled
pursuant to Government Code Section
65962.5 and, as a result, would it create a
significant hazard to the public or the
environment?
e) For a Project located within an airport land
X
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
result in a safety hazard for people residing
or working in the Project area?
f) For a Project within the vicinity of a private
X
airstrip, would the Project result in a safety
hazard for people residing or working in the
Project area?
g) Impair implementation of or physically
X
interfere with an adopted emergency
response plan or emergency evacuation
plan?
h) Expose people or structures to a significant
X
risk of loss, injury or death involving
wildland fires, including where wildlands are
adjacent to urbanized areas or where
residences are intermixed with wildlands?
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S
ETTING
The Project site, 901 Larch Avenue is vacant and located at the
it intersects Larch Avenue, on the north facing slope of Sign Hill (s ee Project Description
Figures1 ProjectArea and2 Project Location inChapter 2). The Project is located within a
residential neighborhood consisting of single-family detached structures in the Sterling Terrace
subdivision. The northern and northeastern facing slopes of Sign Hill, consis
approximately 46 acres, are in private ownership. Sign Hill Park is located on the south facing
slopes of the hill, is owned by the City and is public park and recreation land.
The Project would construct a single-family residence consisting of approximately 2,500 square
feet. Construction is proposed on the front thirdof the lot. Landscaping is proposed in the
front, side and portions of the rear of the property. Japanese Maple, Winter Boxwood, Star
Jasmine, camellia, and lavender are proposed (see Figure 2, Project Description).
SR
ENSITIVE ECEPTORS
Residential, schools, child care facilities, schoolsand convalescent facilities are typically
considered sensitive land uses. Heavy commercial and industrial land uses are typically
considered potential sources of toxic or hazardous materials. The Project and the neighborhood
within which it is located are considered sensitive receptors.
RF
EGULATORY RAMEWORK
As noted above, the Project is considered a receptor and not a generator of haza
The following regulatory framework is provided for informational purposes. Hazardous
materials use, storage, and disposal aregoverned by the following standards and permitsat both
the federal and state level.
F
EDERAL
Toxic Substances Control Act, administered by the EPA, Regulatio, Part 720.
o
Hazardous Materials Transportation Act, administered by the Depa
o
Transportation, Regulation 49 CFR 171 et seq.
Resource Conservation and Recovery Act (RCRA) 42 U.S.C. 6901 et seq.
o
Hazardous Waste Management Standards for Generators, Transporters, and Waste Facilities,
o
administered by EPA, 40 CFR 260 et seq.
Occupation Safety and Health Act, 29 U.S.C. 651.
o
Workplace Exposure Limits, administered by Occupational Health a
o
Administration. 29 CFR 1900 et seq.
S
TATE
California Hazardous Waste Control Act. California Health and Safety Code, Div
o
Chapter 6.5.
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California Hazardous Waste Management Regulations. California Code of Regulations, Title
o
22. Social Security, Division 4. Environmental Health.
California Occupational Safety and Health Act, California Labor Code sections 6300 et seq.
o
R
EGIONAL
The San Mateo Department of Environmental Health (SMCDEH) largel
permitting or remediation agency through various memoranda of un
state, regional agencies,and local government. Often the Regional Water Quality Control
(RWQCB) and/or the Bay Area Air Quality District (BAAQMD) take a lead or partnership in
site remediation with the SMCDEH. Chapter 1, Legislative Framework identifies the
procedures to remediate hazardous materials, soils, water or releases that are levied by federal,
state and local authorities.
SSF
OUTH AN RANCISCO
The South San Francisco Fire Department (SSFFD) requires businesses using or transporting
hazardous substances to provide a Hazardous Materials Business Plan (H
and approval. SSFFD reviews development and entitlement applications, levies
code requirements for fire prevention and safety,and conducts periodic inspections of business
activities.
Fire Marshal, Luis Da Silva reviewed the Project plans and provided the follow
Project Approval (June 22, 2015 memorandum to Ms. Rozalynne Thompson, Associate
Planner).
1.Install fire sprinkler system per National Fire Protection Agency (NFPA) 13D/SSFFD
requirements under separate fire plan check and permit for overh
2.Fire sprinkler system shall be central station monitored per Cal
1003.3.
3.Fire alarm plans shall be provided per NFPA 72 and the City of South San Francisco
Municipal Code.
4.Install exterior listed horn/strobe alarm device, not a bell.
5.Provide fire extinguishers throughout the building.
6.All buildings shall provide premise identification in accordancewith SSF Municipal Code
section 15.24.010.
7.The fire hydrants shall have a minimum fire flow of 2000 gpm at
for duration of 2 hours.
8.Provide fire hydrants with an average spacing of 400 feet betwee
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9.Provide location of new and existing fire hydrants.
10.This new residential construction will be assessed a recently ad
Impact Fee. The amounts for low density are $385.50 per unit for the Police Department
and $899.50 per unit for the Fire Department.
11.All buildings shall have Emergency Responder Radio Coverage throughou
compliance with Section 510 of the California Fire Code.
12.Provide a minimum space of 20 feet to the rear of the property t
The 20 foot clear space (vegetation/fire break) shall be measured from the rear elevation
of the residence including the deck and stairway (i.e., all buil
residence). The 20 foot vegetation/fire break may include fire r-invasive
plantings that reach a maximum of one foot in height at maturity. Trees may be planted
25 feet from the rear elevation of the structure and beyond but
break. Irrigation in the vegetation/fire break is preferred to a
this area from fire.
The Fire Marshal did not identify staffing and service impacts with respect to site development.
SSFGP
OUTH AN RANCISCO ENERAL LAN
The South San Francisco General Plan contains many maps and figures identifying areas with special
risks. One such figure is Figure 8-4 Fire Hazard Management Units identifying High Priority Fire
Management Zones (SSF GP, 1999, p. 265). The Project site is not identified as being within a
High Priority Fire Management Zone; however it is adjacent to one.
I
MPACTS
a) and b) Hazardous Materials
Significance Criteria: The Project would have a significant environmental impact if i
a significant hazard to the public or the environment through th
disposal of hazardous materials or if it were to create a significant hazard to the public or th
environment through reasonably foreseeable upset and accident co
of hazardous materials into the environment.
Operational Impacts
The Project is considered a sensitive receptor. The Project would not handle large amounts
hazardous materials as a course of everyday activities such as traveling to and from the site in
vehicles (gasoline or electrically powered) or using lawnmowers
for landscaping. Project operational impacts with respect to a release of hazardous
substances or materials would be less than significant.
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Construction
Construction related impacts involve the use of gasoline and diesel powered equipment. A
hazard risk assessment was conducted and fully vetted in Chapter 3, Section 3,Air Quality,
above (see Air Quality,Tables 3 and 4). Construction activities would entail the use of diesel
equipment that generates emissions of DPM, which the CARB has categorized as a human
carcinogen.
As noted in Chapter 3, Section 3,Air Quality typically, health risks are estimated based on a
lifetime exposure period of 70 years. Because exhaust emissions
activities of the Project would be very low and short-term in nature (approximately 32 to 44
weeks depending on the contractors work schedule, it is anticipated that exposure to
construction-related DPM would not result in an elevated health risk.The Project is required
by law to implement the conditions of approval identified in Chapter 1, Legislative
Framework and poses a less than significant impact to the enviro
residing therein during construction.
c) and d) Hazardous Materials Presence
Significance Criteria: The Project would have a significant environmental impact if it were to emit
hazardous emissions or handle hazardous or acutely hazardous mat
within a quarter mile of an existing or proposed school, or if i
included on a list of hazardous materials sites compiled pursuant to Gosection
65962.5 (Cortese List).
CSS Environmental Engineering reviewed the location of the Proje
hazardous sources that affect the area and the Project site. The closest source is approximately
¾ mile downstream and southeast of the Project (Aaron N. Stessman, PE, Principal Engineer,
CSS Environmental Services, Inc. November 5, 2015). Mr. Stessman opines that the potential
presence of hazardous material that could affect the site is very remote. Additionally tProject
site is not listed on a Cortese List.
The Project site is within a ¼ mile of a school. The Project isnot a source of hazardous
materials or the handling thereof. The Project would have no impact from the emission or
handling of hazardous materials or wastes on schools or from any
contamination posed by the sites listed on the Cortese List.
e) and f) Safety Hazards Due to Nearby Airport or Airstrip
Significance Criteria: The Project would have a significant environmental impact if it
within an airport land use plan (or, where such a plan has not b
a public airport or public use airport), if it would result in aard for people residing or
working in the Project area; or if it were located within the vi
would result in a safety hazard for people residing or working i
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San Francisco International Airport is approximately 2.5miles southeastof the site. The Project
site is not within the San Mateo County Airport Land Use Commissions (ALUC) and ALUC
Plan Area jurisdiction. The Project is not within 2 miles of a private airstrip. There would be
no impact associated with the location ofairports and airstrips.
g) Conflict with Emergency Response Plan or Emergency Evacuation
Significance Criteria: The Project would have a significant environmental impact if it
implementation of, or physically interfere with, an adopted emergency response plan or
emergency evacuation plan.
There are no emergency response or evacuation plans in effect in
The Project would have no impact on the implementation of any ad
response plan or emergency evacuation plan.
h) Exposure of People or Structures to Wildland Fires
Significance Criteria: The Project would have a significant environmental impact if it
expose people or structures to a significant risk of loss, injurr death involving wildland fires.
The Setting Section,above, lists the 12 conditions of Project approval identified by Fire
Marshal Da Silva. The Project site is not identified as being within a High Priority Fire
Management Zone (SSF GP, 1999, p. 265). The Project is however adjacent to a High Priority
Fire Management Zone.
The Project is required by law to implement the 12 conditions of
Marshal Da Silva. The measures include a 20 foot irrigated fire buffer, fire hydra an alarm
and smoke detectors, emergency communications, fire extinguisher, and fire sprinklers in the
buildings; all designed to reduce the likelihood of and suppress. Project impacts relating
to fire protection would be less than significant with implementation of the conditions of
approval required by law.
Hazards and Hazardous Materials Finding: The Project is a sensitive receptor and not a
source of hazardous materials. The Project would have no impact from the emission or handling
of hazardous materials or wastes on schools within a quarter of a mile or from any
environmental contamination posed by the sites listed on the Cor. The operational
impact of the Project with regard to the use of hazardous materials would be less than significant
and similar to other residential uses in the neighborhood. The Project as proposed would have a
less than significant impact with respect to the release of haza
construction.
There are no emergency response or evacuation plans in effect in the Project vicinity. Therefore
the Project would have no impact on the implementation of any ad
plan or emergency evacuation plan. The Project is not within 2 miles of an airport or air strip
and would have no impact on such use. Project impacts relating to fire protection would b
than significant with implementation of the conditions of approv
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3.9HWQ
YDROLOGY AND ATER UALITY
Potentially Less Than Less Than
Significant Significant Significant No
with
Impact Impact Impact
Mitigation
Would the Project:
a)Violate any water quality standards or waste X
discharge requirements?
b) Substantially deplete groundwater supplies
X
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 (e.g., the
production rate of pre-existing nearby wells
would drop to a level which would not
support existing land uses or planned uses
for which permits have been granted)?
c) Substantially alter the existing drainage X
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?
d)Substantially alter the existing drainage X
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 off-site?
e) Create or contribute runoff water which X
would exceed the capacity of existing or
planned stormwater drainage systems or
provide substantial additional sources of
polluted runoff?
f) Otherwise substantially degrade water
X
quality?
g) Place housing within a 100-year flood hazard X
area as mapped on a federal Flood Hazard
Boundary or Flood Insurance Rate Map or
other flood hazard delineation map?
h) Place within a 100-year flood hazard area X
structures, which would impede or redirect
flood flows?
i) Expose people or structures to a significant
X
risk of loss, injury or death involving
flooding, including flooding as a result of the
failure of a levee or dam?
j) Inundation by seiche, tsunami, or mudflow?
X
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S
ETTING
Colma Creek, the Citys main natural drainage system, is a peren
about 16.3 square miles that trends in a roughly southeasterly d
City. The Colma Creek watershed is one ofthe three largest in the County. The basin is
bounded on the northeast by San Bruno Mountain and on the west b
Boulevard. Dominant topographic features of the drainage basin
mountain ridges that diverge toward the southeast that are connected by a low ridge a
northern boundary of the area. The valley enclosed by the ridge
where it drains into San Francisco Bay.
Flood hazard areas identified on the Federal Emergency Management Agency (FEMA) Flood
Insurance Rate Map (FIRM) are identified as a Special Flood Haza
defined as the area that will be inundated by the flood event ha-percent chance of
being equaled or exceeded in any given year. The one-percent annual chance flood is also
referred to as the base flood or 100-year flood. SFHAs are labeled as Zone A, Zone AO, Zone
AH, Zones A1-A30, Zone AE, Zone A99, Zone AR, Zone AR/AE, Zone AR/AO, Zone
AR/A1-A30, Zone AR/A, Zone V, Zone VE,and Zones V1-V30. Moderate flood hazard areas,
labeled Zone B or Zone X (shaded) are also shown on the FIRM, an
limits of the base flood and the 0.2-percent-annual-chance (or 500-year) flood. The areas of
minimal flood hazard, which are the areas outside the SFHA and higher than the elevatio
0.2-percent-annual-chance flood, are labeled Zone C or Zone X (unshaded).
Areas subject to inundation by the one-percent-annual-chance flood event are generally
determined using approximate methodologies. Because detailed hydraulic analyses have
performed, no Base Flood Elevations (BFEs) or flood depths are s
insurance purchase requirements and floodplain management standa
The Project site is located in Zone X (unshaded); an area of minimal flooding.
RF
EGULATORY RAMEWORK
F
EDERAL
National Pollutant Discharge Elimination System Storm Water Disc: As
identified in Chapter 1, Section 1.5.5, the City of South San Francisco is a member of the San
Mateo Countywide Storm Water Pollution Prevention Program (STOPP
the City/County Association of Governments (C/CAG) of San Mateo
National Pollutant Discharge Elimination System (NPDES) Storm Warge permit.
STOPPP's goal is to prevent polluted storm water from entering c
Francisco Bay. The City requires the implementation of Best Man
Low Impact Development (LID) measures for new developmentand construction as part of its
storm water management program, as levied through standard City
approval.
The City requires the implementation of BMPs and LID measures to
water quality in storm runoff from the Project site. In brief, the measures presented in the BMP
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handbook address pollution control and management mechanisms for
structure construction, material delivery and storage, solid was
subcontractor training, etc. The handbook also provides direction for
sedimentation,as well as the establishment of monitoring programs to ensure th
of the measures. The City also requires an agreement with the Applicantthat ensures the
permanent and on-going maintenance of water quality control improvements by the Applicant
and/or project site owner(s). Refer to the Bay Area Storm Water
Association (BASMAA) Start at the Source Design Guidance Manual for Storm Water Quality Protection
(available from BASMAA)for a comprehensivelisting of required measures. Typical storm
water quality protection measures are identified in Chapter 1, Section 1.5.4 of this document.
The Citys requirements are in compliance with state and federal laws and regulations that are
designed to mitigate potential hydrological and stormwater impacts associated with project
construction and on-going operational activities.
S
TATE
State Water Quality Control Boards General Permitting Requirements: As identified
above and in Chapter 1, Section 1.5.5, the City of South San Francisco requires thorough
conditions of project approval, project compliance with the Stat
general permitting requirements which require the Applicant to secure a Construction Activities
Storm Water General Permit, complete a Notice of Intent (NOI) an
approval of a Storm Water Pollution Prevention Plan (SWPPP). Th
Discharge Identification number within 10 days of receipt of a complete NOI and SWPPP
Applicant is then required to submit copies of the NOI and SWPPP to the Ci
Francisco, Public Works Department Division of Water Quality, pr
and/or grading permits. The conditions of approval identified in Chapter 1,Section 1.5.5
apply to the Project as a matter of law. These measures are required in order to reduce water
quality impacts to a less than significant level.
SSF
OUTH AN RANCISCO
Chapter 1, Sections 1.4 and 1.5 outline the Citys standard review process and conditions of
project approval. Rob Lecel, Senior Environmental Compliance Coordinator,reviewed the
Project and identified the following conditions of approval (mem to Planning Division,
July 13, 2015).
The following items must be included in the plans or are require
and/or Pretreatment programs and must be completed prior to the
1.Submit an erosion and sediment control plan.
2.Downspouts must discharge to landscaping and cannot be directly
water system.
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I
MPACTS
a) Violation of Water Quality Standards or Waste Discharge Requi
Significance Criteria:The Project would have a significant environmental impact if it were to result
in any violation of existing water quality standards or waste di
The Project as a matter of law is required to provide a SWPPP for approval by the City. The
City requires the implementation of LIDs and BMPs for new development and construction as
part of its storm water management program, as levied through st
project approval by the Water Quality Control Division of the PuRob
Lecel, Senior Environmental Compliance Inspector for the City of South San Francisco
reviewed the proposed plans and identified the conditions of approval (listed in the Setting
Section, above). These measures are required by the City in compliance
authority and are designed to reduce potential water quality impacts to less t
The Project would present no impact with respect to violation of
or waste discharge standards as the result of the Citys permitt which
are in compliance with regional, state and federal laws designed
including stormwater impacts both on individual projects and as well as cumulative
impacts.
b) Deplete or Interfere Substantially with Groundwater
Significance Criteria: The Project would have a significant environmental impact if it
depletes groundwater supplies or interferes substantially with g
there would be a net deficit in aquifer volume or a lowering of cal groundwater table level.
The Project would not draw down groundwater but be connected to water supply
provided by California Water Service. The Project would leave 78 percent of the site unpaved
and porous allowing groundwater recharge.
The Project would have a less than significant impact with regard to groundwater
depletion. The Project would continue to receive its water supply from existing local
infrastructure, not groundwater. Current conditions include some filtration and sheet
flow off the site into the street and storm drain. The Project w
significant impact with respect to groundwater recharge by leaving 78 percent of the site
in porous conditions and would improve collection and filtration conditions as required
by conditions of Project approval.
c) Alter Existing Drainage Patterns/Erosion and Siltation Effect
Significance Criteria: The Project would have a significant environmental impact if it
substantially alter the existing drainage pattern of the site in a manner which would result in
substantial erosion or siltation.
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The Project is required to comply with current NPDES and SWPPP measu
sections a and b, above,and Section 3.7, Geology and Soils. The regulations mandate the
Project to treat all stormwater runoff from the entire Project o-site prior to discharging into the
storm drain. Therewould be a less than significant impact related to altered drainage
patterns or siltation at the Project site as a result of the NPDES and SWPPP measures
required by the City.
d) Alter Existing Drainage Patterns/Flooding Effects
Significance Criteria: The Project would have a significant environmental impact if it
substantially alter the existing drainage pattern of the site or area or substantially increase the rate
or amount of surface runoff in a manner that would result in flo- or off-site.
The Project, as noted in sections b and c above, would likely improve the existing drainage
pattern of the site because the Project is required by law to implement NPDES and SWPPP
measures (outlined in detail in the Setting Section above and Chapter 1, Legislative
Framework) and conditions of approval noted in the Setting Section, above. Under current
conditions, it is reasonable to assume that stormwater percolates on site and sheet flows across
the site in a westerly direction (due to the gradient), into the street and the Citys storm drain
system.
The Project is required to comply with conditions of approval. Condition of Approval #2,
noted above, requires that downspouts must discharge to landsca
plumbed to the storm water system (Rob Lecel, Senior Environmental Compliance Inspector).
The Project would result in a less than significant impact related to an increased rate or
amount of surface runoff with implementation of the conditions of approval required by
law.
e) Runoff Exceeding Drainage System Capacity/Increase Polluted R
Significance Criteria: The Project would have a significant environmental impact if it were to
create or contribute runoff water which would exceed the capacit
water drainage systems or provide substantial additional sources
The Project, as a matter of law, is required to submit a SWPPP and an Erosion Control Plan to
the City Engineer and the Water Quality Control Division prior to the commencement of any
grading or construction of the Project. The SWPPP as noted in the Chapter 1, Section 5, the
Setting Section and in sections a, b, c and d above, is designed to reduce stormwater impacts
to less than significant.
Water quality measures are required to be included in the buildi, all
contractors are as a matter of law made aware of the requirements. Additionally, the Engineering
Division of the Public Works Department as well as the Water Qua
Compliance Inspector conducts routine site inspections to insure compliance. Failure to comply
with the approved construction BMPs would result in the issuance of correction notices,
citations and/or a Stop Work Order. Plans for the Project would as a matter of law include
erosion control measures to prevent soil, dirt and debris from e
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Implementation of the measures required as a matter of law would reduce runoff
impacts to less than significant.
f) Otherwise Degrade Water Quality
Significance Criteria: The Project would have a significant environmental impact if it
degrade water quality.
The Project would result a less than significant impact on water quality from point
source water pollution with implementation of the measures required by law.
g i) Flood Hazards
Significance Criteria: The Project would have a significant environmental impact if it were to place
any housing units within a designated 100-year flood hazard area; if it placed any structures in a
manner which would impede or redirect flood flows; or if it were
people or structures to flooding hazards.
The Project site is located in a Flood Zone X (unshaded); an area of minimal flooding. The
Citys Building Official is the Flood Administrator who is respo
construction complies with FEMA regulations. The site is not within a 100-year flood zone.
The Project would result in no impact with respect to flooding.
j) Tsunami Hazards
Significance Criteria: The Project would have a significant environmental impact if i
in the exposure of people or structures to inundation by seiche, tsunami,or mudflow.
The Project site is located approximately 8,000 feet fromSan Francisco Baywith Sign Hill
between the site and the Bay. An earthquake could cause tsunamis (tidal waves) and seiches
(oscillating waves in enclosed water bodies) in the Bay. The Citys general plan estimates that
potential wave run-up of a 100-year tsunami would be approximately 4.3 feet above mean sea
level (msl) and approximately 6.0 feet above msl for a 500-year tsunami (p 250, SSF GP, 1999).
The Project site is 348 feet above msl,would be outside the runup zone subject to inundation by
a 500-year tsunami, and would be outside the any potential tsunami hazard zone. The Projectis
not within an inundation zone;therefore,the impact of potential inundation by tsunami,
seiche, or mudflow isconsidered to be less than significant.
Hydrology and Water Quality Finding:The Citys standard conditions of approval which
implement state, federal,and local regulations are required by law and are adequate to address
any potential water quality impacts as a result of Project constThe
Project site is 348 feet above msl, would be outside the runup z
500-year tsunami and would be outside the any potential tsunami hazard zone. The site is within
Flood Zone X and not subject to an 100-year flood event. No mitigation measures, above those
required by the City as a matter of law, are identified. The Project would not result in an impact
or contributeto a cumulative impact to hydrology or water quality resources.
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3.10LUP
AND SE AND LANNING
PotentiallyLess ThanLess Than
Significant Significant Significant No
ImpactwithImpactImpact
Would the Project:Mitigation
a) Physically divide an established community?
X
b) Conflict with any applicable land use plan, X
policy, or regulation of an agency with
jurisdiction over the Project (including, but
not limited to the general plan, specific plan,
local coastal program, or zoning ordinance)
adopted for the purpose of avoiding or
mitigating an environmental effect?
c) Conflict with any applicable habitat
X
conservation plan or natural community
conservation plan?
S
ETTING
The Project site is located in the northern portion of the City of South San Francisco, in an area
known as the Paradise Valley/Terrabay planning sub-area (SSF GP, 1999, p. 118). The Project
site is in the western portion of the planning area in a single-family neighborhood known as
Sterling Terrace. The Project site is one of the very few remaining vacant lots in the Ster
Terrace neighborhood.
The Paradise Valley/Terrabay planning sub-area spans the northern slope of Sign Hill to the
City boundaries between the Town of Colma, the City of Brisbane, and San Bruno Mountain
County Park to the north; Bayshore Boulevard to the South; and
Airport, Sister Cities and Hillside Boulevards are within the plsub-area. The planning
sub-area is largely residential. Older residential development, circa 1940-1950, and single family
development, is located south of Sister Cities and Hillside Boul-
family detached, duplex and condominium developments associated with Terrabay Phases I and
II are north of Sister Cities and Hillside Boulevards.
RF
EGULATORY RAMEWORK
General Plan Designation
The Project site is designated Low Density Residential (RL) permitting up to 8 units per acre.
th
The site is in within the Sterling Terrace neighborhood, constructed in the mid-20 century
consisting of single-family detached residences. The terminus of Larch Avenue (to the
southwest) abuts multi-family designated and developed properties.
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Zoning Classification
The Project site is zoned Low Density Residential, allowing a maximum of eight units per acre
(RL-8).
I
MPACTS
a and b) Division of an Established Communityand Conflicts with Land Use Plan and
Zon i ng
Significance Criteria: The Project would have a significant environmental impact if it
physically divide an established community and/or the Project would have a significant
environmental impact if it were to result in a conflict with anyapplicable land use plan, policy, or
regulation of an agency with jurisdiction over the Project adoptvoiding or
mitigating an environmental effect.
The Project conforms to the general plan and zoning classifications f as shown in
Chapter 2, Project Description. The lot was created in the 1950s and intended for a single-
family residence.
The Applicant proposes environmental mitigations as part of the Proj Chapter 2,
Project Description and Appendix A). This chapter, Chapter 3, Environmental Checklist,
evaluates potential impacts associated with 17 environmental reslative
impacts and finds Project related impacts to be less than significant with implementation of the
measures required by law and proposed by the Applicant.
The Project would have no impact on dividing an established commu
continue to be consistent with Citys General Plan and zoning. The Project would
conform to all applicable land use plans and zoning regulations and proposes
environmental mitigations as part of the Projectand, therefore, would have no impact.
c) Conflict with Conservation Plan
Significance Criteria: The Project would have a significant environmental impact if i
in a conflict with any applicable habitat conservation plan or n
plan.
There is no conservation or natural community conservation plans that govern the Project site
(or area) as identified in Section 3.5, Biological Resources. Therefore, the Project would
have no impact on conservation plans.
Land Use Finding: The Project would not physically divide an established community. The
site is planned for a single-family use and the Project is consistent with the planned uses. There
are no conservation or natural community conservation plans that
area. The Project would not result in any individually or cumulatively considerable impacts.
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3.11MR
INERAL ESOURCES
Less Than
PotentiallyLess Than
Significant
Significant Significant No
with
Would the Project:
Mitigation
Impact Impact Impact
a)Result in the loss of availability of a known X
mineral resource that would be of value to
the region and the residents of the state?
b) Result in the loss of availability of a locally-
X
important mineral resource recovery site
delineated on a local general plan, specific
plan or other land use plan?
S
ETTING
The Project is located in an area developed with residential lanThe site
is vacant, has never been developed, and was partially graded in the 1950s.
There are no areas of mineral resources in the City as documented by the South San Francisco
General Plan and Background Report(1999).
I
MPACTS
a) and b) Loss of Mineral Resources
Significance Criteria: The Project would have a significant environmental impact if it
in the loss of availabilityof a known mineral resource that would be of value to the region
the residents of the state, or if it were to result in the loss -important
mineral resource recovery site delineated on a local general pla other land use
plan.
No mineral resources of value to the region and the residents of
the Project site. The Project site has not been delineated as a
site on the City of South San Francisco General Plan, on any specific plan, or on any other land use
plan. Therefore, the Project would have no impact on any known mineral resource, or
result in the loss of availability of any locally important reso
Minerals Finding: The Project site does not contain any local or regionally significant mineral
resources. The Project would not result in an impact or contrib
mineral resources.
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3.12N
OISE
PotentiallyLess ThanLess Than
Significant Significant Significant No
ImpactwithImpactImpact
Would the Project:
Mitigation
X
a)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?
X
b) Exposure of persons to or generation of
excessive groundborne vibration or
groundborne noise levels?
X
c)A substantial permanent increase in ambient
noise levels in the Project vicinity above
levels existing without the Project?
X
d) A substantial temporary or periodic increase
in ambient noise levels in the Project vicinity
above levels existing without the Project?
X
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 the Project
expose people residing or working in the
Project area to excessive noise levels?
X
f)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?
S
ETTING
The Project site is located in a residential neighborhood north
major source of noise in the Project vicinity is traffic on Hillch is located
more than 500 feet north of the Project site. Another potential
aircraft noise from the San Francisco International Airport.
The Project could result in a temporary increase in noise levelsactivities. In
general, residences are one of the quietest land uses (other tha), and noise from one
residence would be considered compatible with the surrounding residences. By definition,
residential land uses are considered a sensitive receptor (see discussion below, under Sensitive
Receptors) Therefore, noise impacts generated by the residential use are insignificant and will
notbe further assessed. Temporary construction-related noise impacts will be fully vetted.
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The applicantproposes the following noise reduction measures as part of the Project(see
Chapter 2, Project Description and Appendix A):
1.Secure an exception permit for noise levels that could temporari
property line in order to comply with the Citys Noise Ordinance.
2.Construct a temporary noise barrier between the Project and 859
the site on the east (see Noise Figure 1, below). The noise barrier will remain in place for
the duration of construction. The barrier will be constructed on the eastern property line of
the Project site, and be long and tall enough to block the line
activities and the adjacent sensitive receptor. Temporary barriers will be constructed from
materials such as plywood lined with noise-absorbing material, commercial panels lined
with sound absorbing material, or noise blankets or curtains, and will have a Sound
23
Transmission Class (STC)rating of STC 30 or greater.Examples of noise control
blankets and sound curtains as well as installation of these features can be viewed on the
following website: http://www.allnoisecontrol.com/outdoor-noise-control-blankets.cfm.
3.Enclosures for stationary equipment and movable barriers will be
the sensitive receptors to the north and west of the Project site to the extent feasible.
The barriers will be located as close as possible to the noise s
Portable panels and noise curtains are examples of movable temporary noise barrier
systems that might be feasible on the hillsides (Federal Highway Administration
(FHWA), Construction Noise Handbook, August 2006a).Enclosures around stationary
equipment can provide a 10 to 20 dB sound reduction and barriers
provide a 5 to 20 dB sound reduction in noise levels (California Department of
Transportation (CalTrans), 1998. Technical Noise Supplement, October, 1998 (NCHRP)
1999).
4.Ensure that construction equipment is properly muffled according
5.Provide advance notification to surrounding land uses disclosing the construction schedule
including the various types of activities that would be occurrin
the construction period.
6.Designate a member of the construction team as an on-site construction noisecontactwho
will act as aNeighborhood Liaison for the duration of the Project. TheNeighborhood
Liaison will respond to noise issues and implement solutions, if feasible and necessary, in
addition those identified above. For example, a neighbor may have a special event that
requires a quiet environment for a few hours or a day, such as a,or
23
Sound Transmission Class (STC) is a widely used rating for how well a building parti
sound. STC ratings are used to rate interior partitions, ceiling
configurations.
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memorial service, and the construction schedule may be able to a
activities for afew hours.
7.Post signs around the Project site to inform persons of the construction hours and
name and phone number of the person or persons to notify in the
problem (theNeighborhood Liaison).
NF1
OISE IGURE
LTSB
OCATION OF EMPORARY OUND ARRIER
N
D
OISE EFINED
Noise is generally defined as unwanted sound. Whether a sound is
and where it occurs, what the listener is doing when it occurs,
(loudness, pitch and duration, speech or music content, irregularity) and how intrusive it is above
background sound levels. In determining the daily level of envir
to account for the difference in response of people to daytime a
nighttime, exterior background noises are generally lower than daytime levels. However, most
household noise also decreases at night and exterior noise becom
most people sleep at night and are very sensitive to nighttime n
To quantify the noise over a 24-hour period, the Day/Night Average Sound level (DNL or Ldn)
or Community Noise equivalent Level (CNEL) criteria areused. Both noise descriptors include
a 10 decibel (dB) penalty (addition to the actual measured level(10:00
p.m. to 7:00 a.m.) and a five dB penalty during evening hours (7:00 p.m. to 10:00 p.m.) for the
CNEL to account for peoples sensitivity during these hours. Noise is measured and quantified
with an A-weighted filter which closely approximates the way the human ear hears sound; a de-
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emphasis of low-frequency and high-frequency sound. The resulting measurement is quantified
as an A-weighted decibel or dBA.All references to decibels (dB) in this report will be A-
weighted unless noted otherwise.
Noise attenuates (reduces) the further it travels from the source. Sta
noise, including construction equipment, attenuate (lessen) at a
of distance from the source, depending on ground absorption. Sofes attenuate at 7.5 dB per
doubling because they have an absorptive ground surface such as
bushes and trees. Hard sites have reflective surfaces (e.g., par
therefore have less attenuation (6.0 dB per doubling). Noise from a street with moving vehicles
(known as a line source), would typically attenuate at a lowerapproximately 3 to 4.5 dB
each time the distance doubles from the source, which also depen. The
shell of a building (sometimes referred to as the envelope) attenuates noise
more depending on the type construction, number and type of doors and
insulation contained therein. Physical barriers located between a noise source and the noise
receptor, such as berms or sound walls, will increase the attenu
attenuation that occurs by distance alone.
Projects can result in an increase in noise (unwanted sound) fro/or
operational activities. Construction istypically short-term in nature depending upon the
construction schedule. Construction impacts can be annoying, but are relatively short-term and
restricted to certain times of the day while operational impact
run with the life of the Project and largely result from increased traffic,
and/or land use activities that are conducted external to a buil
RF
EGULATORY RAMEWORK
OSHA(OSHA)
CCUPATIONAL AFETY AND EALTH DMINISTRATION
Federal codes, primarily the Occupational Safety and Health Act of 1970 (OSHA), govern
worker exposure to noise levels. These regulations would be app
Project and are designed to limit worker exposure to noise level
over an 8-hour period (Title 29, Code of Federal Regulations [CFR], Sectio
OSHApermissible noise exposure limits for occupational noise are shown in Noise Table 1.
When employees are subjected to sound exceeding those listed in Noise Table 1, feasible
administrative or engineering controls shall be utilized, or per
provided and used to reduce sound levels within the levels of th
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NT1
OISE ABLE
PNE
ERMISSIBLE OISE XPOSURES
Duration Per Day (Hours) Sound Level (dB, slow response)
16 85
8 90
6 92
495
3 97
2 100
1 & 1/2102
1 105
1/2110
1/4 or less115
Source: Title 29, Code of Federal Regulations [CFR], Section 191-16A
C
S
TATE OF ALIFORNIA
The California Building Code (CBC) Title 24, Part 2, Chapter 2.35 of the California Code of
Regulation, collectively known as Title 24, contains acoustical requirements for interior sound
levels in habitable rooms for multi-family residential land uses. Title 24 contains requirements
for construction of new hotels, motels, apartment houses, and dwellings other than
single-family dwellings intended to limit the extent of noise transmitt
The standard specifies the extent to which walls, doors, and flo-ceiling assemblies must block
or absorb sound in between units and the amount of attenuation n
exterior sources. The standard sets forth an interior noise leve
habitable room with all doors and windows closed. The code requires an acoustical analysis
demonstrating how dwelling units have been designed to meet this
units are proposed in areas subject to noise levels greater than). Title 24
dn
requirements are enforced as a condition of building permit issuance by the Building Division.
SSFGP
OUTH AN RANCISCO ENERAL LAN
The South San Francisco Noise Element (SSF GP, 1999, pp. 275288) contains land use criteria
for noise as it pertains to various land uses. These criteria dene the desirable maximum noise
exposure of various land uses in addition to certain conditional
upon the implementation of noise reduction measures. For residen
than sixty-five dBA CNEL are acceptable and noise levels of 65 to 70 dBA CNEL are
conditionally acceptable. (Table 9.2-1 Land Use Criteria for Noise-Impacted Areas, SSF GP, 1999, p.
280).
SSFNO
OUTH AN RANCISCO OISE RDINANCE
The City of South San Francisco regulates exterior noise levels through its Noise Ordinance
(Chapter 8.32, South San Francisco Municipal Code). The Noise Ordinance contains special
provisions for construction activities (Section 8.32.050(d).). Construction activities authorized by
a valid city permit shall be allowed on weekdays between the hours of 8:00 a.m. and 8:00 p.m.,
on Saturdays between the hours of 9:00 a.m. and 8:00 p.m., and o
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between the hours of 10:00 a.m. and 6:00 p.m., or at such other
the permit, as long as they meet at least one of the following noise limitation
(1) No individual piece of equipment shall produce a noise level exc
distance of twenty-five feet. If the device is housed within a structure or trailerty,
the measurement shall be made outside the structure at a distanc-five feet
from the equipment as possible.
(2) The noise level at any point outside of the property plane of th
ninety dB.
According to Section 8.32.060 of the Noise Ordinance, if the applicant can show t
manager, or the managers designee, that a diligent investigatio
techniques indicates that immediate compliance with the requiremould be
impractical or unreasonable, a permit to allow exception from th
chapter may be issued, with appropriate conditions to minimize t
such exceptions. Any such permit shall be of as short duration as possible, but in no case for
longer than six months. These permits are renewable upon a showi
be conditioned by a schedule for compliance and details of compl
cases.
R
S
ENSITIVE ECEPTORS
Residential, schools, child care facilities, and convalescent facilities are typically considered noise
sensitive land uses. The closest sensitive receptors to the Project site are single-family homes
adjacent to the Project site on the east (the closest of which is approximately five feet from the
Project site eastern boundary) and across Larch Avenue to the no
from the Project site), as well apartment homes located 50 feet
Christian Academy is located 300 feet northwest of the Project site. Aesthetic Figures 1, 2,
and 3 in Section 3.1 illustrate the proximity of the residential uses.
I
MPACTS
a d) Exposure of Persons to or Generation of Noise Levels in Exces
Exposure of Persons to or Generation of Excessive Groundborne Noise Levels, a
Substantial Temporary or Permanent Increase in Ambient Noise Lev
Vicinity above Levels Existing Without the Project.
Significance Criteria: The Project would have a significant environmental impact if it were to result
in exposure of persons to or generation of noise levels in exces
South San Francisco General Plan or the City Noise Ordinance. Construction noise would have a
significant environmental impact if it occurs outside the hours specified in the Noise Ordi
or generates noise levels greater than those specified in the No
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PNIPR
OTENTIAL OISE MPACTS ON ROJECT ESIDENCE
According to the South San Francisco General Plan, the site is located outside of the 60 dB noise
contour for roadway noise (Figure 9-2 Projected Rail and Road Noise,SSF GP, 1999,p.283)and
located outside of the 65 dB contour for airport noise (Figure 9-1 Aircraft Noise and Noise Insulation
Area,SSF GP, 1999, p.279). The airports contours were updated in 2012, and the Project is
outside of the 65 dB contour (Comprehensive Airport Land Use Compatibility Plan for the Enviro
San Francisco International Airport, Ricondo Associates, 2012). Exterior noise levels at the Project
site are less than 65 dB CNEL, and would comply with the land us
uses contained in the South San Francisco General Plan.
Typical residential construction will provide an exterior-to interior noise level reduction of no
less than 25 dB provided that exterior windows and doors are clo
Consultants, PFE/Walerga Mixed-Use Development, Environmental Noise Assessment, 2005. Burn,
Melissa. WYLE Laboratories. WYLE Research Report WR 94-23. Raleigh-Durham International
Airport New Construction Acoustical Design Guide. 1994). Interior noise levels would be less than 45
dB and would comply with the California Building Code.
Noise levels at the future residence would comply with the standards of the California Building
Code and South San Francisco General Plan. Residents of the home would not be exposed to
noise levels in excess of City standards, and impacts to residen
significant.
PC
ROJECT ONSTRUCTION
Project construction would occur during a period of approximately 32 to 44 weeks.
Construction activities would occur during the construction hours contained in the South San
Francisco Noise Ordinance. The Noise Ordinance requires that cononly
take place on weekdays between the hours of 8:00 a.m. and 8:00 p.m., o
hours of 9:00 a.m. and 8:00 p.m., and on Sundays and holidays be
and 6:00 p.m.
Project construction would result in a temporary, short-term increase of noise levels in the
Project vicinity. Construction activities would include gradingof the site, drilling of piers, and
construction of the residence. As shown in Noise Table 2, maximum applicable construction
24
equipment noise levels can range from 76 to 85 dB at 50 feet.
Pile driver noise can reach 101 dB at 50 feet, but pile driving
24
analyzed herein.
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NT2
OISE ABLE
TNLFCE
YPICAL OISE EVELS ROM ONSTRUCTION QUIPMENT
Construction Equipment 1
Noise Level (dB, Lmax at 50 feet)
Dump Truck 76
Auger Drill Rig 84
Drill Rig Truck 79
Air Compressor 78
Crane81
Concrete Mixer (Truck)79
Scraper84
Dozer 82
Paver77
Generator 81
Rock Drill 81
Excavator81
Pile Driver101
Front End Loader 79
Grader 85
Backhoe 78
Federal Highway Administration (FHWA) Roadway Construction Noise
Lmax is the instantaneous maximum noise level for a specified period of time.
1
The highest noise levels during construction would occur during
phase would include grading of the site as well as drilling and installation of the piers foe
residence. Preparation of the site would last for a duration of five days, and grading of the site
would occur for approximately 30 days. Graders may be used durin
can result in a maximum noise level of 85 dB at 50 feet, and drills produce noise levels of 79-84
dB at 50 feet (Roadway Construction Noise Model Users Guide, FHWA, 2006b).
Maximum noise levels that could occur at the nearby sensitive rection are
shown in Noise Table 3, below. Noise levels at each receptor were calculated using the noise
level of the loudest piece of applicable equipment (grader), when it would be operated at its
closest point to each receptor.If excavators are used instead of graders for grading of the
Project site, maximum noise levels would be 4 dB less than these estimates. Noise levels would
be less than these estimates most of the time, since grading would only occur for a d
30 days, and other equipment used for Project construction would, noise
during grading would fluctuate throughout the day because equipm
one location for an extended period of time. As shown in Noise Table 3, the maximum noise
levels inside the nearby residences would be well below the OSHAse exposure limits for
hearing conservation shown in Noise Table 1. Residents of nearby homes would not be
exposed to exterior noise levels exceeding 85 dB for a 16 hour c
identified as the maximum threshold shown in Noise Table 1.
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NT3
OISE ABLE
MCNLANSR
AXIMUM ONSTRUCTION OISE EVELS T EARBY ENSITIVE ECEPTORS
1
Sensitive ReceptorExterior Noise Level Interior Noise
(dB, Lmax) Level (dB, Lmax)
Residence adjacent to the Project site (5 feet 9974
east of the Project boundary, 10 feet from
construction)
Apartment Homes (50feet west of the Project 8560
boundary)
Residences across Larch Avenue (70 feet north 8257
of the Project boundary)
Hillside Christian Academy (300 feet 6944
2 2
northwest of the Project boundary)
Note: Noise levels were predicted using a reference noise level of 85 dB at
per doubling of distance
Typical residential construction will provide an exterior-to interior noise level reduction of no less than 25 dB
1
provided that exterior windows and doors are closed (Bollard, 2005, Burn,
Maximum noise levels at the school would be at least 3 to 5 dB l
2
attenuation provided by buildings between the Project site and tool (Federal Highway Administration
(FHWA), FHWA Highway Noise Barrier Design Handbook, February 2000).
Construction equipment operated in close proximity to the proper
the adjacent residential property to the east. In addition, some of the equipment used for
construction could exceed 90 dB at a distance of 25 feet. As sho Noise Table 4,
equipment producing the highest noise levels (graders, scrapers,
maximum noise levels of 90 to 91 dB at a distance of 25 feet.
NT4
OISE ABLE
CENL25F
ONSTRUCTION QUIPMENT OISE EVELS AT EET
Equipment Noise Level (dB, Lmax at 25 feet)
Auger Drill Rig 90
Grader 91
Scraper 90
Note: Noise levels were predicted using an attenuation rate of 6.0dB per doubling of distance.
The hours of construction would comply with the South San Franci the
absence of the measures proposed by the Applicant, noise levels
noise limits contained in the Noise Ordinance. In addition, temporary construction could result
in short-term noise increases in ambient noise levels that could be annoy
receptors. Implementation of the measures the Applicant proposes
(identified in the Noise Setting Section and Chapter 2) would ensure compliance with the
South San Francisco Noise Ordinance and reduce construction nois
feasible.
The implementation of measures the Applicant proposes would ensure that the Project
complies with the South San Francisco Noise Ordinance and would reduce temporary
short-term noise impacts at sensitive receptors in the Project vicinit
construction noise would be a less-than-significant impact with implementation of the
measures the Applicant proposes as part of the Project.
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TCV
EMPORARY ONSTRUCTION IBRATION
Construction operations have the potential to result in varying
vibration, depending on the specific construction equipment used
ground vibration levels associated with various types of constructio
in Noise Table 5. Ground vibration generated by construction equipment spreads t
ground and diminishes in magnitude with increases in distance. T of ground vibration
may be imperceptible at the lowest levels, low rumbling sounds a
moderate levels, and slight damage to nearby structures at the h
At the highest levels of vibration, damage to structures is primarily architectural (e.g., loosening
and cracking of plaster or stucco coatings) and rarely results i
structures, a peak particle velocity (ppv) threshold of 0.5 inch
avoid structural damage. The Federal Transit Administration recommends a threshold of 0
for residential and commercial structures, 0.25 ppv for historic
and 0.2 ppv for non-engineered timber and masonry building (Federal Transit Administration
(FTA), Transit Noise and Vibration Impact Assessment, 2006).
NT5
OISE ABLE
RVSLCE
EPRESENTATIVE IBRATION OURCE EVELS FOR ONSTRUCTION QUIPMENT
EquipmentPeak Particle Velocity at 25 Feet (in/sec)
upper range 1.518
Pile Driver (impact)
Typical 0.644
upper range 0.734
Pile Driver (sonic)
Typical 0.170
Large Bulldozer 0.089
Caisson Drilling 0.089
Loaded Trucks 0.076
Jackhammer 0.035
Small Bulldozer 0.003
Source: Federal Transit Administration, 2006.
Note: Equipment shown in bold could be used during construction of the Project.
The Projectwould not involve the use of any equipment or processes that wou
potentially significant levels of ground vibration (i.e., would not use pile drivers that could be
above 0.5 ppv). Ground vibration generated by construction operations would be primarily
associated with on-site trucks, bulldozers, and drilling of piers. As shown in Noise Table 5, this
equipmentwould result in vibration levels of less than 0.1 inch per secon
Construction equipment operated as close as 10 feet from the nearby
vibration level of 0.35 ppv. The predicted vibration levels at the nearest structure would no
anticipated to exceed the 0.5 ppv threshold for residential structures. The temporary
construction vibration associated with on-site equipment would not be anticipated to
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expose sensitive receptors to or generate excessive groundborne
groundborne vibration levels, and would result in a less-than-significant impact.
e) and f) Aircraft Noise
Significance Criteria: The Project would have a significant environmental impact if i
within an airport land use plan (or, where such a plan has not b
a public airport or publicuse airport) or in the vicinity of a private airstrip and were t
people residing or working in the Project area to excessive nois
The site is not within an aircraft insulation area as shown on Figure 9-1 Aircraft Noise and Noise
Insulation Program(SSF GP, 1999, p. 279). The contours indicate the Project site is located outside
the 65-dBA (CNEL) aircraft noise contour. The Project is not located within two miles of a
private airstrip, and is not located within the 65 dB SFO noise Therefore, the
Project would result in a less-than-significant impact with respect to excessive aircraft
noise exposure.
Noise Finding: The implementation of measures the Applicant proposes would ensu
Project complies with the South San Francisco Noise Ordinance and would reduce temporary
short-term noise impacts at sensitive receptors in the Project vicinit
noise would be a less-than-significant impact with implementation of the measures the Applicant
proposes as part of the Project.
The temporary construction vibration associated with on-site equipment would not be
anticipated to expose sensitive receptors to or generate excessi
groundborne vibration levels, and would result in a less-than-significant impact.
The Project is not located within two miles of a private airstri
dB SFO noise contour. Therefore, the Project would result in a l-than-significant impact with
respect to excessive aircraft noise exposure.
3.13PH
OPULATION AND OUSING
Potentially Less Than Less Than
Significant Significant Significant No
with
Impact Impact Impact
Mitigation
Would the Project:
X
a) Induce substantial population growth in an
area, either directly (for example, by
proposing new homes and businesses) or
indirectly (for example, through extension of
roads or other infrastructure)?
X
b) Displace substantial numbers of existing
housing, necessitating the construction of
replacement housing elsewhere?
X
c) Displace substantial numbers of people,
necessitating the construction of
replacement housing elsewhere?
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S
ETTING
The site has never been developed and is part of a single-family detached neighborhood known
as Sterling Terrace. The neighborhood was constructed in the 1950-1960s. The Project would
be the construction of one single-family detached residence in a subdivision planned and zoned
for such development.
Typically, the construction of one single-family residence in a residential zone with utilities and
infrastructure in place is categorically exempt from the CEQA re CEQA Guidelines
section 15303, Class 3 New Construction or Conversion of Small S
are exceptions to exemptions as stated in CEQAGuidelines section 15300.2, subsection (a).
Subsection (a) clearly states Class 3 exemptions are qualified b
would be located. The subsection further notes a project that in
in its impact on the environment may in a particularly sensitive environment be signifi
Therefore, if a project might be located in a biological habitat
slopes, or on properties known to have environmental contaminatirials), the
exception to the exemption noted above requires the lead agency
which may be satisfied by utilizing the sample forms provided in
CEQA Guidelines.
Therefore, if a project might be located in a biological habitat, or on steep or potentially unstable
slopes, or on properties known to have environmental contaminati, the
exception to the exemption, noted above, requires the lead agency to conduct an initial study,
which may be satisfied by utilizing the sample forms provided in Appendices G and H of the
CEQA Guidelines. The potential biological issues vetted in Section 3.4, Biology and
geotechnical constraints vetted in Section 3.7, Geology and Soils were the catalyst for the
preparation of this initial study. The addition of one single-family residence planned since the
1950s poses no impact on population and housing.
I
MPACTS
a) Population Growth
Significance Criteria: The Project would have a significant environmentalimpact if it were to
induce either directly of indirectly substantial population grow
The Project site has been planned for a single-family residence since the neighborhoods
development in the 1950s.
The Project is a residence and not a source of employment, albeit it is likely that residents of the
household would be employed. The Project would not add to the growth assumptions
contained in the Citys General Plan and the impact on population growth would be less
than significant.
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b) and c) Displacement of Housing or People
Significance Criteria:The Project would have a significant environmental impact if it
in the displacement of substantial numbers of existing housing u
project site.
There are no residential units on the Project site. The Project would add a residential unit in
a neighborhood with aging residential stock. The Project would have no impact on the
displacement of housing or people.
Population and Housing Finding: The Project site has been planned for a residential use
since the 1950s. The Project site is vacant and would add one housing unit and not displace
housing units or residents.
3.14PS
UBLIC ERVICES
Potentially Less Than Less Than
Significant Significant Significant No
with
Impact Impact Impact
Mitigation
Would the Project:
a) 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 cause significant environmental
impacts, in order to maintain acceptable
service ratios, response times or other
performance objectives for any of the public
services:
X
i) Fire protection?
X
ii) Police protection?
X
iii) Schools?
X
iv) Parks?
X
v) Other public facilities?
S
ETTING
As noted above in the Population and Housing section, the site has never been developed and
is part of a single-family detached neighborhood known as Sterling Terrace. The neighborhood
was constructed in the 1950s. The Project would be the construction of one single-family
detached residence in a subdivision planned and zoned for such d
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I
MPACTS
a) Public Services
Significance Criteria:The Project would have a significant environmental impact if it were to result
in substantial adverse physical impacts associated with the prov
governmental facilities, the construction of which could cause sts,
in order to maintain acceptable service ratios, response times o
for fire protection, police protection, schools, parks and recre
government facilities.
The Project is not anticipated to increase the City of South San Franciscos population as
identified as described above, in Section 3.10, Land Use and Planning and in Section 3.13,
Population and Housing. School impact fees are required for new construction and paid fo
at the time of building permit issuance.
South San Francisco Police and Fire Departments commented on the
standard review process identified in Chapter 1, Legislative Framework, Sections 4 and 5.
Fire Marshal, Luis Da Silva reviewed the Project plans and provided 12 Conditions of Project
Approval (June 22, 2015 memorandum to Ms. Rozalynne Thompson, Associate Planner),
identified in Chapter 3 Section 3.6 Hazards and Hazardous Materials. The Fire Marshal did
not identify staffing and service impacts with respect to the site development.
The Project site is not identified as being within a High Priority Fire Management Zone on
Figure 8-4 Fire Hazard Management Units (SSF GP, 1999, p. 265). Project impacts relating to
fire protection would be less than significant with implementation of the conditions of
approval required by law.
Police Sergeant Plank reviewed the Project plans. All constructi
Francisco Municipal Code Chapter 15.48 Minimum Security Standards (July 23, 2015
memorandum to Ms. Rozalynne Thompson, Associate Planner). Sergea
staffing and service impacts with respect to the site development.
Neither department identified staffing or service issues associated with development of thsite.
School fees are collected at the time of building permit issuanc
one single-family residence, 3.21 persons per household (PPHH), (SSFMC Chapter 19.24) is de
minimus. Recreation and park impacts are discussed in the following section. Any increased
demand for public services as a result of the Project would not
new facilities and would be considered less than significant.
Public Services Finding: The Project was reviewed by Police and Fire Department
representatives and staffing or facility needs were not identified as insufficieevelopment of
the Project site would not increase the demand for public servic.
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3.15R
ECREATION
PotentiallyLess ThanLess Than
Significant Significant Significant No
with
Impact Impact Impact
Mitigation
Would the Project:
X
a) 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?
X
b) Include recreational facilities or require the
construction or expansion of recreational
facilities, which might have an adverse
physical effect on the environment?
S
ETTING
As noted above in Section 3.13, Population and Housing and Section 3.14, Public Services,
the site has never been developed and is part of a single-family detached neighborhood known
as Sterling Terrace. The neighborhood was constructed in the 195s-1960s. The Project would
be the construction of one single-family detached residence in a subdivision planned and zoned
for such development.
I
MPACTS
a) and b) Recreation
Significance Criteria: The Project would have a significant environmental impact if it
in an increase in the use of existing parks or recreational facilities such
deterioration of these facilities could be anticipated, or if it
the construction of which might have adverse physical effects on the environment.
The Project area is served by a variety of open space and recreaThe Hillside and
Martin Schools provide 11 acres of sports and play areas (SSF GP, 1999. p. 177). The Hillside
School is approximately 800 feet northwest and Martin School is approximately 4,000 feet
southeast of the Project. The Terrabay Recreation Center, Hillside Recreation Center, the
Preservation Parcel associated with Terrabay Phase III now dedic
Mountain County Park, the history trail on the Terrabay Phase III site, the shared use
performing arts facility located in the South Tower of Terrabay
Sister Cities Boulevard, and a pocket park on Linden Avenue are
City and are located within the Terrabay/Paradise Valley neighbo
The Project would be one single-family residence with an estimated household of 3.21 people.
The Project would not be a major employer as identified in Section 3.13, Population and
Housing, above. The Project, a single-family residence estimated to add 3.21 people to
the area would not impact the provision of parks, recreational aThe
project does not require the expansion or provision of recreatiohich might
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have an adverse effect on the environment. The Projectsimpact on recreational facilities
would be less than significant.
Parks and Recreation Finding:The Project, the addition of one single-family residence,
th
planned for since the mid-20centurywould not result in an individual or cumulatively
considerable impact on parks and recreation.
3.16 TT
RANSPORTATION AND RAFFIC
Potentially Less Than Less Than
Significant Significant Significant No
with
Impact Impact Impact
Would the Project:
Mitigation
X
a) Conflict with an applicable plan, ordinance or
policy establishing measures of effectiveness
for the performance of the circulation system,
taking into accounts all modes of
transportation including mass transit and
non-motorized travel and relative
components of the circulation system,
including but not limited to intersections,
streets, highways and freeways, pedestrian
and bicycle paths and mass transit?
X
b)Conflict with an applicable congestion
management program including but not
limited to the level of service standards and
travel demand measures, or other standards
established by the county congestion
management agency for designated roads or
highways?
X
c) 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?
X
d) Substantially increase hazards due to a design
feature (e.g., sharp curves or dangerous
intersections) or incompatible uses (e.g., farm
equipment)?
X
e) Result in inadequate emergency access?
X
g) Conflict with adopted policies, plans, or
programs supporting alternative
transportation (e.g., bus turnouts, bicycle
racks)?
S
ETTING
As noted throughout this document, the Project site is located at 901 Larch Avenue is located at
the terminus of Lincoln Street where it intersects Larch Avenue.
approximate 600 foot north/south trending neighborhood street co
Boulevard. Hillside Boulevard provides access to both the western and e
City. To the east, Hillside Boulevard connects to and veers south of Sister Citie
Sister Cities Boulevard in conjunction with Airport and Oyster Pvardsform a leg of
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the Oyster Point Flyover. The Oyster Point Flyover provides access to north and southbound
U.S. Highway 101, as well as the East of 101 Area.
Hillside Boulevard provides access to the western and central poa
series oflocal,connector,and arterialstreets. Hillside Boulevard intersects Chestnut Avenue.
Chestnut Avenue turns into Westborough Boulevard when it crosses
Westborough Boulevard provides access to Interstate 280, Skyline Boulevard, and the City of
Pacifica. Hillside Boulevard also forms the boundary between the
San Francisco,approximately 1,000 feet north of the Project site (Google Earth, 2015).
Sidewalks are present on both sides of Larch Avenue. Larch Avenue has a 60 foot right-of-way.
Roadways in the Project area are not identified as needing major Figure 4-2 Major
Street Improvement s, SSF GP, 1999, p. 149).
Figure 4-1 Street Classifications identifies Larch Avenue and Lincoln Street as Other Streets (SSF
GP, 1999, p. 141). The classification system includes four types of streets dep
amount the street is traveled and its design. The Major Arteria
and includes Hillside and Chestnut Boulevards in the Project area; Grand Avenue south of the
Paradise Valley/Terrabay planning sub-area is an example of a Minor Arterial; Collector Streets
include the south branching portion of Hillside Boulevard and School Street in the eastern
portion of the Paradise Valley/Terrabay planning sub-area; and Other Streets, being the least
traveled, typically appearing in residential neighborhoods, include Hemlock Avenue and Kearney
and Jefferson Streets in the planning sub-area.
I
MPACTS
a and b)Increase in Traffic in Relation to Existing Traffic Load, Street System Capacity
and Complete Streets (discussed in , below)
Significance Criteria: The Project would have a significant environmental impact if it
an increase in traffic which is substantial in relation to the existing traffic load and capacity of
the street system.
The Project would add approximately nine average daily trips to the neighborhood streets (Trip
th
Generation Manual-9Edition, Institute of Transportation Engineers. 2012). The addition of nine
trips is an insignificant amount. Mr. Sam Bautista, City Enginecongestion
issues in the Project area and no improvements are planned (Nove The addition
of nineaverage daily trips per day would result in no impact in the Project area.
c) Alter Air Traffic Patterns
Significance Criteria: The Project would have a significant effect if it were to result
air traffic patterns, including either an increase in traffic leocation that results
in substantial safety risks.
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The Project is not within an airport zone. The Project is approximately2.5 miles northwest of
San Francisco International Airport, as identified in Section 3.8, Hazards and Hazardous
Materials,above. The Project would have no impact on air traffic patterns.
d) Hazards Due to Design Features or Incompatible Uses
Significance Criteria:The Project would have a significant effect if it were to increa
hazards due to its design or the introduction of incompatible traffic or result in safety impacts to
pedestrians or bicyclists due to a circulation pattern or inadeq
increased vehicle circulation looking for parking or inadequate
Larch Avenue is designed as a residential street with a 60 foot right-of -way. Intersecting streets
are perpendicular to Larch Avenue, providing adequate sight distances with no blind corners.
The Project proposes the required two-car off-street garage parking accessed by a driveway
perpendicular to Larch Avenue. The structure will besetback 15 feet from the front property
line,as required by zoning. The setback provides adequate distance and maneuver area to
approach and depart the site. The streets were designed to accommodate residential land uses.
The Project would not impact the streets, pose hazards associate, or pose
incompatible land uses.
e) Emergency Access
Significance Criteria: The Project would have a significant effect if it were to have inadequate
emergency access.
Police and Fire reviewed the Project and found no issues or concerns with respect to
emergency access. The development pattern and layout in the neighborhood was
designed to accommodate residential uses. The Project would pose no impacts
associated with emergency access.
a and f) Alternative Transportation
Significance Criteria: The Project would have a significant effect if it were to conf
policies, plans or programs regarding public transit, pedestrian facilities, or otherwise decrease
the performance or safety of such facilities.
The Project is required to reconstruct curb and sidewalkas noted in Chapter 3.6, Geology and
Soils
The owner shall, at his/her expense, repair any broken sidewalk,veway approaches,
curb and gutter along the entire frontage of the property, prior
inspection for the new building (Sam Bautista, City Engineer, No
The Project would result in no impact with respect to alternate ansportation modes or
conflict with adopted policies, plans or programs regarding publ
facilities, or otherwise decrease the performance or safety of s
is a compatible land use with the neighborhood and will replace sidewalks, driveway
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approaches,curbs,and guttersas required by the Citys identified conditions of
approval.
Transportation Finding: The Project would not impact the streets, pose hazards associate
with its use, or pose incompatible land uses.Police and Fire reviewed the Project and found no
issues or concerns with respect to emergency access. The develop
neighborhood was designed to accommodate residential uses. The P
impacts associated with emergency access. The Project would result in no impact with respect to
alternate transportation modes or conflict with adopted policies, plans or programs regarding
public transit, pedestrian facilities, or otherwise decrease the
facilities. The Project is a compatible land use with the neighborhood and w
driveway approaches and curb and gutter as required by the City
approval.
3.17USS
TILITIES AND ERVICE YSTEMS
PotentiallyLess Than Less Than
Significant Significant Significant No
Would the Project: Impact with Impact Impact
Mitigation
X
a) Exceed wastewater treatment requirements
of the applicable Regional Water Quality
Control Board?
X
b) Require or result in the constructionof new
water or wastewater treatment facilities or
expansion of existing facilities, the
construction of which could cause
significant environmental effects?
X
c) 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?
X
d) Have sufficient water supplies available to
serve the Project from existing entitlements
and resources, or are new or expanded
entitlements needed?
X
e) Result in a determination by the wastewater
treatment provider, which serves or may
serve the Project that it has adequate
capacity to serve the Projects projected
demand in addition to the providers existing
commitments?
X
f) Be served by a landfill with sufficient
permitted capacity to accommodate the
Projects solid waste disposal needs?
X
g) Comply with federal, state, and local statutes
and regulations related to solid waste?
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S
ETTING
The Project proposes one single-family residence. The Project is in a residential neighborhood
developed and planned for such use. The neighborhood, Sterling
th
most of the housing was constructed in the mid-20 century.
I
MPACTS
a) Regional Wastewater Treatment Standards
Significance Criteria: The Project would have a significant environmental impact if it
exceed wastewater treatment requirements of the applicable Regio
Board (RWQCB).
The Citys storm drain outfalls operate under NPDES permits granted by the RWQCB. The
South San Francisco Municipal Code (Title 14) contains regulatio
management. As identified in Chapter 1, Introduction, Section 5 and in Section 3.9,
Hydrology and Water Quality as a matter of law, projects are required to implement BMPs
and LID measures and comply with SWPPP regulations. Mr. Lecel, Senior Environmental
Compliance Inspector for the City, reviewed the Project, identified conditions of approval, and
did not identify any extraordinary measures or significant impacts with respect to wastewater.
The City is in compliance with its RWQCB permit. Therefore, the Project would not exceed
wastewater treatment requirements of the RWQCB, resulting in no impact
b and e) Wastewater Treatment Facilities
Significance Criteria: The Project would have a significant environmental impact if
in a determination by the wastewater treatment provider which ma
inadequate capacity to serve the Project's projected demand in addition to the provider's existing
commitments.
All wastewater produced within the City of South San Francisco i
Quality Control Plant (WQCP), which is located at the end of Bel
San Francisco Bay, south of the Project site. The WQCP is jointly owned by the Cities of South
San Francisco and San Bruno, and it treats all wastewater genera
WQCP also has contracts to treat most of the wastewater produced by the City of Colma and a
portion of the wastewater produced by the City of Daly City. The City of South San Francisco
has a current allocation of 8.74 million gallon per day (MGD), i
The Project was reviewed by both the Engineering and Water Quality Control staff. No
wastewater issues were identified (Sam Bautista, November 14, 20, July 13,
2015).
th
The Project site has been planned for a residential use since the mid-20century. The
City of South San Francisco has a current wastewater allocation of 8.74 million gallon per
day (MGD), is currently generating 5.6 MGD. The wastewater treatment plant has
capacity to treat Project and cumulative projected wastewater. The Project, per
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Engineering Condition of Approval #4,will be required to install a sewer lateral and
clean-out from the Project site to the street as all development is required within the City
(Sam Bautista, November 14, 2015). The Project would have a less than significant imp
act with respect to wastewater treatment.
c) Storm Water Drainage Facilities
Significance Criteria: The Project would have a significant environmental impact if it
require or result in the construction of new storm water drainagon of
existing facilities, the construction of which could cause signi
The Project would be required to connect to the stormwater facilities. As identified in the
Introduction, Chapter 1, Section 5 and Section 3.9, Hydrology and Water Quality,
stormwater is required to be collected on-site and conveyed to landscaping areas. The
Project would not require the construction of new or expanded st
(beyond the standard connection to the facility from the lot), resulting in no impact to
storm water drainage facilities.
b and d) Water Treatment Facilities and Supply
Significance Criteria: The Project would have a significant environmental impact if
require additional water supply beyond that available from existing entitlements and resources.
Senate Bill 610 (SB 610) was adopted in 2001 and became effectiv
requires cities to consider water supply assessments to determin
supplies can meet a projects water demand.
Potable water is provided for the City of South San Francisco by the California Water Service
Company (CWSC) and the Westborough County Water District (WCWD). CWSC provides
water to the area east of Interstate 280 (I-280) in South San Francisco, including the Project site,
and its service areas includes the City of Colma and the Broadmo
portion of South San Francisco west of I-280. CWCS receives water from the City and County
of SanFrancisco, through the San Francisco Public Utilities Commission.
CWSC drafted and adopted an Urban Water Management Plan (UWMP) i
was established in accordance with the California Urban Water Ma
(Division 6, Part 2.6 of the Water Code, Section 10610-10656). Water Code section 10910,
subdivision(c)(2) and Government Code section 66473.7, subdivision (c)(1) note that it is
acceptable to use the most recently adopted UWMP to assess water
the California Urban Water Management Planning Act and SB 610. Between sources guaranteed
by a settlement agreement and the purchase of the Los Trancos Co
has a total Supply Assurance Allocation of 35.5 million gallons
25
indefinitely. The UWMP projected that the South San Francisco District population would
increase from 55,024 in 2000 to 64,050 in 2020; an increase of a
year. CWSC developed an Integrated Long Term Water Supply Plan (ILTWSP) for
CWSC, 2006 Urban Water Management Plan for South San Francisco,
25
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peninsula districts in 2010. The findings of the ILTWSP recommend continuing with
conservation and further evaluating desalination and water trans
The population of the CWSC service area is projected to be 64,05and 70,548by 2040.
South San Franciscos total population is anticipated to be approximately 69,810 in
service area population projections for CWSC are approximately 8
population of South San Francisco. Therefore, in 2020, it is anticipated that the CWSC service
population area will be 57,678,providing adequate water supply for existing and projected
26
development;particularly in light of the conservation efforts identified bel.
The Project would be required to comply with the California Green Building Code which
identifies measures to reduce water consumption, reduce building
energy consumption in both the construction and operation of bui
building (outlined in Chapter 1, Legislative Framework). The regulations prescribe methods
to test, report, maintain, and improve the measures employed to
sustainability.
The Project is one single family residence that for the City has planned for since the
th
mid-20century. The Project would not result in a cumulatively considerable or Project
related impact. The Project would not result in a need to obtain new water alloc
serve existing, Project, or the development projections contained in the South San
Francisco General Plan, and result in a less than significant impact.
f and g) Solid Waste
Significance Criteria: The Project would have a significant environmental impact if it
served by a landfill with inadequate permitted capacity to accomlid waste
disposal needs, or if it were to fail to fully comply with feder
regulations related to solid waste.
The California Integrated Waste Management Board (CIWMB) manages
and disposal data for South San Francisco. Non-recyclable or non-compostable waste is
disposed at Ox Mountain landfill near Half Moon Bay. The closurset
for 2023.
UWMP, 2006 and South El Camino Real General Plan Amendment and EIR, City of South San Francisco,
26
and Bhatia, November, 2009, updated by Knapp Consulting October
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CIWMB notes South San Franciscos solid waste generation is 7.76day.
Solid waste projected at build-out (year 2020) is anticipated to be 276 tons per day. The Ox
Mountain landfill has a maximum permitted disposal rate of 3,598
Francisco. The total projected solid waste disposal needs for South San Francisco, based upon
27
cumulative projections, is 7.7 percent of the daily permitted wa
The City requires construction waste diversion as outlined in Chapter 1, Introduction as well as
recycling and composting waste associated with Project operations.
Construction and operation of the Project would generate a less
of solid waste for the landfill that will be serving it, and operation of the Project would be
in full compliance with all federal, state, and local statutes and regulations related to
solid waste, and result in no impact.
Utilities and Service Systems Finding: The wastewater treatment plant has the capacity to
treat Project and cumulative projected wastewater. The Project is one single-family residence
th
that has been planned for since the mid-20 century. The Project would not result in a
cumulatively considerable or Project-related impact. The Project would not result in a need to
obtain new water allocations to serve existing, Project, or the development projections contained
in the South San Francisco General Plan. The UWMP, adopted in 2006, shows adequate water is
available for the Project and projected cumulative development.
There is adequate capacity at Ox Mountain landfill for Project ad cumulative solid waste and
the City is meeting its 50 percent solid waste diversion mandate, and
operations of the Project would be required to incorporated LIDs
treatment; an improvement over existing conditions. Construction and operation of the Project
would generate a less than significant amount of solid waste, an
be in full compliance with all federal, state, and local statutes, and regulations related to solid
waste.
Stormwater is required to be treated on-site. The Project would not contribute individually or
cumulatively to water, wastewater, solid waste, stormwater, or u
South San Franciscos existing and projected waste stream generaclude an approximate 50 percent
27
demonstrated diversion rate (South El Camino Real General Plan A
Francisco, Dyatt and Bhatia, November, 2009, updated by Knapp Co
and initial study).
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3.18MFS
ANDATORY INDINGS OF IGNIFICANCE
Potentially Less Than Less Than
Environmental Factors and Focused Questions for
SignificantSignificant SignificantNo
Determination of Environmental Impact
with
Impact Impact Impact
Mitigation
XVIII.
MANDATORY FINDINGS OF
SIGNIFICANCE
a) Does the Project have the potential to X
degrade the quality of the environment,
substantially reduce the habitat of a 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?
X
b) Does the Project have impacts that are
individually limited, but cumulatively
considerable? (Cumulatively considerable
means that the incremental effects of a
Project are considerable when viewed in
connection with the effects of past
Projects, the effects of other current
Projects, and the effects of probable future
Projects.)
X
c)Does the Project have environmental
effects, which will cause substantial adverse
effects on human beings, either directly or
indirectly?
a) Quality of the Environment
All environmental impacts associated with aesthetics, agricultures, air quality,
greenhouse gas emissions, health risks, biological resources, cultural resourcesincluding
important examples of the major periods of California history orgeology and soils,
hazards and hazardous materials, hydrology and water quality, land use and planning, mineral
resources, noise, population and housing, public services, recreation, service systems
transportation and traffic and utilities and are considered less than significant without additional
mitigation measures. Construction and occupation of the Project would not impact the
environment
b) Cumulative Impacts
The Project has no cumulatively considerable impacts.
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c) Adverse Effects on Human Beings
The Project would not have environmental effects that would caustantial adverse effects
on human beings, either directly or indirectly.
SF:
UMMARY OF INDINGS
Aesthetics Finding: The Project would not have an impact on the aesthetics or sce
on the site or in the area. The Project is not located within a ally designated public vista, nor
would it result in the obstruction of a formally designated publ
The Project is not identified as a viewpoint parcel or as one co
1999). The Project would not conflict with an adopted planning policy regarding scenic vistas.
The Project would be built on the portion of the lot that is the
other single-family structures in the neighborhood. Massing would be reduced on the second
story. The second story,consisting of 733 square feet, would be 40 percent smaller than the
ground floor, consisting of 1,224 square feet.
The Project would provide a transition from the mass of the back-family structure
to the south and the single-family structures within the subdivision.
There would be no individual or cumulative impacts with respect , or
light and glare associated with the Project.
Agriculture and Timber Resources Finding: The Project would not adversely affect any
existing agricultural operations as none exist on the site. The P
agricultural resources individually or cumulatively and does notFarmland, Unique
Farmland, Farmland of Statewide Importance (Farmland) nor land imson Act
Contract. The site is not zoned for timberland production or in use as such, and would not cause
rezoning of forest land (as defined in the Public Resources Code
(as defined by Public Resources Code section 4526) or timberland zoned Timberland
Production (as defined by Government Code section 51104(g)).
Air Quality Finding: Project impacts that would be associated with construction-related
fugitive dust and combustion exhaust emissions would be less thawith
implementation of the Citys standard Air Quality Conditions of Approval.
The Project traffic would not cause the daily traffic volumes to
based on the circulation infrastructure and the projected traffigle-family house
typically generates nine vehicle trips per day. Therefore, impac
long-term operational CO exhaust emissions would be less than signifi
Odor impacts associated with construction and operation of the Pect would be less than
significant.
There would be a less-than-significant impact associated with, conflicting with, or obstruc
implementation of the applicable air quality plan.
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The health risk and hazard impacts to sensitive receptors from Pnstruction would be
less than significant with implementation of the Citys standard Air Quality Conditions of
Approval, as required by law.
The cumulative impacts would well below the BAAQMD significance
would not result in increased health impacts exceeding the Projectlevel thresholds, the Project
-
would also not result in a cumulatively considerable contributio
hazard impacts. Therefore, the cumulative health impacts would bsignificant.
South San Francisco CAP and it has been determined that the Project would not conflict with
the goals of AB 32 and the applicable CAP. Therefore the Project
stated regulations contained in the plans.
The Project would not result in an impact or contribute to a cumlative impact with respect to
GHG emissions. The Project would not conflict with the plans, po
adopted for the purpose of reducing GHG emissions. Therefore, th-
than-significant impact on climate change.
TheProject would not conflict with the plans, policies, and regulations adopted for the purpos
of reducing GHG emissions. No mitigation is required.
Biology Finding: After review of CNDDB reports and map overlays for the general P
area, and field evaluations of the site, the habitat was found to be highly distur
from other areas containing sensitive habitat. The Applicant pr
nesting season or in compliance with biological protocol for protory birds. As a
result, the site is considered to be of very low value for plant
for sensitive species of plants and animals. No significant biol
full development of the Project site.
Cultural Resources Finding: There are no structures on the Project site. The Project wou
have a less than significant impact on archaeological or paleont
than a mile from the historic baylands, contains no culturally significant soils in the geotechnical
boring, and the disturbance from the grading that occurred in th
Geology and Soils Finding: There are no active faults underlying the site and the neares
one is the San Andreas Fault, located about 2.9 miles southwest. Implementation of the
geotechnical measures required by law (the Citys standard permi
review of all geotechnical reports and the final recommendations
Project) are proposed as part of the Project and identified in the CEQA document. Detailed
earthwork and foundation requirements for design and constructiotheProject will be
implemented. GeoTrinity (or qualified successor) will review the and specifications
to assure quality control. GeoTrinity will be on site full time during the initial
intermittently during the remaining site workandwill as necessary make changes to practices
and methods to assure the safety and stability of the Project ans. CSA will
be present on the Project site intermittently to oversee grading
measures identified by GeoTrinity and CSA would reduce geologic instability to less than
significant. The Project would have no impact on soils due to septic systems as the Project
would be connected to the Citys wastewater system.
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Hazards and Hazardous Materials Finding: The Project is a sensitive receptor and not a
source of hazardous materials. The Project would have no impact or handling
of hazardous materials or wastes on schools within a quarter of
environmental contamination posed by the sites listed on the Cor
impact of the Project with regard to the use of hazardous materiould be less than significant
and similar to other residential uses in the neighborhood. The P
less than significant impact with respect to the release of haza
construction.
There are no emergency response or evacuation plans in effect in the Project vicinity. The
the Project would have no impact on the implementation of any ad
plan or emergency evacuation plan. The Project is not within 2 m
and would have no impact on such use. Project impacts relating t be less
than significant with implementation of the conditions of approv
Hydrology and Water Quality Finding: The Citys standard conditions of approval which
implement state, federal and local regulations are required by l
any potential water quality impacts as a result of Project const
Project site is 348 feet above msl, would be outside the runup zone subject to inundation by a
500-year tsunami and would be outside the any potential tsunami haza
Flood Zone X and not subject to an 100-year flood event. No mitigation measures, above those
required by the City as a matter of law, are identified. The Project would not result in an
or contribute to a cumulative impact to hydrology or water quali
Land Use Finding: The Project would not physically divide an established community. T
site is planned for a single-family use and the Project is consistent with the planned uses.
are no conservation or natural community conservation plans that
area. The Project would not result in any individually or cumulable impacts.
Minerals Finding: The Project site does not contain any local or regionally signif
resources. The Project would not result in an impact or contrib
mineral resources.
Noise Finding: The implementation of measures the Applicant proposes would ensure that the
Project complies with the South San Francisco Noise Ordinance an
short-term noise impacts at sensitive receptors in the Project vicinit
noise would be a less-than-significant impact with implementation of the measures the Applicant
proposes as part of the Project.
The temporary construction vibration associated with on-site equipment would not be
anticipated to expose sensitive receptors to or generate excessive groundborne vibration or
groundborne vibration levels, and would result in a less-than-significant impact.
The Project is not located within two miles of a private airstri
dB SFO noise contour. Therefore, the Project would result in a less-than-significant impact with
respect to excessive aircraft noise exposure.
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Population and Housing Finding: The Project site has been planned for a residential use
since the 1950s. The Project site is vacant and would add one housing unit and not displace
housing units or residents.
Public Services Finding: The Project was reviewed by Police and Fire Department
representatives and staffing or facility needs were not identifi
the Project site would not increase the demand for public services ind
Parks and Recreation Finding: The Project, the addition of one single-family residence,
th
planned for since the mid-20 century would not result in an individual or cumulatively
considerable impact on parks and recreation.
Transportation Finding: The Project would not impact the streets, pose hazards associate
with its use, or pose incompatible land uses. Police and Fire re
issues or concerns with respect to emergency access. The development patt
neighborhood was designed to accommodate residential uses. The
impacts associated with emergency access. The Project would resu
alternate transportation modes or conflict with adopted policies
public transit, pedestrian facilities, or otherwise decrease the
facilities. The Project is a compatible land use with the neighbhood and will replace sidewalks,
driveway approaches and curb and gutter as required by the City
approval.
Utilities and Service Systems Finding: The wastewater treatment plant has the capacity to
treat Project and cumulative projected wastewater. The Project is one single family residence
th
that has been planned for since the mid-20 century. The Project would not result in a
cumulatively considerable or Project-related impact. The Project would not result in a need to
obtainnew water allocations to serve existing, Project or the developm
in the South San Francisco General Plan. The UWMP, adopted in 2006, shows adequate water is
available for the Project and projected cumulative development.
There is adequate capacity at Ox Mountain landfill for Project and cum
the City is meeting its 50 percent solid waste diversion mandate,and
operations of the Project would be required to incorporated LIDss for stormwater
treatment; an improvement over existing conditions. Construction
would generate a less than significant amount of solid waste, an
be in full compliance with all federal, state, and local statutes, and regulations related to solid
waste.
Stormwater is required to be treated on-site. The Project would not contribute individually or
cumulatively to water, wastewater, solid waste, stormwater, or u
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AA
PPENDIX
Q
A
IR UALITY
Construction and Operational Emission Modeling, RCH Group. November 2015.
CalEEmod Output Files, RCH Group. November 2015.
A
PPLICANT
Environmental Mitigation Measures [proposed by Applicant], Vinal Nand. December 2, 2015.
B
IOLOGY
Michael Marangio, Biological Resources Assessment Prepared for Allison Knapp Wollam, Consulting, Proposed
Residence, 901 Larch Avenue, South San Francisco, California. November 10, 2015.
G
EOLOGY
Applicants Reports-GeoTrinity
GeoTrinityConsultants, Inc., Geotechnical and Geologic Investigation, Residential Development
Avenue, South San Francisco, California. May 1, 2015.
GeoTrinity Consultants, Inc., Supplemental Letter for May 2015 Report and August 6, 2015 Plans August
18, 2015.
GeoTrinity Consultants, Inc., Response to Peer Review Letter. September 23, 2015.
City Peer Review-Cotton Shires Associates
Cotton Shires Associates, Inc., Geotechnical Peer Review, Nand New Residence, 901 Larch Avenu. May 26,
2015.
Cotton Shires Associates, Inc., Supplemental Geotechnical Peer Review, Nand New Residence, 901 Larch
Avenue. October 2, 2015.
Appendix A
Construction and Operational Emissions
CalEEMod Output Files
-Annual
-Summer
-Winter
August 18, 2015
Mr. Vinaal Nand
585 Villaa Street #10
Daly Cityy, Californiaa 94014
Re: Supplementall Letter for MMay 2015 Reeport and Reevised (Auguust 6, 2015) Plans
RResidentialDDevelopmentt
901 Larch Avvenue
South San Fraancisco, Callifornia
Dear Mr.. Nand:
Our Mayy 2015 geoteechnical/geollogic report for the propposed develoopment was based on a sset of
drawingss dated Aprril 2015. TThe plans for the profpposed devellopment havve been reevised
somewhaat since thenn.
Accordinng to the graading and draainage plan prepared byy GeoTrinityy Consultantss dated Auguust 6,
2015, thee project wiill mainly coonsist of a ttwo-story, wwood- and cconcrete-framme, single faamily
house wiith 2,038 sqquare feet off reduced livving space wwith partiallly depressedd two-car gaarage.
Thus, thee residence wwill be slighhtly smaller. Also, the loocations and heights of tthe proposedd new
cut slopees will differr; some willl be taller and some shoorter. Specifically, the rrevised drawwings
show thaat 4- to 6-foot-tall retainning walls wwill support a new tieredd cut slope excavatedoon the
uphill (ssoutheast) sside of the residence for a smaall rear pattio. Basemeent walls uup to
approximmately 15 feeet tall will support andd form the nnortheastern walls of thhe residencee, and
walls up to approximmately 19 feeet tall will ssupport and form the sooutheasternaand southweestern
walls of tthe residencee.
In our oopinion, the conditions,conclusionns, and recoommendationns in our MMay 2015 reeport,
except foor the site rettaining wall foundation,remain appllicable to thee new propoosed developpment
configuraation and thhe aforementtioned reviseed plans. Duue to the prroximity of the site retaaining
walls, alll the site retaaining walls at the upperr terrace willl be entirely supported byy drilled pieers.
Shouldyyou have anyy questions oor require additional infoormation, pleease do not hhesitate to caall
7770 Pardee Lane, Suuite 101, Oakland, CACA 94621 Phone: 5510-383-9950 Fax: 510-383-9957
1 of 1
our projeect manager,Mr. Jerry RR. Yang, at 925-699-25500.
Sincerelyy,
it
GeoTriny Consultaants, Inc.
Jerry R. YYang, P.E. GG.E. Frank J. Groffie, P.G., C.E.G.
ProjectMManagerChief Enngineering Geeologist
fjg:mac
Copies: AAddressee (1)
MMr. Ted Sayre, CCSA (1)
RRozalynne Thommpson, City off South San Fraancisco (1)
7770 Pardee Lane, Suuite 101, Oakland, CACA 94621 Phone: 5510-383-9950 Fax: 510-383-9957
2 of 2
SSeptember 23, 2015
MMr. Vinal Naand
9901 Larch AAvenue
SSouth San Frrancisco, Caalifornia
SSubject:Response to Peer Revview
ProposedResidentialDevelopmennt
901 Larchh Avenue
South Sann Francisco, California
GTCProjject No. CS-1481
DDear Mr. Naand:
TThis letter ppresents ouur responses to the doccument titleedGeotechnnical Peer Review, Naand New
RResidence,9901 Larch Avvenue, datedd May 26, 20015, preparedd by Cotton Shires & Asssociates forr the City
oof South Saan Franciscoo. The May 26 review letter preseents commennts on threee documentss for the
pproject: GTCC’s May 1 geologic/geotechnicalrreport, GTCC’s April 211 set of archhitectural pllans, and
GGTC’s Apriil 22 set of grading plans. Cerrtain of thhe responses below prresent suppplemental
rrecommendaations, and thhus your conntractor shouuld be made aware of thee contents off this letter.
CComment 1 concerns thhe excavatioon for the new residencce at 901 Laarch Avenue with regard to the
Responnse
eexisting residdence at 8599 Larch Avenue.: This is a potentiallyy sensitive aarea in that thhere’s an
eexisting house next doorr, and we apppreciate thee reviewers’ attention too this area. TThe floor off the new
bbasement wiill be at Eleev. 108 ft (llocal datumm), roughly llevel with LLarch Avenuue. The gradde at the
eexisting residdence is at aapprox. Elevv. 108 ft, also roughly leevel with Laarch Avenue. Thus, an immaginary
pplane projeccted from thhe bottom eedge of thee existing reesidential fooundation too the propoosed new
eexcavationwwould slope very gently,, if at all, towward the neww basement excavation. The propossed 10-ft-
ddeep cut for the new baasement is duue to the local modifiedd topographhy, which inccludes the nnortheast-
th
ffacing mid-220-century cut slope. AAs shown in Figure 5 (CCross Sectionn B) of our rreport, if a pportion of
tthe soil/rockk between thhe existing aand new struuctures weree to move innto the new excavation,it would
llikely involvve only a smaall volume oof material annd not affectt the existingg house.
Respoonse
Comment 2 concerns freeeboard atopp retaining wwalls.: The neext version of the plans wwill show
tthe freeboarrd atop certain retaining walls as recommendded in our MMay 1 repoort. Specificcally, the
rretaining waalls downsloppe of the existing fill weedge (see Fiigure 3 in reeport) will bbe shown witth 2 ft of
ffreeboard.WWe do not believe that ffreeboard is needed atopp other retaaining walls:: the originaal natural
Page 1 of 3
01 Larch Avenue, Response Leter 9/24/15
99tt
gground surfaace upslope iis at a gradieent of 2½H:1V, is underrlain by thinn (1 ft of) sooil, and has ddisplayed
nno evidence of mass movvement.
RResponse
CComment 3 concerns suurface drainaage along thhe tops of ceertain retainiing walls. :OOur report
((specifically at the end oof Section 4..5) recommeends surfacedrainage diitches atop thhe retaining walls on
tthe southwesst and southeeast sides off the residencce. The nextt version of tthe project pplans will shhow these
rrecommendeed subdrain aand back draain behind thhe retaining wwalls.
Responsee
CComment 4 concerns retaining walll foundations.: The next version of tthe project pplans will
sshow all rettaining wallss to be suppported with pier foundaations to relieve the suurcharge loaad on the
aadjacent tall basement wwalls in the sttructural design.
Responnse
CComment 5 concerns seeismic desiggn parameteers for the rretaining waalls.: In our sstructural
ddesign, we ccan verify an additionall force behinnd the retainning wall coonsidered ass an equivallent fluid
wweight of 25 pcf for bothh native soils and Caltraans standard backfill matterials, actinng at a distannce of 2/3
oof the heightt of the walll from the base of the reetaining walll under a Saafety Factorr of 1.5. Hoowever in
oour experiennce, the seismmic load is uusually oversshadowed byy the Static SSafety Factoor of 2.5 for common
bbox type singgle family hoouse except for single roow of tall eleevated bridge abutment wwall.
CComment 6 concerns thhe potential for tumblinng rocks to impact thee existing neeighboringrresidence
Respponse
dduring the coonstructionpperiod.: We recommend tthat a tempoorary fence bbe installed aalong the
bboundary beetween the ttwo propertiies and dowwnslope of tthe excavatiion work. TThis fence shhould be
cconstructedof geotextile (e.g., biaxxial, low–mooderate strenngth), extennd 4 ft (minn.) above thee ground
ssurface, and be tied to stteel fence sttakes/posts ddriven into tthe ground. BBased on thhe topographhy and on
tthe subsurfacce data pressented in ourr May 1 repport, we beliieve a rock tumbling haazard will be present
oonly early inn the excavattion work annd will involvve rocks smaaller than appprox. 8 inchhes in diametter.
Reesponse
CComment 7 concerns an estimate offconstructionn timing. : In our experieence, the connstruction
wwill start around late Aprril in 2016 aand the earthwwork and drrill piers usuaally will take about 3 moonths.
IIf you have aany questionn regarding tthese responnses to the peer-reviewccomments,pplease do not hesitate
tto call our offfice. Thank you.
SSincerely,
GGeoTrinityConsultantss, Inc.
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01 Larch Avenue, Response Leter 9/24/15
99tt
Jerry Yang, P.E., G.E.
Project Manager
JJY/LK
Copies: Addressee (2)
Mr. Ted Sayre-Cotton Shires & Associates (1)
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