Planning & Design Meetings CEQA Mitigated Negative Declaration 10/30/2009 - MinutesGunn High School Master Plan 1 ESA / 209002
Initial Study September 2009
GUNN HIGH SCHOOL MASTER PLAN
Initial Study and Environmental Checklist Form California Environmental Quality Act (CEQA)
1. Project Title: Gunn High School Master Plan
2. Lead Agency Name and Address: Palo Alto Unified School District
25 Churchill Avenue, Building D
Palo Alto, CA 94306
3. Contact Person and Phone Number: Tom Hodges, Program Director
Telephone: (650) 329-3972
E-Mail: thodges@pausd.org
4. Project Location: 780 Arastradero Road
Palo Alto, CA 94306
5. Santa Clara County Assessor’s Parcel Number: 142-17-032
6. Project Sponsor’s Name and Address: Palo Alto Unified School District
25 Churchill Avenue
Building D
Palo Alto, CA 94306
7. General Plan Designation: School District Lands
8. Zoning: PF – Public Facilities
9. Description of Project: The proposed project includes construction of new buildings,
renovation of existing structures, and other site improvements as part of the Master Plan for
the Gunn High School. See Project Description, below, for details of the Master Plan.
10. Surrounding Land Uses and Setting: The project site is within an urban area in the City of
Palo Alto. Existing adjacent land uses include residential areas on the north and east, Alta
Mesa Cemetery on the south, and the Veterans Affairs (VA) Palo Alto Health Care Systems
campus on the west.
11. Other public agencies whose approval is required (e.g., permits, financing approval, or
participation agreement): During the Site Improvements, the project may require an
encroachment permit from the City of Palo Alto for construction within Arastradero Road. A
permit will also be required from the Bay Area Air Quality Management District
(BAAQMD) for demolition of existing structures.
Initial Study
Gunn High School Master Plan 3 ESA / 209002
Initial Study September 2009
Project Description
Background
The Palo Alto Unified School District (PAUSD or District) was founded in 1893. The District
includes the City of Palo Alto, Stanford University, and areas of Los Altos Hills, Palo Alto Hills,
and Portola Valley within its attendance area. See Figure 1 for attendance boundaries. The
PAUSD consists of twelve elementary schools (grades K-5), three middle schools (6-8), and two
high schools (9-12). In addition, the District operates a pre-school, Young Fives program, a self-
supporting Adult School, the Hospital School at Stanford’s Lucille Packard Children’s Hospital,
and summer school. The total District enrollment for the 2008/2009 school year was
approximately 11,430 students.
Gunn High School is located at 780 Arastradero Rd in Palo Alto and has an existing student
capacity of 1,950. Enrollment at Gunn has steadily increased over the last ten years from 1,508
students in the 1998/1999 school year to 1,917 for the current (2008/2009) school year. The
school employs approximately 135 certified staff and administrative staff. The projected capacity
of Gunn High School at completion of the proposed improvements in 2018 would be 2,300
students, an increase of approximately 18 percent.
Long Range Facilities Master Plan / Measure A
In January 2006, PAUSD staff presented to the Board of Education a School Site Status Report
that provided an assessment of the improvements made to District facilities during the Building
for Excellence Program and outlined the future needs of the PAUSD.1 The Board authorized staff
to prepare a 20-year facilities master plan that would identify facilities needs that were not funded
by the Building for Excellence Program and outline a growth strategy to accommodate projected
increases in enrollment.
The Long Range Facilities Master Plan (LRFMP) is a conceptual document that was presented to
the Board in April 2007. The LRFMP includes and implementation plan for capital
improvements, planned maintenance, and equipment and furnishing needs over the next twenty
years. This document also incorporates current codes and principles from the Collaborative for
High Performance Schools (CHPS).2 These standards incorporate the latest green building
practices to reduce operating costs through sustainable and energy efficient design, reduce
environmental impact, and increase building life, while creating schools that are healthy and
comfortable for students and staff.
1 “Building for Excellence” was a 1995 tax measure that funds upgrading school facilities and some technology
items, such as computers.
2 The Collaborative for High Performance Schools (CHPS) is the United States’ first green building rating program
especially designed for K-12 schools. CHPS provides information and resources to schools in order to facilitate the
construction and operation of high performance institutions. A high performance school is energy and resource
efficient as well as healthy, comfortable, well lit, and containing the amenities for a quality education.
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Palo Alto Unified School District
I280
Lapkoff & Gobalet Demographic Research, Inc. 6/2007www.Demographers.com
HAMILTONAVE
Richard W. LymanGraduate Residencesplus Santa Teresa Lanehomes assigned to Palo Alto HS
Gunn High School Master Plan . 209002
Figure 1
High School Attendance Boundaries,
Palo Alto Unified School District
SOURCE: Lapkoff & Gobalet Demographic Research, Inc.
Initial Study
Gunn High School Master Plan 5 ESA / 209002
Initial Study September 2009
On June 3, 2008, voters in the District approved a $378 million bond issue, Measure A (Palo Alto
School Modernization and Expansion Bond of 2008), that would provide funding to implement
the LRFMP.
The proposed project, the Gunn High School Master Plan (Master Plan) is a component of the
LRFMP. PAUSD, serving as Lead Agency under the California Environmental Quality Act
(CEQA), is completing the required environmental review of the Master Plan pursuant to CEQA,
prior to approval of the plan. In accordance with the CEQA Guidelines, PAUSD has prepared an
Initial Study to determine the potential environmental consequences of adoption and
implementation of the proposed Master Plan. This Initial Study provides the necessary
information to inform PAUSD, other responsible agencies, and the public of the nature of the
project and its potential effect on the environment.
Project Location and Existing Site Characteristics
Gunn High School was constructed in 1964 on an approximately 48-acre site (the project site)
northeast of the intersection of Arastradero Road and Foothill Expressway (see Figure 2).
Adjacent land uses include residential areas to the north and east, Alta Mesa Cemetery to the
south across Arastradero Road, and a Veterans Affairs hospital complex to the west.
The school is composed of 17 permanent buildings clustered on the southern portion of the campus.
These include the following: Administrative Building, Student Activities Building, cluster of four
buildings for language and social studies instruction, cluster of four buildings for math and science
instruction, Resource Materials Building, Music Building, Art Building, Spangenberg Auditorium,
Business Education and Home Economics Building, Industrial Arts Building, and Gymnasium. The
original buildings were constructed in 1964, with a new Library Building and Science facility added
in 2003. The architectural style features single-story structures (with the exception of the Gym and
Spangenberg Auditorium) with exterior wood siding, small window openings, and attached covered
walkways supported by concrete columns and mansard roofs. Most of the southern portion of the
campus is paved with trees and other landscaping interspersed between the buildings. All buildings,
with the exception of the interiors to the Gym, Spangenberg Auditorium, Administration, and the
old Library Building were, fully renovated under the Building for Excellence Program. The campus
also includes approximately 26 relocatable classrooms.
Recreational facilities are located primarily on the northern section of the campus and include a
gym, pool, football field, baseball and softball diamonds, athletic field, outdoor track, seven
tennis courts, and five basketball courts.
The main parking lot is located on the southeast portion of the site, with vehicular access off
Arastradero Road. The campus overall contains approximately 461 parking spaces.
The campus has several public easements including the Hetch-Hetchy water easement running
diagonally across the site in the east-west direction, as well as PG&E and sewer easements. In
addition, a Santa Clara Valley Water District retention basin is located north of the relocatable
classroom buildings.
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Gunn High School Master Plan . 209002
Figure 2
Project Location
SOURCE: ESA
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Initial Study
Gunn High School Master Plan 7 ESA / 209002
Initial Study September 2009
Proposed Improvements
The proposed project features construction of new buildings and other structures; renovation of
some existing buildings; utility and infrastructure improvements; open space and landscaping
enhancements; entry and courtyard upgrades; and pedestrian/bicycle/vehicular circulation
improvements.
Specific components of the proposed Master Plan improvements are summarized in Table 1,
below. Construction of individual projects on the campus would occur in groups or phases over
the time period of the Master Plan, with buildout targeted for 2017. Specific projects within each
project group would be constructed over the same general time period, but not necessarily
simultaneously. Locations of proposed projects are indicated on Figures 3 through 7.
Construction of a new Aquatics Center and renovation of the existing Industrial Arts building are
currently underway with completion anticipated during the summer and fall of 2009, respectively.
Renovations of existing buildings may include, but are not limited to, upgrades to electrical,
communication, water and wastewater systems; replacement or modification of heating and
cooling systems; lighting improvements; replacement of roofs; upgrade or addition of restrooms;
improvements to comply with the Americans with Disabilities Act (ADA) and California Title 24
requirements; and exterior improvements to walls, doors, and windows.
Group 1
Projects under the first group include construction of two new classroom buildings and a second
gymnasium. The new gym would be located just east of the pool, which would require
modifications to the tennis and basketball courts in this area. At buildout, Gunn would have eight
tennis and three basketball courts. The existing gym would be modernized with new equipment,
refinished floors, and other interior improvements. Proposed Classroom Building A would
include 28 classrooms, offices, conference room, and restrooms. This two-story building is
intended to replace the 28 relocatable classrooms currently located at this site (known as Titan
Village) and those located near the Miranda Street entrance to the campus. These relocatable
classrooms would be temporarily moved to the parking area adjacent to the tennis and basketball
courts. Classroom Building B would be a single-story structure with five classrooms for world
languages and program support as well as textbook storage. This phase would include an interim
improvement to the parking and drop-off areas that are designed to provide greater separation
between these two zones and provide easier access to the school during drop-off during
construction and while the relocatables are placed on the parking lot.
Group 2
Group 2 includes construction of a new Performing Arts Center to replace existing inadequate
facilities in Building M. This new building would be located adjacent to the existing Spangenberg
Theater in order to provide protected connection to the backstage access, greenrooms, and other
theater facilities. Spangenberg would be updated as well with new lighting, finishes, and other
interior improvements. Other projects during this phase would include modernization of the
existing math wing building to accommodate the Special Education program, which is currently
Initial Study
Gunn High School Master Plan 8 ESA / 209002
Initial Study September 2009
located in the Resource Center building. Two general laboratory classrooms and a connector to
the prep area
Initial Study
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TABLE 1
MASTER PLAN PROJECT LIST
Phase Project Description Schedule/Timeline
Group 1 1a: Classroom Building A New two-story, 28-classroom building 2011 – 2012
1b: Classroom Building B New one-story, 6-classroom building
1c: Gymnasium New second gymnasium
1d: Existing Gymnasium Renovation of existing gymnasium
1e: Parking & Drop-Off Reconfiguration of parking and student drop-off
areas
1f: Utility & Infrastructure Miscellaneous utility and infrastructure
improvements
Group 2 2a: Performing Arts
Building New performing arts complex 2012 – 2014
2b: Campus Entry Entry and entry court improvements and
reconfiguration
2c: Spangenberg Theater Renovation of existing theater
2d: Special Education
Center Renovation of existing building
2e: Science Lab Two new classrooms
2f: Parking & Drop-Off Reconfiguration of parking and student drop-off areas
Group 3 3a: Spangenberg Theater Renovation of lobby and other areas TBD
3b: Amphitheater Improvements to existing amphitheater
Group 4 4a: Student Activities /
Media Arts / Conference New two-story multiple-use building TBD
4b: Classroom Building Renovation of L-wings for existing building
4c: Art Building Additional classrooms and renovation to A-wing
4d: West Access Road &
Parking Reconfiguration of access and parking area
Group 5 5a: Guidance & Counseling
Center Renovation of existing building TBD
5b: Administration Building Addition and renovation of existing building
5c: Quad Landscaping and other improvements to
expanded quad
5d: Field Structure New athletics storage and snack bar facility
5e: Site Improvements Miscellaneous landscaping and pedestrian
improvements
5f: RC Building Demolition of existing building to accommodate
quad expansion
SOURCE: PAUSD, 2009
Gunn High School Master Plan . 209002Figure 3Gunn High School Master Plan, Group 1 ProjectsSOURCE: Deems Lewis McKinley
Gunn High School Master Plan . 209002Figure 4Gunn High School Master Plan, Group 2 ProjectsSOURCE: Deems Lewis McKinley
Gunn High School Master Plan . 209002Figure 5Gunn High School Master Plan, Group 3 ProjectsSOURCE: Deems Lewis McKinley
Gunn High School Master Plan . 209002Figure 6Gunn High School Master Plan, Group 4 ProjectsSOURCE: Deems Lewis McKinley
Gunn High School Master Plan . 209002Figure 7Gunn High School Master Plan, Group 5 ProjectsSOURCE: Deems Lewis McKinley
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and office would be added to the Science Lab. A redesigned entry area and entry courtyard would
be constructed to form a coherent gateway to the campus from the parking area adjacent to
Spangenberg Theater and the new Performing Arts complex. The existing Music Building would
be demolished in order to create this new entryway. Finally, the parking area would be
reconfigured again after the relocatable classrooms are removed from the campus.
Group 3 (Unfunded)3
Spangenberg Theater would be renovated under this phase with the addition of a focal lobby area
to be used for performances and other activities. A connector to the new Performing Arts Center
constructed during Group 2 would also be added. The outdoor amphitheater adjacent to
Spangenberg on the north would be updated with a new stage and landscaping.
Group 4 (Unfunded)
Group 4 includes a new two-story, centrally-located building to serve as a Student Activities
Center. It would also include the media arts program, additional social studies classrooms, and a
conference center. An existing classroom building would be demolished to make room for the
new Student Center. Other existing buildings would be renovated during this phase. The three
L-wing classroom buildings would be utilized for the expanded social studies and world
languages departments. The Art Building would feature upgraded classrooms and additional
classrooms would be added to the existing A-wing. Access to the campus via the west access road
off Miranda Avenue would be reconfigured to provide a turn-around, parking, and
pedestrian/bicycle paths.
Group 5 (Unfunded)
The existing Administration Building-AD2 would be modernized and converted into a guidance
and counseling center during this phase. The staff lounge and patio would be relocated to the
south side of the building as part of the renovation. Administration Building-AD1 would be
renovated to accommodate administrative functions previously located in AD2, and the cafeteria
would be upgraded. This phase would also include major changes to the Quad. The existing
Resource Center building would be demolished to allow for an expanded Quad with new
landscape/hardscape, furnishings, and other pedestrian improvements. In addition, a new Field
Structure would be constructed just north of the football field. This building would feature snack
bar facilities as well as storage space for soccer, track and field, lacrosse, and physical education
programs.
Sources
California Department of Education, DataQuest, http://dq.cde.ca.gov/dataquest, accessed June 24,
2009.
Palo Alto Unified School District (PAUSD), www.pausd.org, accessed June 2009.
PAUSD, Gunn High School Master Plan, 2009.
3 Design of specific projects listed in Groups 3, 4 and 5 is currently unfunded.
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Environmental Impacts
Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
1. Aesthetics
Would the project:
a) Have a substantial adverse effect on a scenic vista?
b) Substantially damage scenic resources, including,
but not limited to, trees, rock outcroppings, and
historic buildings within a state scenic highway?
c) Substantially degrade the existing visual character or
quality of the site and its surroundings?
d) Create a new source of substantial light or glare
which would adversely affect day or nighttime views
in the area?
Discussion
a, b) No Impact. Gunn High School is located on a trapezoidal shaped block that is located off of
Arastradero Road near Foothill Expressway in a southwestern portion of Palo Alto. There are
no roadways near Gunn High School that have been designated as or are considered eligible
to be a state scenic highway, nor is the project site visible from a state scenic highway
(Caltrans, 2009). In addition, there are no scenic resources, including trees, rock
outcroppings, and historic resources, in the vicinity of the campus. Therefore, the proposed
project would not result in impacts related to scenic resources within a state scenic highway.
The City of Palo Alto considers Arastradero Road west of Foothill Expressway and
Foothill Expressway to be scenic routes (City of Palo Alto, 2007). While the segment of
Arastradero Road that is in front of the high school is not considered to be a scenic route, a
small portion of the high school campus is visible from the intersection of Foothill
Expressway and Arastradero Road (see Figure 8). Arastradero Road is generally the only
roadway that provides views of Gunn’s campus (intermittent views of the sports facilities
are available from Miranda Road). Other public views of the campus are provided by the
publicly accessible pathways that line both the eastern and western edges of the campus.
Gunn High School consists of a collection of classroom buildings that are concentrated in
the southwestern portion of the campus. Parking lots and internal roadways comprise the
southeastern portion and the remainder of campus consists of sports facilities, including
tennis courts, a baseball stadium, football stadium, and an aquatic center. The buildings on
Gunn’s campus maintain a uniform style throughout and are characterized by square or
rectangular massing, mansard roofs and colonnades (see Figures 9 and 10). In addition to
maintaining a consistent style, the buildings also include a common color scheme with
brown siding, white columns, and brown roofs. While the majority of the buildings are one
story, there are a few two-story (in height) buildings on campus, including the library,
theater and the gymnasium.
Gunn High School Master Plan . 209002
Figure 8
Existing Views of Gunn High School Campus
SOURCE: ESA
View of campus near Foothill Expressway and Arastradero Road
View of campus near Foothill Expressway and Arastradero Road
Gunn High School Master Plan . 209002
Figure 9
Existing Views of Gunn High School Campus
SOURCE: ESA
View of campus from Arastradero Road looking east
View of campus from Arastradero Road looking west
Gunn High School Master Plan . 209002
Figure 10
Existing Views of Gunn High School Campus
SOURCE: ESA
View of campus buildings
View of campus buildings
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Buildout of the Master Plan would not affect views from the intersection of Arastradero
Road and Foothill Expressway. Currently, views of the campus from the intersection of
Arastradero Road and Foothill Expressway consist of the roof and some of the columns of
the building located on the southwestern-most corner. Under the proposed project, one
small classroom building would be constructed along the Arastradero Road frontage of
campus. View of this new classroom building from the intersection of Foothill Expressway
and Arastradero Road would be blocked by the existing classroom building and views from
that intersection would not change. Therefore, the proposed project would not affect views
from those scenic routes and impacts related to scenic vistas would be less than significant.
c) Less Than Significant. Buildout of the Master Plan would result in the construction of
new buildings and renovations to existing buildings throughout the campus. Very few of
these improvements would even be visible from the publicly accessible viewpoints. As
noted above, one relatively small classroom building would be constructed along the
Arastradero Road frontage of campus. This building would be set back approximately 100
feet from the roadway. In addition, the elevation of the campus slopes down from the edge
of the roadway, which slightly diminishes the presence of the buildings along the roadway.
All new construction and renovations would be designed to be compatible with the existing
style of buildings on campus in terms of height, massing and color scheme. In addition, the
development pattern of the campus would be maintained with all classroom buildings being
concentrated in the southwestern portion of campus, parking lots would be reconfigured but
not be relocated, and the sports facilities would remain intact in their current locations with
only minor upgrades. Generally, the Master Plan would result in better utilization of the
space on campus, but would not affect the overall character of the site and its surrounding.
Therefore, the proposed project would result in less than significant impacts on the
character of the site and its surroundings.
d) Less Than Significant. New buildings developed under the Master Plan would include
fixed exterior lighting in order to promote safety. Gunn High School is located in a
suburban environment that has some existing sources of light and glare associated with
nearby land uses. Nearby homes and businesses cast light from windows or from outdoor
security lighting and parking lots. Arastradero Road and Foothill Expressway provide street
lighting and are also additional sources of light and glare. Ambient light generated by new
buildings that could be developed or improved under the plan would be minimized and
partially screened by trees and surrounding buildings. Therefore, the proposed project
would not result in adverse light or glare impacts at their specific sites or in the surrounding
areas.
Sources
City of Palo Alto, 2007. Palo Alto Comprehensive Plan, Land Use Element, adopted July 17,
2007.
California Department of Transportation (Caltrans), 2009. California Scenic Highway Mapping
System website, http://www.dot.ca.gov/hq/LandArch/scenic_highways/index.htm, accessed
July 21, 2009.
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Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
2. 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
Department of Conservation as an optional model to use in assessing impacts on agriculture and farmland.
Would the project:
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?
b) Conflict with existing zoning for agricultural use, or a
Williamson Act contract?
c) Involve other changes in the existing environment
which, due to their location or nature, could result in
conversion of Farmland, to non-agricultural use?
Discussion
a–c) No Impact. The project site is not located on or near any agricultural land, nor is the site
zoned for agricultural uses. The project site, as with the majority of developed land in the
City of Palo Alto, is designated as Urban and Built-Up Land by the California Department
of Conservation (Department of Conservation, 2007). Therefore, the proposed project
would not convert farmland to non-agricultural use and would have no effect on farmland
or any property subject to a Williamson Act contract.
Sources
California Department of Conservation, Santa Clara County Important Farmland Map 2006,
August 2007.
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Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
3. Air Quality
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. Would the project:
a) Conflict with or obstruct implementation of the
applicable air quality plan?
b) Violate any air quality standard or contribute
substantially to an existing or projected air quality
violation?
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 pollutant
concentrations?
e) Frequently create objectionable odors affecting a
substantial number of people?
f) Conflict with the state goal of reducing greenhouse
gas emissions in California to 1990 levels by 2020,
as set forth by the timetable established in AB 32,
California Global Warming Solutions Act of 2006?
Discussion
a) Less than Significant. The project site is located in the City of Palo Alto, within the
San Francisco Bay Area Air Basin (Bay Area). The Bay Area experiences occasional
violations of ozone and particulate matter (PM-10 and PM-2.5) standards. Air Quality
standards and regulations are enforced in the Bay Area Air Basin by the Bay Area Air
Quality Management District (BAAQMD).
When a project is proposed in a city with a general plan that is consistent with the most
recently adopted Clean Air Plan and if the project is consistent with the land use
designation of the general plan, then the project is considered consistent with applicable air
quality plans and policies.
As discussed in Checklist Item 9, Land Use and Planning, of this Initial Study, the campus
improvements and educational uses proposed as part of the project would not substantially
conflict with the goals and policies in the City of Palo Alto Comprehensive Plan. Moreover,
although not bound by local land use ordinances, project components proposed by the
PAUSD would nonetheless be consistent with the land use designation and zoning for the
campus.
The applicable Clean Air Plan (CAP) is the Bay Area 2005 Ozone Strategy. The City’s
General Plan is consistent with the CAP because data and projections from the General
Plan are incorporated into the CAP. The project, therefore, is consistent with the plan. This
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is a less-than-significant impact because the project would not conflict with the region’s air
quality management plan.
b, c) Less Than Significant with Mitigation.
Construction Emissions
This analysis evaluates the effect of the site grading and the construction of Master Plan
improvements on the local and regional air quality. Development of this project could
affect local pollutant concentrations in two ways. First, during construction, the project
would affect local particulate concentrations by generating dust. Over the long-term, the
project might result in a slight increase in emissions due to new motor vehicle trips
associated with accommodation of a larger student population.
Activities such as grading and excavation would generate substantial amounts of dust
(including PM-10) from “fugitive” sources, such as proposed earthmoving activities to
improve athletic fields and to excavate foundations and vehicle travel over unpaved
surfaces, and lesser amounts of other criteria pollutants from the operation of heavy
equipment construction machinery (primarily diesel operated) and construction worker
automobile trips (primarily gasoline operated). Construction-related dust emissions would
vary from day to day, depending on the level and type of activity, silt content of the soil,
and the weather. Construction activities may result in significant quantities of dust, and as a
result, local visibility and PM-10 concentrations may be adversely affected on a temporary
basis during the construction period. In addition, larger dust particles would settle out of the
air close to the construction site resulting in a potential soiling nuisance for adjacent uses.
For the evaluation of construction-phase impacts, BAAQMD does not require a detailed
quantification of construction emissions. Instead, it recommends that evaluation of the
significance of impacts be based on a consideration of the control measures to be
implemented (BAAQMD, 1999). Generally, if appropriate measures are implemented to
reduce fugitive dust, then the residual impact can be presumed to be less than significant.
Without these measures, the impact is generally considered to be significant, particularly if
sensitive land uses (e.g., residential or scholastic) are located in the project vicinity.
The Master Plan improvements that would require the greatest degree of grading and
earthwork would be new building excavations for classrooms, the new gymnasium, the new
performing arts center, and the new student activities and media arts buildings. Other
project elements would disturb much smaller areas of earth and have fewer construction
impacts to localized PM-10 and PM-2.5 concentrations. All individual construction areas
would be less than one acre. Because construction grading would generate localized
increased concentrations of PM-10 and PM-2.5 in an area designated as non-attainment for
these pollutants, without appropriate dust mitigation, the impact would be significant.
Mitigation Measure AIR-1: During future construction, PAUSD shall require the
construction contractor to implement BAAQMD’s “basic” dust control procedures
which are required for all construction sites of less than four acres and which would
mitigate the potential impact to a less than significant level.
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Elements of the “basic” dust control program for project components that disturb
more than four acres shall include, but not necessarily be limited to the following:
Basic Control Measures
• Water all active construction areas at least twice daily. Watering should be
sufficient to prevent airborne dust from leaving the site. Increased watering
frequency may be necessary whenever wind speeds exceed 15 miles per hour.
Reclaimed water should be used whenever possible.
• Cover all trucks hauling soil, sand, and other loose materials or require all
trucks to maintain at least two feet of freeboard (i.e., the minimum required
space between the top of the load and the top of the trailer).
• Pave, apply water three times daily, or apply (non-toxic) soil stabilizers on all
unpaved access roads, parking areas and staging areas at construction sites.
• Sweep streets (with water sweepers using reclaimed water if possible) at the
end of each day if visible soil material is carried onto adjacent paved roads.
• Sweep streets daily (with water sweepers) if visible soil material is carried onto
adjacent public streets.
With implementation of these measures, project construction would not be expected to
violate any air quality standard or contribute to an existing or projected air quality violation
in the project vicinity.
Construction activities would also result in the emission of other criteria pollutants from
equipment exhaust, construction-related vehicular activity and construction worker
automobile trips. Emission levels for construction activities would vary depending on the
number and type of equipment, duration of use, operation schedules, and the number of
construction workers. Criteria pollutant emissions of ROG and NOx from these emission
sources would incrementally add to the regional atmospheric loading of ozone precursors
during project construction. BAAQMD CEQA Guidelines recognize that construction
equipment emit ozone precursors, but indicate that such emissions are included in the
emission inventory that is the basis for regional air quality plans. Therefore, construction
emissions would not be expected to impede attainment or maintenance of ozone standards
in the Bay Area (BAAQMD, 1999). The impact would therefore be less than significant.
Operational Emissions
The project would result in a net increase in emissions of criteria pollutants (ROG, NOx and
PM-10) primarily because of a resultant increase in average daily vehicle trips. Based on
the traffic analysis, the proposed change in land use would result in an increase of
approximately 532 net new daily vehicle trips. Increased vehicle trips would lead to a small
increase in ROG (approximately 2.7 pounds per day), NOx (approximately 2.2 pounds per
day) and PM-10 (approximately 6.9 pounds per day) due to vehicle exhaust. Increases in
emissions from stationary sources at the site (such as natural gas combustion for space and
water heating, landscaping, use of consumer products, etc.) would also be minimal
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(approximately 0.72 pounds per day of ROG and 1.06 pounds per day of NOx). Together,
operational emissions increases resulting from the project would represent approximately
ten percent or less of the quantities BAAQMD identifies as significant (80 pounds per day
of either ROG, NOx, or PM-10, individually). Therefore, once operational, the development
under the Master Plan would not significantly contribute to a violation of any air quality
standard in the area.
Cumulative Air Quality Impact
In combination with other future projects in the project vicinity, the construction and
operations of the proposed project would likely result in a small cumulative contribution to
increases in pollutant emissions, but these would have less than significant impacts to air
quality. Furthermore, with the implementation of mitigation measures, these impacts would
be reduced to less than significant levels.
d) Less than Significant with Mitigation. Construction activities could expose sensitive
receptors (students and residences located adjacent to the project site) to substantial
pollutant concentrations, principally PM-10, from fugitive dust sources. However, with
implementation of the dust abatement program described above in Mitigation Measure
AIR-1, impacts from construction-related PM-10 emissions would be less than significant.
The proposed project would locate additional students, considered a sensitive receptor, in
an area established with existing school land use and adjacent residential land uses. There
are no major freeways or land uses that would be considered major (i.e., permitted)
stationary sources of air pollution located within the project vicinity (1,000 feet). The only
BAAQMD-identified source facilities of toxic air contaminant emissions within one-half
mile of the project site is Alta Mesa Improvement Company at 695 Arastradero Road
which would not be expected to represent a threat to the existing scholastic land use, as
their only inventoried emissions are less than one gram of hexavalent chromium per year
(BAAQMD, 2007).
e) No Impact. As a general matter, the types of land use development that pose potential odor
problems include wastewater treatment plants, refineries, landfills, composting facilities
and transfer stations. No such uses would occupy the project site. Therefore, the project
would not create objectionable odors that would affect a substantial number of people. In
addition, there are no existing odor sources in the vicinity of the project site to which future
occupants of the project site would be subjected.
f) Less than Significant with Mitigation. Gases that trap heat in the atmosphere are called
greenhouse gases. The major concern is that increases in greenhouse gases are causing
global climate change. Global climate change is a change in the average weather on earth
that can be measured by wind patterns, storms, precipitation and temperature. Although
there is disagreement as to the speed of global warming and the extent of the impacts
attributable to human activities, most agree that there is a direct link between increased
emission of greenhouse gases and long-term global temperature. What greenhouse gases
have in common is that they allow sunlight to enter the atmosphere, but trap a portion of
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the outward-bound infrared radiation and warm up the air. The process is similar to the
effect greenhouses have in raising the internal temperature, hence the name greenhouse
gases. Both natural processes and human activities emit greenhouse gases. The
accumulation of greenhouse gases in the atmosphere regulates the earth’s temperature;
however, emissions from human activities such as electricity generation and motor vehicle
operations have elevated the concentration of greenhouse gases in the atmosphere. This
accumulation of greenhouse gases has contributed to an increase in the temperature of the
earth’s atmosphere and contributed to global climate change. The principal greenhouse
gases are carbon dioxide (CO2), methane (CH4), nitrous oxide (N2O), sulfur hexafluoride
(SF6), perfluorocarbons (PFCs), hydrofluorocarbons (HFCs), and water vapor (H2O).
Carbon dioxide is the reference gas for climate change because it is the predominant
greenhouse gas emitted. To account for the varying warming potential of different
greenhouse gases, greenhouse gas emissions are often quantified and reported as CO2
equivalents (CO2e).
Executive Order S-3-05
In 2005, Governor Schwarzenegger established Executive Order S-3-05, which sets forth a
series of target dates by which statewide emission of greenhouse gases (GHG) would be
progressively reduced, as follows:
• By 2010, reduce GHG emissions to 2000 levels;
• By 2020, reduce GHG emissions to 1990 levels; and
• By 2050, reduce GHG emissions to 80 percent below 1990 levels.
Assembly Bill 32 (California Global Warming Solutions Act of 2006)
In 2006, California passed the California Global Warming Solutions Act of (Assembly Bill
No. 32; California Health and Safety Code Division 25.5, Sections 38500, et seq., or
AB 32), which requires the California Air Resources Board (CARB) to design and
implement emission limits, regulations, and other measures, such that feasible and cost-
effective statewide GHG emissions are reduced to 1990 levels by 2020 (representing an
approximate 25 percent reduction in emissions). Under AB 32, the CARB must adopt
regulations by January 1, 2011 to achieve reductions in GHGs to meet the 1990 emission
cap by 2020.
CARB Climate Change Scoping Plan
In December 2008, CARB adopted the Climate Change Scoping Plan (AB 32 Scoping
Plan) outlining the State’s strategy to achieve the 2020 greenhouse gas emissions limit. The
AB 32 Scoping Plan, developed by CARB in coordination with the Climate Action Team
(CAT), proposes a comprehensive set of recommended actions designed to reduce overall
GHG emissions in California. The measures in the AB 32 Scoping Plan approved by the
Board will be developed over the next two years and be in place by 2012.
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OPR on CEQA and Climate Change
The Governor’s Office of Planning and Research (OPR) June 2008 Technical Advisory
(OPR, 2008) provides informal guidance for public agencies as they address the issue of
climate change in their CEQA documents. The June 2008 Technical Advisory offers
recommendations for identifying GHG emissions, determining significance under CEQA,
and mitigating impacts.
The June 2008 OPR Advisory states that lead agencies under CEQA should develop their
own approach to performing a climate change analysis for projects that generate GHG
emissions. The approach should be consistent for analyzing all such projects, and analyses
should be performed based on the best available information. If a lead agency determines
that GHGs may be generated by a proposed project, the agency is responsible for
quantifying estimated GHG emissions by type and source. The June 2008 OPR Advisory
also states that the lead agency must assess whether project emissions are individually or
cumulatively significant and implement strategies to avoid, reduce, or otherwise mitigate
the impacts of those emissions when impacts are potentially significant. Regional agencies
can attempt to reduce GHG emissions through their planning processes, according to the
June 2008 OPR Advisory. Regional transportation planning agencies can adopt plans and
programs that address congestion relief and reduce vehicle miles traveled (VMT), for
example.
Subsequent to the release of the 2008 Technical Advisory, OPR has developed proposed
guidelines for the mitigation of GHG emissions or the effects of GHG emissions under
CEQA, following Senate Bill 97. On April 13, 2009, OPR submitted additions and
amendments to the CEQA Guidelines to the Secretary for Natural Resources for
certification and adoption by January 1, 2010.
CARB Preliminary Draft Staff Proposal, October 2008
In its Staff Proposal, CARB is taking the first step toward developing recommended
statewide interim thresholds of significance for GHGs that may be adopted by local
agencies for their own use. The proposal does not attempt to address every type of project
that may be subject to CEQA, but instead focuses on common project types that,
collectively, are responsible for substantial GHG emissions – specifically, industrial,
residential, and commercial projects. CARB is developing these thresholds in these sectors
to advance climate objectives, streamline project review, and encourage consistency and
uniformity in the CEQA analysis of GHG emissions throughout the State.
CARB staff’s objective in this proposal is to develop a threshold of significance that will
result in the vast majority (approximately 90 percent statewide) of GHG emissions from
new industrial projects being subject to CEQA’s requirement to impose feasible mitigation.
CARB believes this can be accomplished with a threshold that allows small projects to be
considered insignificant. CARB staff used existing data for the industrial sector to derive a
proposed hybrid threshold. The threshold consists of a quantitative threshold of 7,000
metric tons of CO2 equivalent per year (MT CO2e/year) for operational emissions
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(excluding transportation), and performance standards for construction and transportation
emissions. These performance standards have not yet been developed.
To date, CARB has only developed preliminary interim threshold concepts for industrial
projects. No proposed thresholds for non-industrial project have been developed.
As with other individual and relatively small projects (i.e., projects that are not cement
plants, oil refineries, electric generating facilities/providers, co-generation facilities, or
hydrogen plants or other stationary combustion sources that emit more than 25,000 metric
tons (MMT) CO2e/yr), the project specific emissions from the proposed project would not
be expected to individually have an impact on global climate change (AEP, 2007) and the
primary concern would be whether the project would be in conflict with the state goals for
reducing greenhouse gas emissions.
Three types of analyses are used to determine whether the project could be in conflict with
the state goals for reducing greenhouse gas emissions. The analyses are reviews of:
• Assessment A: The potential conflicts with the CARB 39 recommended actions of the
Climate Change Scoping Plan;
• Assessment B: The relative size of the project in comparison to the estimated
greenhouse reduction goal of 174 MMTCO2E by 2020 and in comparison to the size
of major facilities that are required to report greenhouse gas emissions (25,000 metric
tons of CO2E/yr)4 and proposed thresholds of CARB; and
• Assessment C: The basic parameters of a project to determine whether its design is
inherently energy efficient, will lead to wasteful energy use, or is neutral with regard
to future energy use.
With regard to Assessment A, the project does not pose any apparent conflict with the most
recent list of the CARB early action strategies as these are aimed at industry, water use and
new land use development.
With regard to Assessment B, project construction GHG emissions were estimated with the
URBEMIS2007 computer model. CO2 emissions from construction assumed peak annual
GHG emissions would most likely occur during Group 1 and 2 classroom improvements.
An overall project construction area of 2.5 acres was assumed based on 110,000 square feet
of improvements. Per the Project Description this work would occur over a nine moth
period in 2011 and 2012. GHG emissions from this activity were calculated using the
URBEMIS2007 model of the CARB. Equipment exhaust also contains small amounts of
methane and nitric oxides which are also GHGs. Non-CO2 GHG emissions represent
approximately a three percent increase in CO2-equivalent emissions from diesel equipment
exhaust. For purposes of analysis, it was assumed that non-CO2 GHG emissions from
4 The State of California has not adopted guidance as to quantitative significance thresholds for assessing the impact
of greenhouse gas emissions on climate change and global warming concerns.
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construction equipment would be negligible. The peak annual activity would generate 245
“short” or 222 metric tons (MT) per year of CO2.
The proposed improvements to Gunn High school under the Master Plan would result in an
increase in daily operational CO2 emissions from project-related traffic and area source
emissions for space and water heating as well as electricity demand. Operational emissions
of CO2 from vehicle traffic as calculated by URBEMIS2007 would be 665 “short” tons per
year or 603 MT per year. URBEMIS also calculates natural gas combustion emissions
based on square footage of improvements. CO2 emissions from natural gas emissions are
calculated to be 233 “short” tons per year or 211 MT per year. Electricity demand based on
square footage of improvements and California specific emission factors of the California
Climate Action Registry and high school-specific electrical demand estimates would result
in an additional 430 MT per year of GHGs emitted indirectly as a result of the project.
Consequently the total operational CO2 emission rate resulting from implementation of the
proposed Master Plan is estimated to be 1,244 MT per year.
When compared to the state facility reporting requirement for GHG emissions of 25,000
MT per year CO2e, the maximum GHG emissions for the project (222 MT per year CO2e
during construction; and 1,244 MT per year during operations are not significant enough to
require reporting to the CARB relative to the requirements of AB32. Additionally, although
not yet adopted nor applicable to the proposed Master Plan, project GHG emissions would
be less than the proposed 7,000 MT per year Preliminary Staff Proposal threshold for
industrial projects under consideration by CARB.
With regard to Assessment C, in the absence of any definitive thresholds of significance,
the GHG emphasis on a project-specific level is to incorporate project design features that
reduce energy consumption and reduce vehicular travel as much as is feasible once such
measures are adopted in the Climate Change Scoping Plan of CARB. Unless there is a
greater shift to clean energy such as solar, hydroelectric, wind, nuclear, etc., no substantial
reduction in GHG is likely attainable by conventional methods except through energy
conservation.
GHG reduction options on a project-level basis are similar to those measures designed to
reduce criteria air pollutants (those with ambient air quality standards). Mitigation
Measure TRAN-2 (See Checklist Item 15, Transportation) would reduce trip generation
thus optimize the transportation efficiency of the land use and measures that promote
energy conservation within a development would reduce GHG emissions.
Because the proposed project consists of improvements under a Master Plan, there are no
specific building details at this level of project development. Consequently, mitigation
measures are recommended to ensure that development under the proposed Master Plan
would be inherently energy efficient and commensurate with achieving the goals of GHG
reductions under AB32.
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Mitigation Measure AIR-2: Building development plans resulting from the Master
Plan shall include “green building” features to reduce energy consumption to the
extent practicable. These measures may include:
• Building design consistent with the Collaborative for High Performance
Schools (CHPS). CHPS is a third party program that oversees the nation’s first
green building rating program especially designed for K-12 schools. CHPS has
published design guidelines and performance criteria specific to California
schools.
• Install efficient lighting and lighting control systems. Site and design buildings
to take advantage of daylight.
• Plant trees and vegetation near structures to shade buildings and reduce energy
requirements for heating/cooling.
• Preserve or replace onsite trees consistent with Mitigation Measure BIO-4 (that
are removed due to development) as a means of providing carbon storage.
• Install light-colored “cool” roofs and cool pavements.
• Install energy efficient heating and cooling systems, appliances and equipment
and control systems.
• Install light emitting diodes (LEDs) for traffic, street and other outdoor
lighting.
• Install water efficient fixtures and appliances.
Implementation of the above mitigation measures would reduce the impact to less
than significant levels.
Sources
Bay Area Air Quality Management District (BAAQMD), BAAQMD CEQA Guidelines: Assessing
the Air Quality Impacts of Projects and Plans, December 1999.
BAAQMD, Toxic Air Contaminant 2003 Annual Report, published 2007.
BAAQMD, Rules & Regulations, www.baaqmd.gov/dst/regulations/index.htm, accessed May 10,
2007.
California Air Resources Board, Air Quality and Land Use Handbook: A Community Health
Perspective, April 2005.
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Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
4. Biological Resources
Would the project:
a) Have a substantial adverse effect, either directly or
through habitat modifications, on any species
identified as a candidate, sensitive, or special-status
species in local or regional plans, policies, or
regulations, or by the California Department of Fish
and Game or U.S. Fish and Wildlife Service?
b) Have a substantial adverse effect on any riparian
habitat or other sensitive natural community
identified in local or regional plans, policies,
regulations or by the California Department of Fish
and Game or U.S. Fish and Wildlife Service?
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.) or state-protected
wetlands, through direct removal, filling, hydrological
interruption, or other means?
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?
e) Conflict with any local policies or ordinances
protecting biological resources, such as a tree
preservation policy or ordinance?
f) Fundamentally conflict with the provisions of an
adopted Habitat Conservation Plan, Natural
Community Conservation Plan, or other approved
local, regional, or state habitat conservation plan?
Discussion
a) Less than Significant with Mitigation. ESA conducted a reconnaissance-level field
survey of the project area on July 9, 2009 to verify existing biological conditions, assess
vegetation and wildlife habitats, and identify potential for special-status wildlife species to
occur onsite (ESA, 2009).5 Palo Alto and surrounding cities on the San Francisco peninsula
have been extensively developed in the last century, and areas directly surrounding Gunn
High School are primarily single-family homes and commercial business parks. Most of the
Gunn campus is landscaped, and common trees on campus include coast live oak (Quercus
agrifolia), valley oak (Quercus lobata), and elm (Elmus spp.). Several small, less
landscaped areas contain coyote brush (Baccharis pilularis) growing underneath oak trees.
5 The term “special-status” species includes those species that are listed and receive specific protection defined in
federal or state endangered species legislation, as well as species not formally listed as Threatened or Endangered,
but designated as “Rare” or “Sensitive” on the basis of adopted policies and expertise of state resource agencies or
organizations, or local agencies such as counties, cities, and special districts. A principle source for this designation
is the California “Special Animals List” (CDFG, 2009B).
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Birds identified on campus were species typically accustomed to disturbance, including
scrub jay (Aphelocoma californica), common raven (Corvus corax), black phoebe
(Sayornis nigricans), and American robin (Turdus migratorius).
Most open areas on campus are either paved parking lots, walkways, or grass playing
fields. In the northernmost corner of the campus, there is an approximately four-acre annual
grassland habitat. The area is gently sloped and had been recently mowed prior to a site
visit (ESA, 2009). Several California ground squirrel (Spermophilus beecheyi) burrows
were observed. Typical vegetation in this area includes wild oats (Avena barbata), ripgut
brome (Bromus hordaceous), and several oaks along the perimeter of the area. This habitat
could potentially support burrowing owl (Athene cunicularia), but construction would not
occur close enough to impact owls and any pairs present would be accustomed to
residential noise and disturbance.
The Barron Creek Debris Basin and an upstream wetland area are located directly west of
the Gunn campus. When ESA conducted a site visit, the basin was holding water but the
wetland area was dry (ESA, 2009). The basin likely holds water year-round and effectively
functions as a pond, and the wetland area becomes seasonally ponded but dries out in arid
months of the year. This habitat is described in more detail in c) below.
The California Natural Diversity Database (CNDDB) documents 43 special-status species
within the Palo Alto and Mountain View U.S. Geological Survey (USGS) quadrangles that
include the project area (CDFG, 2009). Potential for the project area to support special-
status species was assessed using the CNDDB (CDFG, 2009). No suitable habitat for
special-status plant species was found on or directly adjacent to the project area. Special-
status wildlife species that could potentially be impacted by the project include California
red-legged frog (Rana dratonyii), western pond turtle (Actinemys marmorata), pallid bat
(Antrozous pallidus) and hoary bat (Lasiurus cinereus). Construction activities and tree
removal may adversely impact nesting birds as well. These impacts are discussed below.
California red-legged frog
The California red-legged frog (CRLF) is a federally-threatened and California species of
special concern that can be found in man-made or natural ponds with little shade and some
aquatic vegetation, streams, and in moist upland areas near water bodies. Aquatic habitats
that seasonally dry up are preferred because they are less likely to contain predators like
bullfrogs (Lithobates catesbeianus) and non-native fish. CRLF, especially juveniles, can
disperse into poor quality habitats more than one mile from breeding ponds (Rathbun, pers.
comm.). The nearest CRLF occurrences are in Matadero and Deer Creeks, less than
0.75 miles away (CDFG, 2009), and potential dispersal and breeding habitat does exist in
the basin and upstream wetlands. Construction of a two-story classroom building within
100 feet of the debris basin is scheduled in Phase 1 of the Master Plan, which could result
in impacts on CRLF. Although unlikely, transient frogs could move from nearby wetland
areas to the Gunn campus and be impacted by project construction activities. Additionally,
sediment or hazardous materials from project activities could be carried into wetlands,
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especially during rain events. Both these potential impacts will be mitigated to less-than-
significant levels through Mitigation Measure BIO-1.
Mitigation Measure BIO-1: PAUSD shall require its contractor(s) to install silt
fence along the chain-link fence bordering the debris basin and wetland area on the
west side of the campus. This would prevent any sensitive wildlife from entering
active construction zones on the project site and will keep disturbed material,
sediment, or hazardous materials from travelling into these waters. The fence shall be
constructed of geotextile fabric with a minimum 3.5-inch overlap between panels.
Fence panels shall be attached to the chain-link fence or to wooden fence posts, and
sunken to a minimum of 6 inches below grade.
Western Pond Turtle
Western pond turtle is a California species of special concern that occupies permanent
bodies of water including ponds, streams and wetlands. They are found basking on logs,
rocks, or floating vegetation and submerge quickly when disturbed. Females need sandy
beaches or dry upland habitats to lay eggs, and have been recorded moving as far as 100
feet from aquatic habitats to lay eggs (Zeiner, 1990). The debris basin is potential habitat
for the western pond turtle year-round, and the wetlands upstream contain pond turtle
habitat when seasonally inundated. The nearest CNDDB occurrences for the western pond
turtle are along San Francisquito Creek and Lake Lagunita, both of which are on Stanford
University land approximately 2.5 miles away from the project area. While no occurrences
of western pond turtle have been documented at the debris basin, it does contain suitable
western pond turtle habitat. Discharge of sediment or hazardous materials during
construction would be a significant impact to western pond turtles. This potential impact
would be reduced to less-than-significant levels by Mitigation Measure BIO-1.
Special-Status Bats
The pallid bat, hoary bat, and Townsend’s big-eared bat could be present in trees or
buildings at Gunn High School. The pallid bat is a California species of concern present in
most low elevations in California. Preferred habitats for the pallid bat include rocky
outcrops with crevices and access to open areas, but they can be found in a variety of other
habitats as well. Day roosts can be found in crevices, caves, mines, and occasionally
buildings and hollow trees, while night roosts can be in more open areas such as open
buildings or porches (Zeiner et al, 1990). Pallid bats are nocturnal and present year-round
in most areas of California. Local CNDDB occurrences include Stanford University, and
within the cities of Menlo Park, Woodside, and Los Altos (CNDDB, 2009). The hoary bat
is a California species of concern and can be found at nearly any location in California.
Maternity roosts of this species are typically found in woodlands with medium to large
trees and dense foliage cover (Zeiner et al, 1990). Hoary bats migrate between summer and
winter ranges but can be found year-round in the San Francisco Bay Area. While not
common behavior, hoary bats may roost or be present on buildings or in building attics.
Several historical CNDDB occurrences from nearby Stanford University and the Los Altos
area exist for this species (CNDDB, 2009). Townsend’s big-eared bat is a California
species of special concern also found in most of California. Roosting habitat includes
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Initial Study September 2009
caves, mines, tunnels, buildings, or other human-made structures (Zeiner, 1990), and
maternity roosts for the Townsend’s big-eared bat are warm, while hibernation roosts can
be cold. This species is especially sensitive to disturbance, and a single visit by humans
may result in roost abandonment.
Removal of any trees or demolition of buildings containing special-status bat species in the
project area would be a significant impact. This impact can be reduced to less-than-
significant levels through implementation of Mitigation Measure BIO-2:
Mitigation Measure BIO-2: PAUSD shall require its contractor(s) to implement the
following measures:
• Prior to construction or demolition activities within 250 feet of trees/structures
with at least a moderate potential to support special-status bats, a qualified
biologist (i.e., a biologist holding a CDFG collection permit and a
Memorandum of Understanding with the CDFG allowing the biologist to
handle and collect bats) shall survey for bats. If no evidence of bats (i.e., visual
or acoustic detection, guano, staining, strong odors) is present, no further
mitigation is required.
• If bats raising pups (also called a maternity colony) are identified within 250 feet
of the project area during preconstruction surveys or project construction
(typically April 15 through August 15), the PAUSD will create a no-disturbance
buffer acceptable in size to the CDFG around the bat roosts. Bat roosts initiated
within 250 feet of the project area after construction has already begun are
presumed to be unaffected by project-related disturbance, and no buffer would be
necessary. However, the “take” of individuals (e.g., direct mortality of
individuals, or destruction of roosts while bats are present) is prohibited.
• Trees or buildings with evidence of bat activity shall be removed during the
time that is least likely to affect bats as determined by a qualified bat biologist
(in general, roosts should not be removed if maternity bat roosts are present,
typically April 15 – August 15, and roosts should not be removed if present
bats are in torpor, typically when temperatures are less than 40 degrees
Fahrenheit). Non-maternity bat roosts shall be removed by a qualified
biologist, by either making the roost unsuitable for bats by opening the roost
area to allow airflow through the cavity, or excluding the bats using one-way
doors, funnels, or flaps.
• All special-status bat roosts that are destroyed shall be replaced at a 1:1 ratio
with a roost suitable for the displaced species. The roost shall be modified as
necessary to provide a suitable roosting environment for the target bat species.
Nesting Birds
Trees and buildings in and around the project area provide suitable habitats for breeding
birds. Most native, breeding birds are protected under Section 3503 of the CDFG Code
(Code), and raptors are protected under Section 3503.5 of the Code. In addition, both
Section 3513 of the Code and the Federal Migratory Bird Treaty Act (16 U.S. Code,
Sec. 703 Supp. I, 1989) prohibit the killing, possession, or trading of migratory birds.
Finally, Section 3800 of the Code prohibits the taking of non-game birds, which are defined
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Initial Study September 2009
as birds occurring naturally in California that are neither game birds nor fully protected
species. To the degree feasible, construction activities would be scheduled to avoid the
nesting season between February 1 and August 31. In the event construction or vegetation
removal must be performed during the nesting season, potential impacts to breeding or
nesting birds could be significant and would be minimized to less-than-significant levels
with the implementation of Mitigation Measure BIO-3.
Mitigation Measure BIO-3: If construction or vegetation removal must be
performed in the bird nesting season (February 1 through August 31), a qualified
biologist shall be retained to survey the project area for nesting raptors and other
birds and verify the presence or absence of nesting birds or raptors no more than
14 days prior to construction activities. If active nests are observed, buffer zones shall
be established around trees/shrubs with nests, with a buffer size established by the
qualified biologist through consultation with the appropriate regulatory agency (e.g.,
CDFG). Buffered zones shall be avoided during construction activities until young
have fledged or the nest is otherwise abandoned.
b) Less than Significant with Mitigation. Riparian habitat exists less than 150 feet from
construction areas on the western side of the Gunn campus. This habitat consists of large
California buckeye (Aesculus californica), coast live oak, and willow (Salix spp.) trees
lining the western side of a wetland area within the Barron Creek channel, with coyote
brush and blackberry (Rubus spp.) growing inside the channel as well. The riparian area is
fairly narrow and limited by a paved bike path to the east of Barron Creek and a
commercial business park to the west of Barron Creek. This habitat would not be directly
impacted by construction activities, and any water quality or nesting bird impacts would be
mitigated to less-than-significant levels by Mitigation Measures BIO-1 and BIO-3. Other
nearby riparian areas include San Francisquito Creek, Matadero Creek, and Lake Lagunita,
but these are all greater than 0.5 miles from the project site and would not be impacted by
project activities. Potential impacts to wetlands in the Barron Creek channel are addressed
in c) below.
c) Less than Significant with Mitigation. Wetlands are a subset of “waters of the United
States,” which are defined in the Code of Federal Regulations (CFR) (33 CFR 328.3[a];
40 CFR 230.3[s]) as rivers, streams, mud flats, sand flats, wetlands, sloughs, prairie
potholes, wet meadows, playa lakes, or natural ponds, the use, degradation, or destruction
of which could affect interstate or foreign commerce including any such waters. These
waters and their associated riparian corridors (discussed under b) above) fall under the
jurisdiction of the U.S. Army Corps of Engineers (Corps), San Francisco Bay Regional
Water Quality Control Board, and the California Department of Fish and Game.
The Barron Creek Debris Basin is less than 100 feet away from existing portable buildings
on the west side of campus, and consists of a 250-foot wide pond lined with concrete. This
habitat is classified by the Corps as open water, under other waters of the U.S., another
subset of waters of the U.S. Ponded and open stream waters are still jurisdictional, much
like wetland areas discussed above. The basin was constructed directly in the channel of
Barron Creek to prevent seasonal flooding of the surrounding businesses and
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neighborhoods, and is designed to catch debris that previously hindered creek flow during
large storm events. No emergent vegetation is present in the pond, but dense aquatic
vegetation grows along its perimeter. The wetland area slightly upstream of the debris basin
contains dense areas of emergent wetland vegetation including cattails (Typha spp.), curly
dock (Rumex crispus), and sedges (Cyperace spp.), but was dry when ESA conducted a site
visit (ESA, 2009). Aerial photos show inundation of much of the wetland (NAIP, 2005),
and it is presumed that standing water seasonally ponds there. Barron Creek is culverted for
much of its extent downstream of the debris basin, but it does discharge into San Francisco
Bay at the Palo Alto Baylands Park. Discharge of sediment and hazardous materials from
construction work could enter these waters, and would result in significant impacts on
jurisdictional waters. These impacts would be mitigated to less than significant levels
through Mitigation Measure BIO-1.
d) No Impact. Areas around Gunn are heavily developed, and any historically present
terrestrial wildlife corridors have already been disrupted. Riparian corridors discussed in b)
and extensive areas of oak savanna west of Gunn provide connected habitats suitable for
migration of various wildlife species. Most developed areas of Palo Alto provide habitat for
urban wildlife in landscaped environments, but little native habitat exists to provide
significant wildlife movement corridors around the project area. Additionally, large roads
with moderate to high traffic volume restrict movement of many terrestrial wildlife species
through the project area. No impacts on wildlife corridors are anticipated by project
activities.
e) Less than Significant with Mitigation. Many large trees grow within the project area, and
proposed construction of new facilities may necessitate tree removal. Under the City of
Palo Alto Tree Preservation and Management Regulations (Municipal Code Section 8.10)
and the Tree Technical Memo (City of Palo Alto, 2001), trees designated as protected trees
or street trees are subject to several conditions before removal. A protected tree is:
• A coast live oak (Quercus agrifolia) or valley oak (Quercus lobata) tree greater
than 11.5 inches diameter at breast height (DBH)6;
• A redwood (Sequioa sempervirens) tree greater than 18 inches DBH; or
• Any tree designated a heritage tree by the Palo Alto city council.
• A street tree is any tree that grows within the publicly-owned street right-of-way.
Removal of any protected or street trees in the project area would be considered a
significant impact. These impacts can be mitigated to less-than-significant levels through
Mitigation Measure BIO-4.
Mitigation Measure BIO-4: PAUSD shall require its contractor(s) to implement the
following measures:
6 Diameter at breast height (DBH) is the diameter of the trunk of a tree 4.5 feet above natural grade.
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• Fulfill pre-construction requirements consistent with Section 2.15 of the City
of Palo Alto Tree Technical Memo, including establishment of a tree
protection and preservation plan; verification of tree protection; a pre-
construction meeting with the City Arborist, community representative, and
District Arborist to coordinate a tree replacement plan and protective fencing
for retained protected or street trees; establishment of tree protection zones for
retained trees; and trimming of any retained trees.
• Obtain a tree removal permit for removal of any street trees in the project area
by submitting the following to the City of Palo Alto:
1) Protected Tree Removal Application;
2) Application fees; and
3) Letter report from a certified arborist including tree species, location,
size (DBH, height and crown spread), condition, and life expectancy and
prognosis.
• Obtain a permit from the City of Palo Alto Department of Public works for any
construction activities occurring within the dripline7 of a street tree.
• Remove no more than 25 percent of a protected tree’s canopy during pruning
activities of retained trees, and remove no more than 25 percent of a protected
tree’s root mass during construction activities.
• Replace all removed street trees as specified by the City of Palo Alto’s Director
of Planning and Community Environment and in conjunction with standards
described in section 3.15-C in the City of Palo Alto Tree Technical Manual.
f) No Impact. The proposed project would not conflict with the provisions of an adopted
Habitat Conservation Plan, Natural Community Conservation Plan, or other approved local,
regional, or state habitat conservation plan. Mitigation Measures BIO-1, BIO-2, BIO-3, and
BIO-4 are designed to reduce cumulative impacts to special-status species and wetlands,
and avoid conflicts with any other local plans or ordinances.
Sources
California Department of Fish and Game (CDFG), California Natural Diversity Database for 7.5
minute topographic quadrangles of Mountain View, Palo Alto, Commercial Version,
accessed July, 2009.
CDFG, California Natural Diversity Database. Special Animals (901 Taxa),
www.dfg.ca.gov/biogeodata/cnddb/pdfs/SPAnimals.pdf, accessed May 18, 2009.
City of Palo Alto, Department of Planning and Community Environment, Tree Technical
Manual, 2001.
City of Palo Alto Municipal Code, Section 8.10,
www.cityofpaloalto.org/depts/clk/municipal_code.asp, accessed July 15, 2009.
ESA. 2009. Site reconnaissance, July 9, 2009.
7 Dripline area, as defined in the Tree Technical Manual, is the circular area underneath a tree with a radius equal to
ten times the tree’s trunk diameter.
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Initial Study September 2009
NAIP (National Agriculture Imagery Program), U.S. Department of Agriculture Farm Service
Agency, 2005.
Rathbun, G., and Scott, N., Personal communication: biology and management of the California
red-legged frog (Rana draytonii). Workshop sponsored by Alameda County Conservation
Partnership, 2009.
Zeiner, D.C., Laudenslayer, W.F., Mayer, W.E., and White, M., ed., California’s Wildlife,
Volume III, Mammals, California Department of Fish and Game, Sacramento, CA, 1990.
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Initial Study September 2009
Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
5. Cultural Resources
Would the project:
a) Cause a substantial adverse change in the
significance of a historical resource as defined in
§15064.5?
b) Cause a substantial adverse change in the
significance of a unique archaeological resource
pursuant to §15064.5?
c) Directly or indirectly destroy a unique paleontological
resource or site or unique geologic feature?
d) Disturb any human remains, including those interred
outside of formal cemeteries?
Discussion
a) No Impact. CEQA Guidelines Section 15064.5 requires the lead agency to consider the
effects of a project on historical resources. A historical resource is defined as any building,
structure, site, or object listed in or determined to be eligible for listing in the California
Register of Historical Resources (CRHR), or determined by a lead agency to be significant
in the architectural, engineering, scientific, economic, agricultural, educational, social,
political, or cultural annals of California. The following discussion will focus on
architectural/structural resources. Archaeological resources, including archaeological
resources that are potentially historical resources according to Section 15064.5, are
addressed in b), below.
The Palo Alto Unified School District (PAUSD or District) was founded in 1893. The
District includes the City of Palo Alto, Stanford University, and areas of Los Altos Hills,
Palo Alto Hills, and Portola Valley within its attendance area. Gunn High School was
constructed in 1964 on an approximately 48-acre site northeast of the intersection of
Arastradero Road and Foothill Expressway. The school is comprised of 17 permanent
buildings clustered on the southern portion of the campus. These include the following:
Administrative Building, Student Activities Building, cluster of four buildings for language
and social studies instruction, cluster of four buildings for math and science instruction,
Resource Materials Building, Music Building, Art Building, Spangenberg Auditorium,
Business Education and Home Economics Building, Industrial Arts Building, and
Gymnasium. The original buildings were constructed in 1964, as described above, with a
new Library Building and Science facility added in 2003. The modern architectural style of
the campus buildings features single-story structures (with the exception of the Gym and
Spangenberg Auditorium) with exterior wood siding, small window openings, and attached
covered walkways supported by concrete columns and mansard roofs. Most of the southern
portion of the campus is paved with trees and other landscaping interspersed between the
buildings. All buildings with the exception of the interiors to the Gym, Spangenberg
Auditorium, Administration, and the old Library Building were fully renovated under the
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Building for Excellence Program. The campus also includes approximately 26 relocatable
classrooms.
Archival research revealed that none of the buildings on the Gunn campus are listed in the
federal, state, or local listings of historical resources. While the campus has not been
systematically surveyed or evaluated for any potential historical or architectural
significance, given the age of the campus, it would not meet the minimum threshold for
consideration for listing, which is generally 50 years of age or older. In addition, research
revealed no significant associations with important historical events, important persons, or
buildings with a high degree of architectural merit. Due to their relatively recent age and
general lack of historical and architectural merit, none of the buildings on the Gunn campus
appear eligible for listing in the federal, state, or local listings of historical resources. While
the proposed project would make a number of physical changes to the campus, no direct or
indirect impacts to historic architectural resources (either on or off-campus) as defined by
CEQA Section 15064.5 are anticipated. No mitigation measures would be necessary.
b) Less Than Significant with Mitigation. This section discusses archaeological resources,
both as historical resources according to Section 15064.5 as well as unique archaeological
resources as defined in Section 21083.2 (g).
A records search was conducted at the Northwest Information Center of the California
Historical Resources Information System (NWIC) at Sonoma State University on June 29,
2009 (File No. 08-1672) to: (1) determine whether known archaeological resources had
been recorded within a 0.5 mile radius of the project site; (2) assess the likelihood for
unrecorded archaeological resources to be present based on historical references and the
distribution of nearby archaeological sites; and (3) develop a context for the identification
and preliminary evaluation of cultural resources. During the records search, the following
sources for information on historical resources were reviewed: the California Inventory of
Historical Resources (OHP, 1976), California Historical Landmarks (DPR, 1996),
California Points of Historical Interest (DPR, 1992), and Historic Properties Directory
Listing (OHP, 2009). The Historic Properties Directory includes listings of the National
Register of Historic Places and the California Register of Historical Resources, and the
most recent listings of California Historical Landmarks and California Points of Historical
Interest. Historic topographic maps were also reviewed.
The project site is situated within the territory of the Costanoan—also referred to as
Ohlone—language groups. Eight Costanoan languages were spoken in an area extending
from the southern edge of the Carquinez Strait to portions of the Sur and Salinas Rivers
south of Monterey Bay (Levy, 1978). At the time of Euro-American contact, Ramaytush
speakers occupied the San Francisco Peninsula. Levy’s 1978 summary of Costanoan
lifeways describes territories as comprised of one or more land-holding groups, which
anthropologists named tribelets. The tribelet, or village community, was a nearly universal
characteristic throughout Native California, consisting of a principal village that was
occupied year-round and a series of smaller hamlets occupied intermittently or seasonally
(Kroeber, 1925). Tribelet territories were generally defined on the basis of physiographic
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features (e.g., river drainage systems) and stretched between 8 and 12 miles across.
Population densities within tribelets ranged from 50 to 500 people and were largely
determined by the carrying capacity of a tribelet’s territory. San Francisquito Creek, located
approximately 3.5 miles northwest of the project site, was one of the most densely occupied
watersheds along the San Francisco Peninsula during the prehistoric period. At the time of
Euroamerican contact, two or more Ohlone tribelets may have occupied this watershed at
the villages of puyšon and Ssiputca.
No archaeological resources have been recorded in the immediate project site. Two
archaeological sites have been recorded north of the project site along the south bank of
Matadero Creek (Bocek and Rutherford, 1985; Bocek, 1987). Both archaeological sites are
extensive shell middens with artifacts and human remains, likely related to a major
prehistoric occupation area along Matadero Creek. An ESA Registered Professional
Archaeologist surveyed the project site on August 22, 2009. The project site was walked in
transects spaced 10–20-meters apart. Visibility was moderate in the undeveloped area
nearest to the recorded archaeological sites. Exposed ground surface and rodent holes were
inspected for cultural materials. No cultural materials were located. The project site is in an
area mapped as bedrock. This geologic landform does not have the potential to contain
deeply-buried soils or paleosols that would have once been available for human use and
occupation.
The project site does not appear to contain archaeological materials; however the
possibility cannot be entirely discounted. The following mitigation measure would reduce
potential impacts to the inadvertent discovery of archaeological resources to a less-than-
significant level.
Mitigation Measure CUL-1: If previously unidentified cultural materials are
unearthed during construction, work shall halt in that area until a qualified
archaeologist can assess the significance of the find. Additional archaeological
survey will be needed if project limits are extended beyond the present study limits.
Prehistoric materials might include obsidian and chert flaked-stone tools (e.g.,
projectile points, knives, scrapers) or toolmaking debris; culturally darkened soil
(“midden”) containing heat-affected rocks, artifacts, or shellfish remains; and stone
milling equipment (e.g., mortars, pestles, handstones, or milling slabs); and battered
stone tools, such as hammerstones and pitted stones. Historic-era materials might
include stone, concrete, or adobe footings and walls; filled wells or privies; and
deposits of metal, glass, and/or ceramic refuse. If any find is determined to be
significant, the project proponent and the archaeologist will meet to determine the
appropriate avoidance measures. If the resources cannot be avoided they must be
evaluated for their eligibility to the California Register of Historical Resources.
c) Less Than Significant with Mitigation. Paleontological resources are the fossilized
remains of plants and animals, including vertebrates (animals with backbones),
invertebrates (e.g., starfish, clams, ammonites, and marine coral), and fossils of
microscopic plants and animals (microfossils). The age and abundance of fossils depend on
the location, topographic setting, and particular geologic formation in which they are found.
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Subsurface excavations into undisturbed soils and rock beneath the high school could
potentially disturb or destroy paleontological resources. Gunn High School is underlain by
the Santa Clara Formation, which is a sedimentary rock unit that is approximately 3.5 to
11 million years old and has yielded fossilized plants and animals in other locations in the
Bay Area. The University California Museum of Paleontology contains five records of
vertebrate fossils that originated in the Santa Clara Formation, including teeth and bone
fragments from several extinct species of hoofed mammals (UCMP, 2009). The closest of
these finds is on the Stanford Campus, approximately 2.5 miles northwest of the site. Plant
fossils found within the unit include petrified wood fragments as large as 60 cm in diameter
at Coal Mine Ridge in the Santa Cruz Mountains and a suite of plant fossils along Scott
Creek, approximately 8.5 miles southwest of the site (UCMP, 2009; USGS, 2000). Fossil
discoveries of this kind provide scientific value because they help establish a historical
record of past plant and animal life and can assist geologists in dating rock formations.
Because the Santa Clara Formation beneath Gunn High School has yielded vertebrate
fossils, it qualifies under the Society of Vertebrate Paleontology guidelines as a unit of high
paleontological potential8 (SVP, 2006). While no information exists to refute or confirm the
presence of fossils beneath the high school, disturbance or destruction of a paleontological
resource is a potentially significant impact if excavations for the project disturb the Santa
Clara Formation. Mitigation Measure CUL-2 would reduce this impact to a less than
significant level by informing earth moving crews on the appearance of fossils, procedures
to follow if any are discovered, and ensuring that a paleontologist assess the significance of
any fossil find, and recovers it, if appropriate.
Mitigation Measure CUL-2: Prior to the start of any subsurface excavations, all
construction forepersons and field supervisors shall receive training by a qualified
professional paleontologist, as defined by the SVP (1995), who is experienced in
teaching non-specialists, to ensure they can recognize fossil materials and will follow
proper notification procedures in the event any are uncovered during construction.
Procedures to be conveyed to workers include halting construction within 50 feet of
any potential fossil find and notifying a qualified paleontologist, who will evaluate its
significance. Training on paleontological resources will also be provided to all other
construction workers, but may involve using a videotape of the initial training and/or
written materials rather than in-person training by a paleontologist. If a fossil is
determined to be significant and avoidance is not feasible, the paleontologist will
develop and implement an excavation and salvage plan in accordance with SVP
standards (SVP, 1995; SVP, 1996).
d) Less than Significant with Mitigation. Based upon the records search, no human remains
are known to exist within the project site. The proposed project would involve ground-
disturbing activities; therefore the possibility that such actions could unearth, expose, or
disturb buried human remains cannot be entirely discounted. The following mitigation
measure would reduce potential impacts attributable to the inadvertent discovery of human
remains to a less-than-significant level.
8 Paleontological potential refers to the probability that a rock unit will yield a unique or significant paleontological
resource.
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Mitigation Measure CUL-3: If human remains are encountered unexpectedly during
construction excavation and grading activities, State Health and Safety Code Section
7050.5 requires that no further disturbance shall occur until the County Coroner has
made the necessary findings as to origin and disposition pursuant to PRC Section
5097.98. If the remains are determined to be of Native American descent, the coroner
has 48 hours to notify the Native American Heritage Commission (NAHC). The
NAHC will then identify the person(s) thought to be the Most Likely Descendent of
the deceased Native American, who will then help determine what course of action
should be taken in dealing with the remains.
Sources
Bocek, Barbara, Archaeological Site Record for CA-SCL-616. On file, Northwest Information
Center of the California Historical Resources Information System, Sonoma State
University, Rohnert Park, California, 1987.
Bocek, Barbara, and James Rutherford, Archaeological Site Record for CA-SCL-585. On file,
Northwest Information Center of the California Historical Resources Information System,
Sonoma State University, Rohnert Park, California, 1985.
California Department of Parks and Recreation (DPR), California Points of Historical Interest,
Office of Historic Preservation, Sacramento, California, 1992.
California Department of Parks & Recreation (DPR), California Historical Landmarks,
Sacramento: State of California, Resources Agency, 1996.
Kroeber, Alfred L., Handbook of the Indians of California. Bureau of American Ethnology
Bulletin 78. Smithsonian Institution, Washington, D.C., Reprinted 1976 by Dover, New
York, 1925.
Levy, Richard, Costanoan In California. Handbook of North American Indians, vol. 8, William
C. Sturtevant, general editor. 1978.
Society of Vertebrate Paleontology (SVP), Assessment and mitigation of adverse impacts to
nonrenewable paleontologic resources: standard guidelines, Society of Vertebrate
Paleontology News Bulletin, Vol. 163, pp. 22–27, 1995.
Society of Vertebrate Paleontology (SVP), Conditions of Receivership for Paleontologic Salvage
Collections, Society of Vertebrate Paleontology News Bulletin, Vol. 166, pp. 31–323,
February 1996.
United States Geological Society (USGS), Geologic map and map database of the Palo Alto 30’
X 60’ quadrangle, California, Prepared by Brabb E.E., Graymer R.W., and Jones D.L.,
USGS Miscellaneous Field Studies, Map MF-2332, Version 1.0, 2000.
University of California Museum of Paleontology (UCMP), Collections Database. Accessed
Online August 20, 2009 at: http://www.ucmp.berkeley.edu/science/collections.php.
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Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
6. Geology and Soils
Would the project:
a) Expose people or structures to potential substantial
adverse effects, including the risk of loss, injury, or
death involving:
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.
ii) Strong seismic ground shaking?
iii) Seismic-related ground failure, including
liquefaction?
iv) Landslides?
b) Result in substantial soil erosion or the loss of topsoil?
c) Be located on 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?
d) Be located on expansive soil, as defined in
Table 18-1-B of the Uniform Building Code (1994, as it
may be revised), creating substantial risks to life or
property?
e) Have soils incapable of adequately supporting the use
of septic tanks or alternative wastewater disposal
systems where sewers are not available for the
disposal of wastewater?
Setting
The City of Palo Alto is located along the southern portion of the San Francisco Peninsula. The
landscape is typical of much of the California Coast Ranges, characterized mainly by northwest
trending ridges and valleys of moderate topographic relief. The area is also characterized by
numerous active and potentially active faults, and frequent earthquakes. The San Andreas fault, a
major tectonic and structural feature of the Coast Range, that bisects the City’s foothill area,
forms the boundary between the North American and Pacific plates.
The greatest hazards associated with earthquakes are fault rupture and groundshaking, although
liquefaction hazards are significant east of U.S. Highway 101 due to the porous nature and
relatively shallow groundwater table. Other geologic hazards in Palo Alto may or may not include
landslides, expansive soils, settlement, and erosion. Landsliding may result from heavy rain,
erosion, removal of vegetation, or human activities. Settlement and subsidence due to
groundwater withdrawal has historically been a problem in south and east Palo Alto but has been
largely halted by groundwater recharge efforts and reduced pumping from local groundwater
resources. Seismically-induced flooding is a hazard due to the possibility of dam failure at Felt
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Lake, Searsville Lake, and Lagunita Reservoir, as well as from the potential for levee failure near
the San Francisco Bay.
Discussion
a.i) Less than Significant with Mitigation. Surface fault rupture is most commonly seen along
traces of active faults during major earthquakes and results in observable offsets on the
ground surface. On faults that generate horizontal movement (referred to as strike-slip
faults) this displacement along a fault trace can cause considerable damage to a structure,
even collapse. Non-structural damage from fault rupture includes distorted asphalt, severe
utility damage, distressed foundations and extensive service disruption for transportation
facilities. Surface fault rupture presents a substantial potential risk to people and property,
especially in the San Francisco Bay Area where there are several active faults.
The State of California, through the Alquist-Priolo Earthquake Fault Zoning Act (Alquist-
Priolo Act), prohibits the development of structures for human occupancy across active
fault traces9. Under the Alquist-Priolo Act, the California Geological Survey (CGS) must
establish zones on either side of the active fault that delimit areas most susceptible to
surface fault rupture. These zones are referred to as fault rupture hazard zones and are
shown on official maps published by the CGS.
The project site is located approximately five miles from the San Andreas fault. The project
site is not located in an Alquist-Priolo Earthquake Fault Zone, as defined by the CGS.
However, the project site is located in the immediate vicinity of the Stanford fault zone,
which is part of the front-range fault system. The location and levels of risk associated with
individual faults of the front-range fault system are not well defined and there is no known
displacement within the last 10,000 years. The location of the probable rupture area within
the Stanford fault zone is poorly defined; therefore, the level of risk associated with rupture
of the Stanford fault zone is essentially undefined (City of Palo Alto DEIR, 1996). From a
planning standpoint, the Stanford fault zone should be considered as potentially active with
associated zones of possible surface rupture. The ability to produce an earthquake large
enough to rupture the earth’s surface is significantly less certain along the Stanford fault
zone than that of the San Andreas fault because there is no documented historic record of
ground rupture.
The project site is located between two concealed fault traces of the Pulgas fault within the
frontal Stanford fault zone, a series of high angle thrust faults generally located along the
base of the low hills lying immediately west of the campus. The nearest mapped traces of
9 An active fault is defined by the State of California as a fault that has had surface displacement within Holocene
time (approximately the last 10,000 years). A potentially active fault is defined as a fault that has shown evidence
of surface displacement during the Quaternary (last 1.6 million years), unless direct geologic evidence demonstrates
inactivity for all of the Holocene or longer. This definition does not, of course, mean that faults lacking evidence of
surface displacement are necessarily inactive. Sufficiently active is also used to describe a fault if there is some
evidence that Holocene displacement occurred on one or more of its segments or branches (Hart, 1997).
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the Pulgas fault are located approximately 200 feet to the southwest and 400 feet to the
northwest of the site.
According to the geotechnical report prepared for Gunn (Cleary, 2009), the evidence for
Holocene activity on the Stanford fault zone, and specifically the Pulgas fault, is
inconclusive and thus a “very low likelihood” that proposed improvements would be
affected due to surface displacement on the fault.
Implementation of Mitigation Measure GEO-1 would ensure that impacts related to
surface rupture would be less than significant.
Mitigation Measure GEO-1: The proposed construction shall comply with site
specific recommendations made in design level geotechnical investigations by the
District’s geotechnical engineers. These recommendations shall be designed to
mitigate geologic hazards and shall become part of the project. The final seismic
considerations shall be submitted to and approved of by the Division of the State
Architect (DSA), prior to project commencement, to ensure compliance with the
most current California seismic building codes.
a.ii) Less than Significant with Mitigation. Seismic ground shaking is a significant hazard
within Palo Alto because of its close proximity to the San Andreas fault, the Hayward fault,
the front-range fault system, and several other faults within the Bay Area that have the
capability of producing a large magnitude earthquake. The level of shaking is influenced by
various factors including distance to the epicenter, underlying soil or bedrock conditions,
and the magnitude of the event.
In April 2008, a new earthquake forecast called the Uniform California Earthquake Rupture
Forecast (UCERF) was released that updated the earthquake forecast for the Bay Area.
Produced by the U.S. Geological Survey 2007 Working Group on California Earthquake
Probabilities (WG07), the UCERF evaluated the likelihood of one or more earthquakes of
moment magnitude 6.7 or higher occurring in the San Francisco Bay Area.10 The result of
the evaluation indicated a 63 percent likelihood that such an earthquake event will occur in
the Bay Area before 2037.
Within this 63 percent probability, the Hayward-Rodgers Creek and San Andreas Fault
systems are the two most likely fault systems to cause the event (UCERF, 2008).
Therefore, the proposed project would likely experience at least one major earthquake
(greater than moment magnitude 6.7) before 2037.
10 Moment magnitude is related to the physical size of a fault rupture and movement across a fault. The Richter
magnitude scale reflects the maximum amplitude of a particular type of seismic wave. Moment magnitude provides
a physically meaningful measure of the size of a faulting event (CGS, 1997).
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According to the CGS Probabilistic Seismic Hazard Assessment (PSHA), peak ground
acceleration at the project site could reach or exceed 0.6 g (CGS, 2009).11 The PSHA
identifies the hazard from earthquakes that geologists and seismologists agree could occur.
It is “probabilistic” in the sense that the analysis takes into consideration the uncertainties
in the size and location of earthquakes and the resulting ground motions that can affect a
particular site.
In addition, the Association of Bay Area Governments (ABAG) determined that ground
shaking at the project site would most likely be felt as very strong if a moment magnitude
7.2 earthquake were to occur on the San Andreas Fault Zone (ABAG, 2009).
Ground shaking from a moderate to strong earthquake could generate ground accelerations
at the proposed project site that could cause damage to structures, utilities, and/or
unsecured equipment and objects. Specifically, the proposed school buildings and
underground utilities could sustain structural damage, potentially causing injury to anyone
present during an earthquake event. Damage from ground shaking could include cracking
in walls and pavement and damage to exterior building elements.
Although some structural damage is typically not avoidable during an earthquake, current
building codes and construction ordinances have been established to protect against
building collapse and major injury during a seismic event. Implementation of Mitigation
Measure GEO-1 would ensure that the level of risk from ground shaking would be less
than significant.
a.iii) Less than Significant. Liquefaction is the sudden temporary loss of shear strength in
saturated, loose to medium dense, granular sediments subjected to ground shaking. It
generally occurs when seismically induced ground shaking causes pore water pressure to
increase to a point equal to the overburden pressure. Liquefaction can cause foundation
failure of buildings and other facilities due to the reduction of foundation bearing strength.
The State of California, through the Seismic Hazard Zonation Program, produces Seismic
Hazard Zone maps that identify areas of liquefaction and landsliding, as required by the
Seismic Hazards Mapping Act. These maps depict “areas where historical occurrence of
liquefaction, or local geological, geotechnical and ground water conditions indicate a
potential for permanent ground displacement such that mitigation as defined in Public
Resources Code Section 2693(c) would be required.” Mitigation is defined as “those
measures that are consistent with established practice and that will reduce seismic risk to
acceptable levels.”[PRC 2693(c)]
The CGS Seismic Hazard Zone map for the Palo Alto Quadrangle (CGS, 2006) shows a
narrow band of liquefaction running across the campus along the undergrounded Barron
Creek. This area begins at the Santa Clara Valley Water District detention basin on the
11 g is equivalent to the acceleration due to gravity, or 980 centimeters per second squared. Acceleration is scaled
against acceleration due to gravity or the acceleration with which a ball falls if released at rest in a vacuum (1.0 g).
Acceleration of 1.0 g is equivalent to a car traveling 100 meters (328 feet) from rest in 4.5 seconds.
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western boundary of the campus, runs between the existing gymnasium and football field,
and exits the campus near Los Robles Avenue.
The geotechnical investigation (Cleary, 2009) determined that proposed new building sites
are generally underlain by firm to very stiff sandy clay and medium dense to very dense
clayey sand, silty gravelly clayey sand and sandy clay gravel from the surface to the
maximum depth explored of 45 feet. Based on these conditions, the likelihood of soil
liquefaction during strong ground shaking is very low; however, the sand and clay layers
encountered in borings below the assumed high groundwater table (estimated to be at
25 feet) were conservatively analyzed for liquefaction-induced settlement.
The analysis calculated the theoretical liquefaction-induced settlements as less than an inch
a proposed building sites. Because the computed settlements would occur below a depth of
25 feet, the likelihood of significant surface manifestation from settlement at such depth is
low.
The proposed second gymnasium, as well as the relocated tennis and basketball courts, are
located in proximity to this liquefaction zone. Construction of these proposed facilities in
this area may lead to foundation failure during a seismic event. With implementation of
Mitigation Measure GEO-1, the potential impact associated with liquefaction would be
reduced to a less than significant level.
a.iv) Less than Significant. Slope failures, including landslides, include many phenomena that
involve the down-slope displacement and movement of material, either triggered by static
(i.e. gravity) or dynamic (i.e. earthquake) forces. Slope failure is dependent on degree of
incline, subsurface materials, precipitation, excavation, and seismicity. The type of failure
can include deep-seated massive slope movements or shallow slump type movements.
The project site is generally level and it is not located within an “earthquake-induced
landslide” zone according to the Seismic Hazard Zone map for the Palo Alto Quadrangle
(CGS, 2006). Therefore, the potential impact of slope failure would be considered less than
significant.
b) Less than Significant with Mitigation. Construction activities associated with the
proposed project would require earthmoving, grading, and compaction. These activities
may expose areas of soil that have previously been covered with asphalt, concrete, or
landscaping. This temporary loss of erosion control would expose bare soil, which would
be subjected to erosion by wind and storm water runoff. Concentrated water erosion, if not
managed or controlled, can eventually result in substantial soil loss and/or discharging of
sediment into utilities, adjacent lots, or nearby creeks and drainages. Excessive soil loss can
cause a potential threat to the structural integrity of structural foundations, earthen berms,
or engineered fills.
Stormwater discharges from construction activities that disturb one acre or more are
regulated by the local Regional Water Quality Control Board (RWQCB) and are subject to
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the permitting requirements of the National Pollutant Discharge Elimination System
(NPDES) General Permit for Discharges of Stormwater Runoff Associated with
Construction Activity (General Construction Permit). The General Construction Permit
requires the preparation and implementation of a Storm Water Pollution Prevention Plan
(SWPPP) for construction activities.
As fully described in Checklist Item 8, Hydrology and Water Quality, Mitigation
Measure HYD-1, the PAUSD would be required to develop and implement a SWPPP in
order to minimize potential erosion and subsequent sedimentation of storm water runoff.
This SWPPP would include Best Management Practices (BMPs) to control erosion
associated with grading, trenching, and other ground surface-disturbing activities.
Since BMPs have been recognized as methods to effectively prevent or minimize the
erosion, and the PAUSD will adhere to erosion control measures outlined in the SWPPP,
the potential for erosion impacts during the various projects would be less than significant.
c) Less than Significant with Mitigation. The upper soils at the project site were found to be
of variable density and strength, and are considered unsuitable for support of proposed
building foundations and slabs if left in place (Cleary, 2009). However, over-excavation
and replacement with engineered fill in compliance with the standards described in the
preliminary foundation recommendations would mitigate the potential for unstable soils to
affect the building foundations (Cleary, 2009). The potential landslide hazard for the
proposed project is discussed above in Section 6.a.iv. With implementation of preliminary
foundation recommendations and Mitigation Measure GEO-1, above, the potential hazard
from unstable soils would be considered less than significant.
Due to the generally high relative densities associated with the subsurface soils, soil
lurching and lateral spreadings are considered unlikely (Cleary, 2009)
d) Less than Significant with Mitigation. Preliminary foundation recommendations
indicated that upper sandy clay at the project site is considered to be moderately to highly
expansive based on its plasticity characteristics and laboratory test results (Cleary, 2009).
The effects of expansive soils could damage foundations and aboveground structures,
paved parking areas, and concrete slabs. Surface structures with foundations constructed in
expansive soils could experience expansion and contraction depending on the season and
the amount of surface water infiltration. The expansion and contraction due to the behavior
of expansive soils could exert enough pressure on the structures to result in cracking,
settlement, and uplift. Cleary indicates that the potential detrimental effects of expansive
soils may be largely eliminated through the proposed grading plan and replacement of well-
compacted engineered fill. Interior and exterior slabs should be supported on a cushion of
imported aggregate base to minimized expansive soil movements.
Recommendations given in the geotechnical reports require design and construction of the
proposed projects to follow engineering design criteria needed to improve and/or eliminate
settlement from expansive soils conditions.
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The design and construction of the proposed project in accordance with the engineering
recommendations of the preliminary foundation recommendation by Cleary, and
implementation of Mitigation Measure GEO-1, would ensure that the level of risk from
expansive soils would be less than significant.
e) No Impact. Implementation of the proposed project would not involve the use of septic
tanks or alternative wastewater treatment disposal systems to handle wastewater
generation. Therefore, no impact would result from project implementation.
Sources
Association of Bay Area Governments (ABAG), Earthquake Hazard Map for Palo Alto/Stanford,
Peninsula Segment of the San Andreas Fault System, www.abag.ca.gov/cgi-
bin/pickmapx.pl, accessed July 20, 2009.
California Geological Survey (CGS), Probabilistic Seismic Hazards Mapping Ground Motion
Page, http://redirect.conservation.ca.gov/cgs/rghm/psha/pshamap.asp, accessed July 10,
2009.
CGS, Seismic Hazard Zones, Palo Alto Quadrangle Official Map, October 18, 2006.
CGS, Special Studies Zones, Palo Alto Quadrangle Official Map, July 1, 1974.
California Public Resources Code, Division 2, Geology, Mines and Mining, Chapter 7.8, Seismic
Hazards Mapping, Section 2693(c).
City of Palo Alto, Comprehensive Plan Update, 1996.
City of Palo Alto, Draft and Final Environmental Impact Report, Comprehensive Plan Update,
1996.
Cleary Consultants, Inc., Geotechnical Investigation, Campus Improvements-Group 1, Gunn
High School, July 31, 2009.
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Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
7. Hazards and Hazardous Materials
Would the project:
a) Create a significant hazard to the public or the
environment through the routine transport, use, or
disposal of hazardous materials?
b) Create a significant hazard to the public or the
environment through reasonably foreseeable upset
and accident conditions involving the release of
hazardous materials into the environment?
c) Emit hazardous emissions or handle 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 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 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 airstrip,
would the project result in a safety hazard for people
residing or working in the project area?
g) Impair implementation of or physically interfere with
an adopted emergency response plan or emergency
evacuation plan?
h) Expose people or structures to a significant risk of loss,
injury or death involving wildland fires, including where
wildlands are adjacent to urbanized areas or where
residences are intermixed with wildlands?
Setting
Hazardous materials are handled and stored on a number of properties in Palo Alto, primarily in
the East Bayshore and San Antonia Road/Bayshore corridor, University Avenue/Downtown, the
South of Forest Area, and at the Stanford Research Park. Contamination has resulted from leaking
underground storage tanks, disposal of hazardous materials, and various industrial practices. Fuel
leak sites are concentrated in the areas of University Avenue/Downtown, South of Forest, the
Stanford Research Park, and along San Antonia Road, Alma Street, and El Camino Real.
The California Environmental Protection Agency, Department of Toxic Substances Control
(DTSC) is authorized by the United States Environmental Protection Agency (EPA) to enforce
and implement federal hazardous materials laws and regulations, including disposal and
transportation of hazardous materials.
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Discussion
a, b) Less than Significant with Mitigation. The Department of Toxic Substances Control
(DTSC) EnviroStor database listed one site at or in the vicinity of the school as having had
a past release to soil and/or groundwater (DTSC, 2009). The former Fairchild
Semiconductor site at 4001 Miranda Avenue is currently undergoing remediation. A land
use covenant was recorded in 2003 that prohibits the use of groundwater at the site as a
source of drinking water until groundwater cleanup standards have been achieved (SCCR,
2003). Water supply to the City of Palo Alto, and the project site, is provided by the San
Francisco Public Utilities Commission’s Hetch Hetchy water supply system, which is not
sourced from local groundwater supplies. Therefore, this contamination would not be
considered a hazard to development of the proposed project.
The proposed project includes re-grading in areas prior to new construction. Construction
would require the use of certain hazardous materials such as fuels, oils, solvents, and glues.
Inadvertent release of large quantities of these materials into the environment could
adversely impact soil, surface waters, or groundwater quality. However, implementation of
Mitigation Measure HAZ-1 would reduce the risk associated with hazardous materials
used during construction to a less than significant level.
Mitigation Measure HAZ-1: The PAUSD shall require its contractor(s) to use
construction best management practices typically implemented as part of its
construction activities to minimize the potential adverse effect of the project to
groundwater and soils from construction activities. These shall include the following:
• Follow manufacturer’s recommendations on the use, storage, and disposal of
chemical products used in construction;
• Avoid overtopping construction equipment fuel tanks;
• During routine maintenance of construction equipment, properly contain and
remove grease and oils; and
• Properly dispose of discarded containers of fuels and other chemicals.
c) Less than Significant with Mitigation. The project site consists of an existing high
school. As under existing conditions, proposed development on the campus, including new
classrooms, lounges, recreational facilities, and other associated educational facilities,
would involve storage and use of limited quantities of hazardous materials such as cleaners,
toners, correction fluid, paints, lubricants, kitchen and restroom cleaners, pesticides and
other maintenance materials, but not to the extent of causing a significant impact.
Construction and renovation of the various Master Plan projects would be completed in
phases over a period of several years with some of the work scheduled for the summer
months. Considering the types and quantities of hazardous materials used and stored, and
implementation of Mitigation Measure HAZ-1, the proposed project would not emit or
use acutely hazardous materials during either construction or operation that would
significantly impact the schools or immediate area.
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d) No Impact. The project site is not included on a list of hazardous materials sites compiled
pursuant to Government Code Section 65962.5; therefore, no impact would result (DTSC,
2009).
e, f) No Impact. The project site is not located within the boundaries of the Comprehensive
Land Use Plan (CLUP) for the Palo Alto Airport or within the vicinity of a private airstrip.
No element of the proposed project would result in a safety hazard related to air traffic.
g) Less than Significant. The proposed project would not impair implementation of, or
physically interfere with, an adopted emergency response plan or emergency evacuation
plan. Please also refer to Checklist Item 15, Traffic and Transportation for additional
discussion of emergency access.
h) No Impact. The project site is located in an urbanized area and is not intermixed with or
adjacent to wildlands. There are no elements of the proposed project that would increase
the potential for wildfires in the project vicinity. All new buildings would be required to
comply with all applicable fire code and fire suppression systems, and be approved by the
Division of State Architect for fire and life-safety compliance. Therefore, the proposed
project would not expose people or structures to significant risks associated with wildland
fires.
Sources
California Department of Toxic Substances Control (DTSC), EnviroStor Database,
www.envirostor.dtsc.ca.gov, accessed July 21, 2009.
City of Palo Alto, Comprehensive Plan Update, 1996.
City of Palo Alto, Draft and Final Environmental Impact Report, Comprehensive Plan Update,
1996.
County of Santa Clara, Comprehensive Airport Land Use Plan, Palo Alto Airport, adopted
November 19, 2008.
County of Santa Clara, Wildland Urban Interface Fire Area Map, February 24, 2009.
Santa Clara County Recorder (SCCR), Covenant and Environmental Restriction on Property,
4001 Miranda Avenue, Palo Alto, Document No. 17136705, June 25, 2003.
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Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
8. Hydrology and Water Quality
Would the project:
a) Violate any water quality standards or waste
discharge requirements?
b) Substantially deplete groundwater supplies or interfere
substantially with groundwater recharge such that there would be a net deficit in aquifer volume or a lowering of the local groundwater table level (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 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 of siltation on- or off-site?
d) Substantially alter the existing drainage pattern of the site or area, including through the alteration of the course of a stream or river, or substantially increase the
rate or amount of surface runoff in a manner which
would result in flooding on- or off-site?
e) Create or contribute runoff water which would exceed the capacity of existing or planned stormwater drainage systems or provide substantial additional
sources of polluted runoff?
f) Otherwise substantially degrade water quality?
g) Place housing within a 100-year flood hazard 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 structures which would impede or redirect flood flows?
i) Expose people or structures to a significant risk of
loss, injury or death involving flooding, including
flooding as a result of the failure of a levee or dam?
j) Inundation of seiche, tsunami, or mudflow?
Setting
The City of Palo Alto is located in the watersheds of several creeks and drainageways, including
Adobe, Barron, Matadero, and San Francisquito Creeks. The Santa Clara Valley Water District
regulates creekside development and provides flood control services in the City of Palo Alto.
Barron Creek begins in the foothills of Los Alto Hills and flows northwest through Palo Alto
until it joins Adobe Creek just west U.S. Highway 101. Barron Creek is in a relatively natural
state southwest of the project site. A flood control project was completed in 1996 that diverts
excess flows from the creek into Matadero Creek during large storm events. Barron Creek flows
in an underground culvert across the project site beginning at a Santa Clara Valley Water District
retention basin on the western boundary of the campus.
Most of the urban core of Palo Alto is located within the Federal Emergency Management
Agency (FEMA) Flood Zone X. These areas are outside the 100-year flood zone, but within the
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500-year flood zone. Some areas are located within Special Flood Hazard Areas, which are
subject to flooding in the event of a 100-year flood.
Groundwater in Palo Alto is contained in both shallow and deep aquifers formed in the alluvial
deposits of streams running from the foothills to the San Francisco Bay. Historical saltwater
intrusion in the shallow aquifers along the bay has largely been reversed as alternative sources of
water have been secured for irrigation and other purposes. Surface water bodies in and around the
City include Felt, Searsville, Boronda, and Arastradero RoadLakes and the Lagunita Reservoir.
Discussion
a) Less than Significant with Mitigation. The proposed project could result in potential
water quality impacts during construction phases. Construction activities involving soil
disturbance, excavation, cutting/filling, stockpiling, and grading activities could result in
increased erosion and sedimentation to surface waters, which could produce contaminated
stormwater runoff, a major contributor to the degradation of water quality.
Project construction would also involve use of motorized heavy equipment, including
trucks and other construction vehicles that require fuel, lubricating grease, and other fluids.
Accidental chemical release or spill from a vehicle or equipment could affect surface water.
Such spills could also wash into nearby storm drains or infiltrate into soil affecting
groundwater quality. However, the volume of material would not be significant; therefore
runoff and groundwater pollution resulting from use of construction vehicles is considered
minimal. Furthermore, implementation of standard construction procedures and precautions
as discussed under Section 7, Hazards and Hazardous Materials, would ensure that
impacts related to construction vehicle pollutants would be less than significant.
The NPDES permit program under the Federal Clean Water Act controls water pollution by
regulating point and nonpoint sources that discharge pollutants into “waters of the U.S.”
Authority for NPDES permitting has been delegated by the federal government to the
California State Water Resources Control Board (SWRCB), which has nine regional
boards; the San Francisco Bay Regional Water Quality Control Board (RWQCB) regulates
water quality in the project area.
The Santa Clara Valley Urban Runoff Pollution Prevention Program (SCVURPPP) is an
association of thirteen cities and towns in the Santa Clara Valley (including Palo Alto),
together with Santa Clara County and the Santa Clara Valley Water District. Program
participants share a common permit to discharge stormwater to South San Francisco Bay.
The RWQCB issued the SCVURPPP its first NPDES permit in 1990, and reissued the
permit in 1995. In 2001, the SCVURPPP was reissued its third NPDES permit and
provision C.3 of the permit was also revised to address post-construction and some
construction phase impacts of new and redevelopment projects on stormwater quality.
Provision C.3 calls for enhancement of the existing performance standard to increase the
effectiveness of existing implementation, primarily by: 1) setting volume and flow based
hydraulic sizing criteria for stormwater treatment measures; 2) setting minimum sizes of
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new development and redevelopment projects which must employ the treatment measures;
3) creation of a program to assure the adequate operation and maintenance of treatment
measures occurs; 4) creation of standards for source control measures and site design
measures which can lead to reduced impervious surface for a given equivalent land use;
and 5) development of a process and criteria to limit changes in the runoff hydrograph for
new and redevelopment, where those changes could have a harmful effect on downstream
beneficial uses by excessive erosion of the bed and bank of downstream watercourses.
Stormwater discharges from construction activities on one acre or more are regulated by the
RWQCB and are subject to the permitting requirements of the NPDES General Permit for
Discharges of Stormwater Runoff Associated with Construction Activity (General
Construction Permit). The General Construction Permit requires the preparation and
implementation of a SWPPP for construction activities. As described in Checklist Item 6,
Geology and Soils, above, the SWPPP must be prepared before the construction begins, and
in certain cases, before demolition begins. The SWPPP must include specifications for
BMPs that would need to be implemented during project construction. BMPs are measures
that are undertaken to control degradation of surface water by preventing soil erosion or the
discharge of pollutants from the construction area. The SWPPP must describe measures to
prevent or control runoff after construction is complete and identify procedures for
inspecting and maintaining facilities or other project elements.
The proposed project would disturb approximately 2.4 acres (DLM, 2009), exceeding the
NPDES one-acre threshold; therefore, the PAUSD would be required to apply to the
RWQCB for the General Construction Permit and comply with the SCVURPPP NPDES
requirements that apply to “significant redevelopment” projects. Implementation of a
SWPPP as required by Mitigation Measure HYD-1 would ensure that the proposed
project would not violate any water quality standards or waste discharge requirements and
reduce potential impacts to a less than significant level.
Mitigation Measure HYD-1: The PAUSD shall apply for coverage under the State
General Construction Permit to comply with federal NPDES regulations. The
NPDES and State General Construction Permit require a project applicant to develop
and implement a Storm Water Pollution Prevention Plan (SWPPP) that identifies
appropriate construction BMPs in order to minimize potential sedimentation or
contamination of storm water runoff generated from the project site. BMPs could
include, without limitation, silt fences, gravel or sand bag berms, storm drain inlet
protection, soil stockpile protection, preservation of existing vegetation, use of straw
mulch, dust control, and others. The SWPPP shall also include any additional
measures identified in the Santa Clara Valley Urban Runoff Pollution Prevention
Program, as required. The District shall adhere to the identified BMPs as well as the
waste discharge and stormwater requirements outlined in the permit.
b) Less than Significant. Preliminary geotechnical investigation of the project site indicated
that the uppers soils are considered unsuitable for proposed building foundations and slabs
and would require excavation and replacement with engineered fill to a depth of at least 3.0
feet below the ground surface (see Section 6, Geology and Soils). The water level was
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encountered in borings at depths of 25 to 30 feet. Therefore, the potential for intercepting
groundwater and depleting groundwater supplies or recharge through excavation or
subsurface foundations is considered to be low. Water supply to the City of Palo Alto is
provided by the City Utilities Department through purchases from the San Francisco Public
Utilities Commission’s Hetch Hetchy water supply system. The proposed project would not
involve depletion of groundwater supplies; however, it would increase the amount of
impervious surface area and thereby reduce the potential amount of groundwater recharge.
As mentioned above, the proposed project would have to comply with the C.3 requirements
which include measures for reducing the amount of flow from offsite and using
biofiltration improvements to the extent possible. Adherence to these requirements would
reduce the amount of offsite runoff volumes and create a less than significant impact to
groundwater supplies.
c, d) Less than Significant with Mitigation. Proposed new structures and other improvements
on the project site would not alter existing drainage patterns, nor would there be any
alteration to the existing Santa Clara Valley Water District retention basin located on the
western boundary of the campus. Although soil erosion could occur due to project
construction, the resulting operational surface runoff rates would not significantly increase
due to the generally flat topography of the project site and the relatively small net increase
in impervious surface areas occurring during each individual phase of the Master Plan. The
potential for accelerated runoff flow rates or flooding would be low. The use of BMPs and
adherence to SWPPP and NPDES permit requirements as described in Mitigation
Measure HYD-1, above, would reduce potential erosion and flooding impacts to a less
than significant level.
e) Less than Significant with Mitigation. As discussed above, the surface runoff rates
resulting from operation of individual phases of the Master Plan would not significantly
increase due to the generally flat topography of the project site and the relatively small net
increase in impervious surface area. Stormwater runoff would flow from the project site
into the City of Palo Alto’s stormwater drainage system, which would be adequate to
handle any increase in flows resulting from the proposed project. In addition, stormwater
treatment measures required as part of the NPDES permit described in Mitigation
Measure HYD-1, including, but not limited to, vegetated swales, detention basins, and
landscape infiltration systems, must be hydraulically sized to treat a specified amount of
runoff, and they must include provisions to meet ongoing maintenance needs. Therefore,
the project’s impact on the stormwater drainage system would be less than significant.
f) Less than Significant with Mitigation. As discussed in a) and c) above, construction is the
only phase of the proposed project that could affect water quality. Stormwater runoff would
be controlled on-site using standard engineering practices and as required by Mitigation
Measure HYD-1. Therefore, substantial degradation of water quality would not be
expected and the proposed project’s impact would be less than significant.
g, h) Less than Significant. According to the FEMA Flood Insurance Rate Map covering the
project area, a narrow band designated as Zone A runs across the project site above Barron
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Creek, which is undergrounded in a culvert (FEMA, 2009). This area begins at the Santa
Clara Valley Water District retention basin on the western boundary of the campus, runs
between the gymnasium and football field, and exits the campus near Los Robles Avenue.
Zone A areas are subject to flooding by the one percent annual chance flood, which is a
flood event that has a one percent chance of occurring in any given year (also known as the
100-year flood). No base flood elevations have been determined for Zone A areas. The
proposed project would include construction of new basketball and tennis courts that may
be located within small sections of this zone. These improvements are not anticipated to
significantly impede or redirect flood flows on the project site; therefore the impact would
be considered less than significant.
i) No Impact. The project site is not located within any dam failure inundation area;
therefore, no impact would occur.
j) No Impact. Although tsunamis could occur and cause tidal surges in San Francisco Bay,
these events are extremely rare and the project site is located sufficiently far enough away
from the Bay shoreline that tsunamis would not impact the project site. No water bodies
large enough to cause a seiche are located in the vicinity of the project site. The potential
for mudflows or landslides is discussed under Section 6, Geology and Soils. No impact
would occur due to inundation of seiche or tsunami.
Sources
City of Palo Alto, Comprehensive Plan Update, 1996.
City of Palo Alto, Draft and Final Environmental Impact Report, Comprehensive Plan Update,
1996.
Deems Lewis McKinley, Gunn High School, Site Perviousness, 2009.
Federal Emergency Management Agency (FEMA), Flood Insurance Rate Map (FIRM), Santa
Clara County, Map Number 06085C0019H, May 18, 2009.
Santa Clara Valley Urban Runoff Pollution Prevention Program, www.scvurppp-wk2.com,
accessed July 14, 2009.
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Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
9. Land Use and Planning
Would the project:
a) Physically divide an established community?
b) Conflict with any applicable land use plan, 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 conservation plan
or natural community conservation plan?
Setting
Gunn High School is located on an approximately 48-acre site northeast of the intersection of
Arastradero Road and Foothill Expressway. The campus includes 17 permanent buildings
clustered on the southern portion of the campus. Adjacent land uses include residential areas on
the north and east, Alta Mesa Cemetery on the south, and the Veterans Affairs (VA) Palo Alto
Health Care Systems campus on the west.
Local Plans and Policies
The following policies from the Land Use and Community Design Element and the Community
Services and Facilities Element of the City of Palo Alto Comprehensive Plan are relevant to the
proposed project:
Policy L-5: Maintain the scale and character of the City. Avoid land uses that are overwhelming
and unacceptable due to their size and scale.
Policy L-7: Evaluate changes in land use in the context of regional needs, overall City welfare
and objectives, as well as the desires of surrounding neighborhoods.
Policy L-48: Promote high quality, creative design and site planning that is compatible with
surrounding development and public spaces.
Policy L-61: Promote the use of community and cultural centers, libraries, local schools, parks,
and other community facilities as gathering places. Ensure that they are inviting and
safe places that can deliver a variety of community services during both daytime and
evening hours.
Policy L-71: Strengthen the identity of important community gateways, including entrances to the
City at…Embarcadero Road at El Camino Real.
Policy C-4: Maintain a close, collaborative relationship with the PAUSD to maximize the use of
school services and facilities for public benefit, particularly for young people,
families, and seniors.
Policy C-5: Recognize the importance of schools to the social and economic vitality of the City.
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Policy C-6: Continue and enhance City efforts to assist PAUSD in anticipating and addressing
land development-related school enrollment impacts.
The General Plan designates the project site as School District Lands. This land use designation
applies to properties owned or leased by public school districts and used for educational,
recreational, or other non-commercial, non-industrial purposes. Floor area ratio may not exceed
1.0. The campus is zoned PF-Public Facilities, which is designed to accommodate governmental,
public utility, educational, and community service or recreational facilities.
The California Constitution (Article 9, Section 6), prohibits the PAUSD, as a component of the
state’s public school system, from being placed under the jurisdiction of a local government.
Therefore, the PAUSD is exempt from the requirement to comply with local land use controls,
including local general plans and zoning ordinances, within the District’s boundaries. However,
the PAUSD attempts to ensure its Master Plan is compatible with the goals and policies of the
City of Palo Alto to the extent feasible. Goals of the Master Plan are listed below:
• Give organization and structure to the campus
• Create a hierarchy of open space
• Utilize in-between spaces—preserve open space
• Create edges to open space and buildings
• Define and articulate building entries
• Provide growth strategies—consolidate departmental functions
Discussion
a, b) Less Than Significant. The land uses proposed as part of the Master Plan would represent
a continuation of established public education land uses that have existed on the project site
for several decades. The project therefore would not deviate from established development
patterns on the project site or in the vicinity. New development would be designed in
keeping with the predominant styles of the existing campus architecture. As such, the new
uses proposed as part of the project would be consistent with, and would represent an
enhancement of, existing educational uses on the Gunn campus.
While the proposed Master Plan would represent changes and improvements to the existing
campus, the proposed project would not cause a significant adverse land use impact.
Furthermore, all potential physical environmental effects of the proposed project on
adjacent land uses during construction (including traffic, noise, air quality) are addressed
and mitigated where required to the extent feasible throughout this environmental
document.
The campus improvements and educational uses proposed as part of the project would not
substantially conflict with the goals and policies in the City of Palo Alto Comprehensive
Plan. Moreover, although not bound by local land use ordinances, project components
proposed by the PAUSD would nonetheless be consistent with the land use designation and
zoning for the campus. The project would also require review and approval by Board of
Education and would be required to meet design criteria established by the Department of
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General Services, Division of the State Architect, which is responsible for review of the
architectural plans and construction documents.
In conclusion, the proposed project would not disrupt or divide the physical arrangements
of existing uses and activities that surround them, nor would the proposed physical changes
displace any businesses, residences, or other uses. Therefore, land use impacts are
considered less than significant and no mitigation is required.
c) No Impact. As discussed in Section 4, Biological Resources, no Habitat Conservation Plan,
Natural Community Conservation Plan, or other approved local, regional, or state habitat
conservation plan exist within the project boundaries.
Sources
City of Palo Alto, Comprehensive Plan Update, 1996.
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Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
10. Mineral Resources
Would the project:
a) Result in the loss of availability of a known mineral
resource that would be of value to the region and the
residents of the state?
b) Result in the loss of availability of a locally-important
mineral resource recovery site delineated on a local
general plan, specific plan or other land use plan?
Discussion
a, b) No Impact. According to the Santa Clara County General Plan, the project site does not
contain any known mineral resources. No impact would result.
Sources
Santa Clara County, General Plan 1995-2010, adopted December 20, 1994.
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Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
11. Noise
Would the project result in:
a) Expose persons to or generate noise levels in excess
of standards established in the local general plan or
noise ordinance, or applicable standards of other
agencies?
b) Exposure of persons to or generation of excessive
groundborne vibration or groundborne vibration
levels?
c) A substantial permanent increase in ambient noise
levels in the project vicinity above levels existing
without the project?
d) A substantial temporary or periodic increase in
ambient noise levels in the project vicinity above
levels existing without the project?
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?
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?
Discussion
a) Less Than Significant with Mitigation. The California Department of Education (CDE)
requires all school districts to select school sites that provide safety and support learning.12
Because the CDE recognizes that unwanted sound can be distracting and can present an
obstacle to learning, the CDE requires school districts to consider noise in the site selection
process.13 The School Site Selection and Approval Guide document recommends that this
be accomplished with an assessment of noise from major roadways and railroads during
environmental review of school construction.14 If PAUSD considers a potential school site
near a freeway or other source of noise, CDE recommends hiring an acoustical engineer to
determine the level of sound that the location is subjected to and to assist in designing the
school. The American Speech Language-Hearing Association (ASLHA) guidelines
recommend that in classrooms sounds dissipate in 0.4 seconds or less (and not reverberate)
and that background noise not rise above 30 dBA.15 While PAUSD has not adopted any
specific interior noise standard for its classrooms, other districts, such as Los Angeles
Unified have adopted an interior standard of 45 dBA.
12 California Department of Education (CDE), Regulations (CCR Tit. 5, Div. 1, Ch. 13 Subchapter 1, Article 2
§14010 “Standards for School Site Selection”)
13 CDE Regulations (CCR Tit. 5, Div. 1, Ch. 13 §14010(q))
14 CDE, School Facilities Planning Division. 2001. School Site Selection and Approval Guide. March.
15 Ibid.
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Long-term (24-hour) noise monitoring was conducted at two locations on the Gunn campus
to determine the existing noise environment of proposed locations of new classrooms.
The first location monitored was the location of the proposed Group 1, six-classroom
building. Noise sources in this area are dominated by vehicle traffic on Arastradero Road
which is approximately 100 feet from the southern building façade. Daytime hourly
average noise levels at this location ranged from 63 to 67 dBA with a (logarithmic) average
of 64 dBA.
The second location monitored was the location of the proposed Group 1, 2-story, 28-
classroom building. Noise sources in this area are dominated by students as there are no
roadways within several hundred feet of this location. Daytime hourly average noise levels
at this location ranged from 49 to 58 dBA with a (logarithmic) average of 53 dBA.
Standard building construction methods typically result in an exterior to interior noise
reduction of 15 to 20 dBA (HUD, 2004), which would be insufficient to meet the
recommended goals of the ASLHA. The location of the 28-classroom building could
achieve the generally accepted 45 dBA standard for interior residential spaces without
special insulation considerations. Consequently, classroom buildings will need to be
designed to incorporate sound insulation sufficient to maintain interior noise levels
appropriate for a classroom.
Mitigation Measure NOI-1: The PAUSD shall collaborate with a certified
acoustical engineer to assist in design and verification of noise insulation measures
for the classrooms proposed under the Master Plan.
b) Less than Significant with Mitigation. In discussing whether the project would expose
people to severe noise via airborne or ground-borne vibrations, this analysis examines the
impact of construction activities associated with the project on the existing sensitive
receptors in the vicinity of the site.
Ground-borne vibration from activities that involve “impact tools,” especially pile driving
could produce significant vibration. It is unknown, at the Master Plan level, whether pile
driving would be required for two-story classroom buildings to meet seismic code. Pile
driving can result in typical peak particle velocities (PPV) of 0.64 inches per second at a
distance of 25 feet, which would exceed the criteria published by the U.S. Department of
Transportation (DOT) of 0.2 inches per second for the protection of non-engineered timber
and masonry buildings and 0.3 inches per second for concrete and masonry buildings with
no plaster. Distances of 55 and 42 feet are required for the attenuation of pile driving
vibrations to below these respective building protection thresholds. The nearest existing
buildings to the proposed building locations are adjacent language classrooms,
approximately 30 feet away. The nearest residences would be located over 300 feet away
from any proposed building locations and would not be susceptible to building damage
from pile driving activity. Consequently, the potential for adjacent building damage would
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be a concern at the nearest adjacent classrooms if installation of piles were a necessary
construction method and mitigation measures are recommended.
Vibration levels can also result in interference or annoyance impacts to residences or other
land uses where people sleep, such as hotels and hospitals. Vibration annoyance impact
criteria published by U.S. DOT relative to daytime residential land uses (the most
applicable use listed to a classroom) are established in terms of vibration decibels (VdB).
VdB’s are generally used when evaluating human response to vibrations, as opposed to
structural damage, where PPV is the more commonly used descriptor. Vibration decibels
are established relative to a reference quantity, typically 1 x 10-6 inches per second.16
The criterion for vibration annoyance established by U.S. DOT for daytime residential uses
(again, the most applicable use listed to a classroom) is 78 VdB. Pile driving can result in
typical vibrations of 104 Vdb at a distance of 25 feet. The nearest residence to the proposed
two-story classrooms would be located approximately 300 feet away at which distance
vibrations from pile driving activities would be reduced to 72 Vdb. This would be a less
than significant vibration impact to the nearest residences. However, annoyance impacts
would be a concern at the nearest adjacent classrooms if installation of piles were a
necessary construction method and therefore, mitigation measures are recommended.
Mitigation Measure NOI-2: To reduce potential structural damage impacts from
pile driving (if necessary), PAUSD shall employ the following measures:
• Verify the construction method of adjacent buildings of concern. If buildings
are constructed of reinforced concrete, steel or timber without plaster, these
structures can withstand vibrations of up to 0.5 PPV without structural damage.
If located at a distance of at least 30 feet from pile locations potential structural
impacts would be considered less than significant.
• Use alternative driving methods. If adjacent buildings are non-engineered
timber and masonry buildings or concrete and masonry buildings with no
plaster then alternative driving methods may be employed to reduce vibration
impacts to a less than significant level. Use of a sonic (or vibratory) pile driver
can result in typical vibration levels being reduced from 0.644 feet per second
to 0.170 feet per second (U.S. DOT, 2006). Alternatively pile holes may be
pre-drilled to reduce vibrations.
Mitigation Measure NOI-3: To reduce the potential for annoyance impacts from
pile driving (if necessary) at occupied adjacent classrooms, PAUSD shall have the
contractor schedule any pile driving activities during the summer or winter breaks or
other times when classrooms within a 150-foot radius are unoccupied. Additionally,
any required pile driving should be restricted to daytime hours.
c) Less than Significant. Future development of the site could generate noise from motor
vehicle trips as well as from stationary sources (i.e., HVAC equipment etc.) that could
adversely affect nearby noise-sensitive land uses.
16 Ibid.
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Noise from air handling equipment would be located more than 300 feet away from the
nearest sensitive receptor and would be no different than the existing equipment located on
campus buildings. Given the presence of other noise sources between the site and the
nearest residential receptors, noise from air handling equipment would not represent a
significant noise impact.
Noise level projections from roadway traffic increases were made using traffic data and the
TNM version 2.5 Lookup Noise Prediction Model of the Federal Highway Administration
(FHWA) for those road segments that would experience the greatest increase in traffic
volumes and/or that would pass nearest to residential areas. The model is based on the
TNM reference noise factors for automobiles, medium trucks, heavy trucks, and buses with
consideration given to vehicle volume, speed, roadway configuration, and distance to the
receiver.
The results of the modeling are presented in Table 2 for existing and existing plus project
scenarios. The traffic analysis indicates that the proposed project would generate
approximately 532 total daily vehicle trips. This traffic would be distributed over the local
street network and would affect roadside noise levels. For the modeling effort, a.m. peak
hour traffic volumes during weekdays were used as a worst-case analysis because the
proposed project would contribute more traffic to the a.m. peak hour than to the a.m. peak
hour. Modeled existing noise levels shown in Table 2 correspond to a distance of 50 feet
from the centerline of applicable roadway segments.
As presented in Table 2, roadway traffic noise increases resulting from the proposed project
would be less than 1 dBA. Generally, even in a laboratory environment, increases of less
than 1 dBA are too small to be detected by the human ear (Caltrans, 1998). Consequently,
increases in roadway noise resulting from the proposed project would be less than
significant.
TABLE 2
TRAFFIC NOISE INCREASES IN ROADSIDE LEQ
Road Segment Existing
Existing +
Project
Contribution of
Proposed Project
1. Arastradero Road (between Foothill Expressway and
Old Trace Road) 63.4 63.4 0.0
2. Arastradero Road (between Gunn Driveway and Donald
Drive) 65.3 65.4 0.1
3. Foothill Expressway (between Arastradero Road and
Edith Avenue) 68.3 68.3 0.0
a These listed values represent the modeled existing noise levels from mobile sources along specified roadways and are based on traffic
data. Road center to receptor distance is assumed to be 50 feet. The speed limit for these segments is assumed to be 25 miles per hour
except for Arastradero Road 45 miles per hour for Foothill Expressway.
SOURCE: ESA, 2009.
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d) Less than Significant with Mitigation. Noise standards are typically addressed in Title 24,
local General Plan policies and local noise ordinance standards. The City of Palo Alto
Noise Ordinance (Section 9.10.060 of the Municipal Code) establishes construction noise
regulations in the City. The noise ordinance restricts the allowable hours for construction to
between 8:00 a.m. and 6:00 p.m. on weekdays. Construction may occur on weekends
between 9:00 a.m. and 5:00 p.m. on Saturdays. Construction activities are prohibited on
Sundays and holidays. In addition, no individual pieces of construction equipment are
allowed to exceed 110 dBA at a distance of 25 feet.
Construction of future buildings would involve demolition of some existing structures at the
site and the construction of one and two-story classrooms and renovations of existing
buildings. Various types of equipment would be used for demolition and construction
purposes. Some of this equipment would generate relatively steady-state noise levels, such as
the noise from diesel engines, and other equipment would generate impulse or impact noise.
Construction noise levels at and near locations on the project site would fluctuate
depending on the particular type, number, and duration of use of various types of
construction equipment. The effect of construction noise depends upon how much noise
would be generated by construction, the distance between construction activities and the
nearest noise-sensitive uses, and the existing noise levels at those uses.
Table 3 presents typical noise levels generated by construction equipment. As shown in
Table 3, the noisiest phases of (non-pile driving) construction would generate
approximately 88 Leq at 50 feet. Pile driving, if necessary, would generate noise levels of
approximately 101 dBA at 50 feet. All of these construction equipment noise levels would
be consistent with the restriction of the City’s municipal code.
The receptors nearest to the proposed construction activities would be adjacent classrooms.
The nearest residences to proposed construction activities would be located 300 feet from
the proposed gymnasium.
TABLE 3
TYPICAL CONSTRUCTION EQUIPMENT NOISE EMISSION LEVELS
Equipment Noise Level (Leq)a
Shovel (Excavator) 82
Back Hoe 80
Concrete pumps 82
Jack Hammer 88
Pneumatic tools 85
Truck 88
Pile Driving 101
a Estimates correspond to a distance of 50 feet from the piece of equipment. SOURCE: U.S. Department of Transportation, Transit Noise and Vibration Impact
Assessment, May 2006.
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While construction-related noise would be within the limits established by the City’s noise
ordinance, construction noise could be a nuisance to the nearest sensitive receptors.
Consequently, mitigation measures are recommended to reduce noise impacts of project
construction on adjacent sensitive receptors.
Mitigation Measure NOI-4: Construction contractors shall be required to follow
appropriate time restrictions consistent with the City’s Municipal Code. Specifically,
it is recommended that contractors be required to limit noisy construction activities,
including related on-road truck use in the immediate project vicinity, to the hours of
8:00 a.m. to 6:00 p.m. on weekdays. No construction shall be allowed on Sundays
and legal holidays. In addition, although not required, it is recommended that the use
of impact tools (e.g., hoe-ram, jackhammers, pile driver) be limited to the hours of
8:00 a.m. to 5:00 p.m.
Construction Related Noise Attenuation Measures
• Notify adjacent residents of any planned pile-driving activities, as well as any
particularly noisy activity that would affect them for a given short period of
time so they can plan their activities accordingly.
• Ensure that all diesel equipment is equipped with effective mufflers, in
accordance with the manufacturer’s specifications, and that the mufflers are in
good repair.
• Use temporary noise barriers along the perimeter of the sites, to the maximum
extent feasible during demolition and grading activities.
• Locate stationary noise-generating equipment such as generators and
compressors as far as possible from the nearest residential property line.
• Locate any construction trailers or offices as far from the adjacent residential
uses as possible.
Implementation of the above mitigation measures would reduce the impact to less than
significant levels.
e, f) No Impact. There are no public use airports or private air strips within a two mile radius of
the project site. Consequently, there are no noise or vibration impacts associated with these
uses that would occur on the project site.
Sources
Caltrans, Technical Noise Supplement, 1998.
U.S. Department of Transportation, Federal Traffic Administration (FTA), Transit Noise and
Vibration Impact Assessment, May 2006.
U.S. Department of Housing and Urban Development, Office of Community Planning and
Development, The Noise Guidebook, updated, August, 2004.
Initial Study
Gunn High School Master Plan 69 ESA / 209002
Initial Study September 2009
Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
12. Population and Housing
Would the project:
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)?
b) Displace substantial numbers of existing housing,
necessitating the construction of replacement housing
elsewhere?
c) Displace substantial numbers of people, necessitating
the construction of replacement housing elsewhere?
Discussion
a) Less than Significant. As described in the Project Description, the purpose of the proposed
project is to renovate existing aging facilities, and to provide additional building capacity,
as well as various infrastructure and site access/circulation/landscaping upgrades consistent
with the Master Plan. Student enrollment is anticipated to incrementally increase within the
PAUSD over the time period of the Master Plan buildout in 2017. However, the proposed
project would not, in itself, induce student growth within the PAUSD, but rather, better
accommodate existing and planned student enrollment within the PAUSD. Furthermore,
utility infrastructure improvements are intended to improve utility service at the project
site, and would not be oversized to potentially serve additional growth within the area.
b, c) Less than Significant. The proposed project would not displace any existing housing or
generate a demand for housing elsewhere. Furthermore, the project would not result in a
displacement of people from the project site. No impact would result.
Sources
PAUSD, Gunn High School Master Plan, 2009.
Lapkoff & Gobalet Demographic Research, Inc., Enrollment Forecasts for PAUSD Middle and
High Schools, January 12, 2009.
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Initial Study September 2009
Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
13. Public Services
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:
i) Fire protection?
ii) Police protection?
iii) Schools?
iv) Parks?
v) Other public facilities?
Setting
Fire Protection Services
Fire protection services to the project site are provided by the City of Palo Alto Fire Department.
The Fire Department has approximately 122 employees and staffs seven full time stations located
throughout the City and on the Stanford University campus. To provide coverage in the sparsely
developed hillside areas, an additional fire station in the foothills is operated during summer
months when fire danger is high. Service areas for the Fire Department include the Stanford
University campus, the Stanford Linear Accelerator Center (SLAC), and unincorporated areas of
Santa Clara County. The nearest fire station to the Gunn campus is Fire Station No. 5 at 600
Arastradero Road, which is approximately one-mile from the campus. The City also has mutual
aid agreements with Menlo Park, Mountain View, Los Altos, and Woodside.
In fiscal year 2007-08, the Fire Department responded to an average of 21 calls per day. The
average response time for fire calls was 6 minutes 48 seconds, and the average response time for
medical/rescue calls was 5 minutes 24 seconds. There were more than 4,500 medical/rescue
incidents and 192 fire incidents (including 43 residential structure fires) in 2007-2008. The Fire
Department also performed 1,277 fire inspections and 406 hazardous materials inspections.
Police Protection Services
Law enforcement services to the project site are provided by the Palo Alto Police Department.
The Police Department has 169 personnel; it shares Special Weapons and Tactical (SWAT)
Teams with Los Altos and Mountain View and provides dispatching to the Stanford University
Police through the City’s Communications Center.
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Initial Study September 2009
The Police Department handled more than 58,700 calls for service in fiscal year 2007-08, or
about 161 calls per day. The average response time for emergency calls is 4 minutes 32 seconds.
Police Department statistics show 127 reported crimes per 1,000 residents, with 87 reported
crimes per officer last year. The Police Department is located at 275 Forest Avenue,
approximately four miles from the Gunn campus.
Public Schools
The PAUSD attendance area includes the City of Palo Alto, Stanford University, and areas of
Los Altos Hills, Palo Alto Hills, and Portola Valley. The PAUSD consists of twelve elementary
schools (grades K-5), three middle schools (6-8), and two high schools (9-12). In addition, the
District operates a pre-school, Young Fives program, a self-supporting Adult School, the Hospital
School at Stanford’s Lucille Packard Children’s Hospital, and summer school. The total District
enrollment for the 2008/2009 school year is 11,431.
Discussion
a.i-ii) Less than Significant. The proposed project would result in construction of new buildings
and other site improvements to accommodate anticipated enrollment increases through
buildout of the Master Plan in 2017. While no off-site access improvements are proposed,
parking and drop-off areas would be reconfigured as part of the project to improve
vehicular, pedestrian, and bicycle circulation and safety on the campus. The proposed
project would be required to comply with all applicable requirements of the California Fire
Code, and be consistent with the California Building Code regarding life safety issues,
including emergency vehicle access. In addition, during the construction document phase,
all plans would be subject to review and approval by the Division of State Architect for a
fire and life-safety compliance review. In consideration of these factors, the proposed
project would not adversely affect the ability of the Palo Alto Fire and Police Departments
to maintain adequate fire and police protection services, or result in the need for expanded
public services that would result in the need for new or expanded facilities.
a.iii) No Impact. There are no elements of the proposed project that would adversely affect
public schools. Consequently, no impact is anticipated.
a.iv) Less than Significant. Refer to Section 14, Recreation, for a discussion of the need for
additional park and recreational facilities, and the potential environmental impacts
associated with the provision of new facilities.
a.v) Less than Significant. The proposed project would not adversely affect any other public
services in the City of Palo Alto.
Sources
City of Palo Alto, City Auditor, Annual Report on City Government Performance, Service Efforts
and Accomplishments Report FY 2007-2008, Summary, January 2009.
City of Palo Alto, Comprehensive Plan Update, 1996.
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Gunn High School Master Plan 72 ESA / 209002
Initial Study September 2009
City of Palo Alto, Draft and Final Environmental Impact Report, Comprehensive Plan Update,
1996.
City of Palo Alto, Fire Department, www.cityofpaloalto.org/depts/fir/news, accessed July 22,
2009.
City of Palo Alto, Police Department, www.cityofpaloalto.org/depts/pol/news, accessed July 22,
2009.
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Gunn High School Master Plan 73 ESA / 209002
Initial Study September 2009
Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
14. Recreation
Would the project:
a) Would the project increase the use of existing
neighborhood and regional parks or other recreational
facilities such that substantial physical deterioration of
the facility would occur or be accelerated?
b) Does the project include recreational facilities or
require the construction or expansion of recreational
facilities which might have an adverse physical effect
on the environment?
Setting
The City of Palo Alto owns and operates 28 neighborhood and district parks totaling
approximately 190 acres. They range in size from one-half to two-acre mini-parks to “district”
parks that serve the entire community and feature playing fields, picnic grounds, and community
centers. Many parks feature specialized facilities such as tennis courts, basketball courts, skate
bowls, community gardens, dog exercise areas, and par courses. The City also owns and operates
several large open space preserves such as Foothills Park. The Recreation Division provides
numerous programs, classes, and special events. Recreation facilities include community centers,
pools (including the new Gunn High School Aquatic Center), and a teen center. The City also
maintains PAUSD athletic fields and tennis courts at all elementary and middle school sites and
manages public use of those facilities. The City of Palo Alto brokers all city athletic fields, tennis
courts and Palo Alto Unified School District school fields. Park Services also maintains school
athletic fields and tennis courts at all elementary and middle school sites. Parks in the vicinity of
Gunn High School include Bol, Briones, and Terman Parks.
Discussion
a, b) Less than Significant. Implementation of the proposed project over buildout of the Master
Plan in 2017 and associated incremental increase in student population at the project site
would not substantially increase the use of existing neighborhood or regional parks in the
vicinity or cause substantial physical deterioration of those facilities.
Construction of the new gymnasium is proposed to occur in the area currently occupied by
tennis and basketball courts. Some or all of these facilities would be temporarily disrupted
during construction of the new gym. Approximately 45 other tennis courts located at other
schools and parks throughout the City of Palo Alto (including four at nearby Terman Park)
would be available for use by the public during the closure of Gunn’s courts. New tennis
and basketball courts would be constructed in areas adjacent to the new gym. Any potential
environmental effects associated with the construction and operation of these recreational
facilities are discussed in this environmental document and mitigated to a less than
significant level.
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Initial Study September 2009
Sources
City of Palo Alto, Community Services Department, www.cityofpaloalto.org/depts/csd, accessed
July 22, 2009.
City of Palo Alto, Comprehensive Plan Update, 1996.
City of Palo Alto, Draft and Final Environmental Impact Report, Comprehensive Plan Update,
1996.
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Initial Study September 2009
Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
15. Transportation/Traffic
Would the project:
a) Cause an increase in traffic which is substantial in
relation to the existing traffic load and capacity of the
street system (i.e., result in a substantial increase in
either the number of vehicle trips, the volume-to-
capacity ratio on roads, or congestion at intersections)?
b) Exceed, either individually or cumulatively, a level of
service standard established by the county congestion
management agency for designated roads or
highways?
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?
d) Substantially increase hazards due to a design feature
(e.g., sharp curves or dangerous intersections) or
incompatible uses (e.g., farm equipment)?
e) Result in inadequate emergency access?
f) Result in inadequate parking capacity?
g) Conflict with adopted policies, plans, or programs
supporting alternative transportation (e.g., bus
turnouts, bicycle racks)?
Setting
Gunn High School is located on Arastradero Road immediately east of Foothill Expressway. The
school has one primary entrance from Arastradero Road at the southeastern corner of the campus.
The driveway includes two lanes in each direction and is signalized. A secondary driveway is on
Miranda Avenue.
Existing Traffic Volumes and Intersection Lane Configurations
Four study intersections that would be most affected by project traffic were selected for analysis:
1. Arastradero Road and Foothill Expressway
2. Arastradero Road and Miranda Avenue
3. Arastradero Road and School Driveway
4. Arastradero Road and Donald/Terman Road
The study intersections were analyzed during weekday a.m. peak-hour traffic conditions. Peak
traffic conditions, which would coincide with school traffic, typically occur during the morning
commute periods (between 7:00 a.m. and 9:00 a.m.). Intersection operations were evaluated for
the one hour during the morning peak period for which the highest traffic volumes were
measured.
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Initial Study September 2009
Vehicle counts at the driveway were conducted at the start and end of the school day on a Friday
in March (March 16, 2009). The counts included inbound and outbound vehicles, as well as count
of parked cars by location.
Morning drop-offs and afternoon pick-ups are part of the student commute. Under existing
conditions, over 550 vehicles are inbound (includes both drop-offs and parking) to the site in 30
minutes and over 700 in less than 90 minutes as illustrated in Figure 11. Inbound traffic from the
east on Arastradero Road is backed-up out of the right turn lane into the right or curb lane for
several blocks. The backup lasted for approximately 15- to 20-minutes and peaked just before the
first class.
During observations, vehicles were primarily dropping-off and picking-up at the front of the
school as illustrated at Location B in Figure 11. Drives followed the entrance road north, turned
left into the drop-off area and then exited back on to Arastradero Road. The entrance includes two
northbound lanes to the beginning of the drop-off lane. At that point, one lane turns left into the
drop-off area while the other continues northerly to student and staff overflow parking areas.
Vehicles leaving the rear parking areas are routed through the drop-off area to Arastradero Road.
Parking at the high school is currently concentrated in three locations as show in Figure 11. The
school has a total of 461 parking spaces. Lots D, E, F, and G, with a total of 147 parking spaces
are reserved for staff and visitors (part of lot G). Lot I with 17 spaces on the west side of the
campus is reserved for staff. Lots A, B, and C with the majority of the parking (294 spaces) are
located toward the rear of the site and are used for staff overflow and students.
Parking demand at the high school fluctuates very little over the course of the day, but generally,
the lots in close proximity to the campus buildings (Lots D, E, and G) can exceed capacity
periodically as people arrive and depart during the day, The student lots, particularly Lot A,
generally has 60 to 80 spaces available throughout the day. As a whole, the school had a peak
parking demand for approximately 440 parking spaces (95 percent).
Existing Intersection Operations
The operations of roadway facilities are described with the term Level of Service. Level of Service
(LOS) is a qualitative description of traffic flow based on such factors as speed, travel time, delay,
and freedom to maneuver. Six levels are defined from LOS A, as the best operating conditions, to
LOS F, or the worst operating conditions. LOS E represents “at-capacity” operations. When
volumes exceed capacity, stop-and-go conditions result, and operations are designated as LOS F.
Level of Service Calculation Method. The level of service calculation methodology for
intersections is dependent on the type of traffic control device, traffic signals or stop signs. The
level of service methodology used in this analysis bases a signalized intersection’s operation on the
average control delay calculated using methods described in Chapter 16 of the 2000 Highway
Capacity Manual (Transportation Research Board, 2000). The average delay for signalized
intersections was calculated using Synchro analysis software and is correlated to a LOS designation
as shown in Table 4. The level of service standard (i.e., minimum acceptable operations) for the
City of Palo Alto is LOS D.
Gunn High School Master Plan . 209002
Figure 11
AM and PM Peak Hour Intersection Volumes
and Parking Count Summaries
SOURCE: Wilson (2009). Merci. LL
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TABLE 4
SIGNALIZED INTERSECTION LEVEL OF SERVICE DEFINITIONS
Level of
Service
Average Control Delay
Per Vehicle
(Seconds) Description
A ≤ 10.0 Operations with very low delay occurring with favorable progression
and/or short cycle length.
B 10.1 to 20.0 Operations with low delay occurring with good progression and/or
short cycle lengths.
C 20.1 to 35.0 Operations with average delays resulting from fair progression and/or
longer cycle lengths. Individual cycle failures begin to appear.
D 35.1 to 55.0
Operations with longer delays due to a combination of unfavorable
progression, long cycle lengths, and high V/C ratios. Many vehicles
stop and individual cycle failures are noticeable.
E 55.1 to 80.0
Operations with high delay values indicating poor progression, long
cycle lengths, and high V/C ratios. Individual cycle failures are
frequent occurrences.
F > 80.0 Operations with delays unacceptable to most drivers occurring due to
over-saturation, poor progression, or very long cycle lengths.
SOURCE: Transportation Research Board, 2000 Highway Capacity Manual.
Existing Intersection Levels of Service. The existing lane configurations, signal phasing, and
peak-hour turning movement volumes were used to calculate the level of service for the study
intersections. The results of the level of service analysis are presented in Table 5. Two of the
study intersections are currently operating at acceptable LOS D: Arastradero Road intersections
with Foothill Expressway and at Donald Road under a.m. peak hour conditions. The intersections
of Arastradero Road at Miranda Avenue and the Gunn High School Driveway, however, are
operating at unacceptable LOS F under existing conditions.
TABLE 5
EXISTING INTERSECTION AM PEAK-HOUR LEVELS OF SERVICE (LOS)
ANDAVERAGE VEHICLE DELAY (seconds/vehicle)a
Existing
Intersection Delay LOS
Arastradero Road and Foothill Expressway 42.7 D
Arastradero Road and Miranda Avenue >120 F
Arastradero Road and School Driveway >120 F
Arastradero Road and Donald/Terman Road 42.4 D
a LOS calculations performed for using SYNCHRO and the 2000 Highway Capacity Manual operations
analysis methodology.
SOURCE: Wilson (2009).
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Pedestrian and Bicycle Facilities
Pedestrian facilities include sidewalks, crosswalks, and pedestrian signals. The existing school
site currently contains pedestrian facilities. School route crosswalks exist on Arastradero Road at
its intersections with Miranda Avenue, the Gunn High School Driveway, and Donald Drive.
There is a crosswalk with a pedestrian signal phase across the driveway and across Arastradero
Road on the west side. The pedestrian phase across the driveway runs concurrent with the
westbound through and right-turn vehicle movements on Arastradero Road. This puts all
pedestrian traffic across the driveway at conflict with inbound right-turns in the morning
commute period. Similarly pedestrian and bicycle traffic crossing Arastradero Road using the
eastbound crosswalk is in conflict with vehicles making right-turns out of the driveway.
Bicycle facilities include bike paths, bike lanes, and bike routes. Bike paths are paved trails that
are separated from the roadways. Bike lanes are lanes on roadways that are designated for use by
bicycles by striping, pavement legends, and signs. Bike routes are roadways that are designated
for bicycle use with signs, but no separate lane width. Within the vicinity of the project site, there
are bike lanes on Miranda Avenue and Arastradero Road. Bike paths are present along the
property boundary with the Veterans Hospital and between Los Altos Road and Arastradero
Road.
Bicycle counts were conducted at the start and end of the school day on a Monday in March
(March 16, 2009). The counts included both inbound and outbound bicycles by location, as well
as count of parked bicycles by location.17
Bicycle counts, illustrated in Figure 12, reveal that approximately 400 students bicycle to school.
Approximately 73 percent (285 students) entered from the rear of the school property at Los
Robales/Gerogia/McGregor. At the main entrance, 11 percent (44 students) approached from the
east on Arastradero Road and 6 percent (23 students) approached from the west. The remaining
10 percent (37 students) entered from Miranda Road or the bike trail on the western edge of the
campus. Outbound bicycle traffic in the afternoon is much less focused in that departures occur
over a much longer period as student leave the campus over a more extended period. Directions
are generally reversed from morning arrivals.
By comparison, counts conducted by the Parent Teacher Association (PTA) on a warmer day,
have documented upwards of 600 students bicycling to school, roughly 50 percent more than was
counted in March.
Bike cages are generally located at three points in the central area of the campus, including near
the library, near the science building, and near the student center.
17 It should be noted that both vehicle and bicycle counts represent a worst-case scenario as the weather was cold in
March. Mode-shift would occur as weather improves (i.e., more bicycling and walking would occur on a warm
day).
Gunn High School Master Plan . 209002
Figure 12
Bicycles and AM/PM Peak Period
Pickup/Dropoff Volumes
SOURCE: Wilson (2009)
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Initial Study September 2009
Transit Facilities
Bus service in Santa Clara County is operated by the Santa Clara Valley Transportation Authority
(VTA). Route 88 is a local bus route that provides service between the Palo Alto Veterans
Hospital and Colorado/Middlefield Roads. It operates with additional service when school is in
service to accommodate students. Route 88 stop is directly in front of Gunn High School on
Arastradero Road.
In addition, the PAUSD makes unused seats on its Bus Routes J, Y, and Z buses available to high
school students for a fee.
Discussion
a, b) Less than Significant with Mitigation. Implementation of the proposed project over
buildout of the Master Plan in 2017 and associated incremental increase in student
population at the project site would increase trips to the high school. The vehicle trip
generation for the proposed project is presented in Table 6. Vehicle trip generation for the
proposed improvements was estimated based on trip generation rates published in the
Institute of Transportation Engineers Trip Generation (8th edition). The proposed high
school expansion is estimated to generate approximately 82 net new morning vehicle trips
(57 inbound and 25 outbound) at the school driveway.
TABLE 6
AM PEAK HOUR TRIP FORECAST
Existing Student
Population
Forecast 2018 Student
Population Net Increase in Tripsa
Net Inbound/Outbound
Trips
1,948 2,259 82 57/25
a Trip generation was based on the trip generation rates published in ITE Trip Generation, 8th edition.
SOURCE: Wilson (2009), ITE (2008)
The vehicle trip distribution pattern for the proposed project was estimated based on the
existing travel patterns of students and faculty from the traffic counts conducted in March
2009.
Project Conditions
Project conditions are defined as existing conditions plus traffic added by the proposed
project. Project impacts are then identified by comparing the LOS results under project
conditions to those under existing conditions.
The results of the LOS analysis for project conditions are summarized in Table 7; turning
movement counts and LOS calculations are presented on-file at the District. With the
addition of project-generated traffic, the study intersections would continue to operate at
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Initial Study September 2009
TABLE 7
EXISTING AND PROJECT LEVELS OF SERVICE (LOS)a
Intersection
Existing Project
Delay LOS Delay LOS
AM Peak Hour
Arastradero Road and Foothill Expressway 42.7 D 42.7 D
Arastradero Road and Miranda Avenue >120 F >120 F
Arastradero Road and School Driveway >120 F >120 F
Arastradero Road and Donald/Terman Road 42.4 D 44.2 D
a LOS calculations performed for using SYNCHRO and the 2000 Highway Capacity Manual operations analysis
methodology.
SOURCE: Wilson (2009)
the same acceptable levels of service during the a.m. peak hour as they do under existing
conditions. Two of the study intersections are currently operating at acceptable LOS D:
Arastradero Road intersections with Foothill Expressway and at Donald Road under a.m.
peak hour conditions. The intersections of Arastradero Road at Miranda Avenue and the
Gunn High School Driveway, however, are operating at unacceptable LOS F under existing
conditions. Under Existing Plus Project Conditions, the delay would increase at the study
intersections, and the project would contribute to these unacceptable levels during the a.m.
peak hour.
Cumulative Conditions
The Arastradero Road corridor is effectively at capacity now and further increases in
demand would expand the peak in terms of length of time but not peak volumes. The
Arastradero Road corridor is at capacity and traffic is metered into and out of it at both
ends (El Camino Real and Foothill Expressway) during the morning and evening commute
periods. Under Cumulative Conditions, the delay would increase at the study intersections,
and the project would contribute to these unacceptable levels during the a.m. peak hour.
Implementation of Mitigation Measures TRAN-1 and TRAN-2 would reduce the
project’s contribution to vehicle delays on Arastradero Road by moving students to
alternative modes of transportation by including additional measures in their
comprehensive Traffic Demand Management (TDM) Program. The goal of the TDM
program is to not increase traffic volumes to the high school as the student body increases.
Mitigation Measure TRAN-1: PAUSD shall require Gunn High School to set up a
carpool matching program for students. The program should be well advertised at the
beginning of the school year and the service should remain available throughout the
school year. Ideally a match person/scheduler would be available at all time to react
to changing driver schedules (vacation, sickness etc.) as needed.
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Mitigation Measure TRAN-2: PAUSD shall require Gunn High School to continue
the existing TDM program. The TDM program shall include the following:
• No net increase in the number of onsite parking spaces relative to 2009 (461
parking spaces);
• No increase in student parking permits relative to 2009;
• Direct bicycle access via Georgia and Los Robles versus Arastradero Road to
remove bicycle traffic from the main driveway to improve existing intersection
level of service;
• Locate bicycle racks in convenient areas to facilitate ease of queues, safety, and
accessibility;
• Provide maps at the start of the school year illustrating preferred bicycle access
routes;
• Extend arrivals over a longer period of time by getting students to school
before the peak rush. Consider providing study areas or breakfast incentives or
similar to encourage student to arrive a little before school starts.
Construction Period
Construction of the proposed modifications to the school is anticipated to commence in
summer 2010, and would be conducted in phases. Construction activities that would
generate offsite traffic would include the initial delivery of construction vehicles and
equipment to the project site, the daily arrival and departure of construction workers, and
the delivery of materials throughout the construction period, and removal of construction
debris. Deliveries would include shipments of concrete, lumber, and other building
materials for onsite structures, utilities (e.g., irrigation and plumbing equipment, electrical
supplies) and paving and landscaping materials.
Construction-generated traffic would be temporary, and therefore, would not result in any
long-term degradation in operating conditions on any project roadways. The impact of
construction-related traffic would be a temporary and intermittent lessening of the
capacities of project area streets because of the slower movements and larger turning radii
of construction trucks compared to passenger vehicles. However, given the proximity of the
project site on and near major arterials (Arastradero Road, Foothill Expressway) and to El
Camino Real, construction trucks would have relatively easy and direct routes. Most
construction traffic would be dispersed throughout the day. Thus, the temporary increase
would not significantly disrupt daily traffic flow on any of the study area roadways.
Although the impact would be less than significant, truck traffic could have some adverse
effect on traffic flow in the study area. As such, the transport of construction materials and
equipment should be limited to off-peak traffic periods. This measure should be
incorporated by the school district into the contract specifications documents to ensure
implementation by the construction contractor(s).
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c) No Impact. The proposed school would not change air traffic patterns, increase air traffic
levels or result in a change in location that would result in substantial safety risks. There
would be no project effect.
d) Less than Significant with Mitigation. The project would result in an increase in vehicle
trips, as well as an increase in pedestrian traffic within the project site and on local
roadways, and correspondingly, would increase the potential for interaction between these
travel modes.
Sidewalks currently exist on roadways adjacent to the project site. To further improve
pedestrian circulation, pedestrian walkways would be enhanced from the sidewalk and all
passenger loading/unloading zones to the main entrance to the campus site.
Bicycle access to the high school would increase as student population increases. Assuming
the same rate of bicycle use as observed in the March 2009 counts, the projected number of
cyclists at buildout of the Master Plan would be approximately 485. The high school would
continue to encourage bicycling to campus as part of their Transportation Demand
Management program and further through Mitigation Measure TRAN-2, and thus would
provide adequate and secure bicycle parking, in the form of bicycle cages, at convenient
and commute entrances.
Circulation and parking aisles at the high school would continue to serve both one-way and
two-way traffic and provide both angled and perpendicular parking spaces. The aisles
would be designed to be wide enough for maneuvering all types of passenger vehicles.
Morning drop-offs observed approximately 365 vehicles dropping off students on campus.
Assuming the percentage of drop-offs remains constant as the enrollment increases, a
future student population is forecasted to result in approximately 450 drop-offs during the
morning commute period. A queue of approximately 1,100 feet (in two lanes) would be
required to accommodate the projected drop-offs.
Based on the residential distribution of existing students and transit routes, the school
would generate pedestrian traffic through the neighborhood and along roadways that front
the school property. The existing sidewalks on all street frontages would accommodate the
pedestrian traffic.
Implementation of Mitigation Measures TRAN-3 and TRAN-4 would reduce onsite
circulation impacts to less-than-significant levels.
Mitigation Measure TRAN-3: PAUSD shall incorporate the following measures
into the project site’s final internal circulation design:
• The drop-off lane shall be designed to accommodate queuing onsite during the
morning commute period without blocking driveways or the Arastradero Road
entrance;
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Initial Study September 2009
• Internal driveway approaches shall be painted red to prohibit stopping and
maintain sight-distance;
• Internal roadway curbs shall be painted red to prohibit stopping;
• Internal circulation would use a curbside drop-off zone, which shall be painted
white and striped with a lane to allow vehicles to pass on the left-side of
loading/unloading vehicles;
• The loading zone shall be marked with signs/pavement markings that make
vehicles aware of pedestrian and loading activities;
• Signs and pavement markings (i.e., painted arrows) shall designate directional
flow through the parking lot.
Mitigation Measure TRAN-4: PAUSD shall integrate the following measures to
reduce potential queuing impacts:
• Circulate informational flyers to parents and students that discuss onsite
circulation patterns and designated parking areas;
• Encourage drivers with disabled passengers that would require longer dwell
times (i.e., wheelchair users) to use ADA parking spaces for loading/unload;
• Use staff to monitor and direct onsite traffic during peak drop-off/pick-up times
both before and after school (i.e. 7:45 a.m. to 8:00 a.m.).
With implementation of the above mitigation measures, there would be no apparent
circulation design features that would create a traffic safety hazard or significantly increase
the potential for conflicts between vehicles, pedestrians and bicycles.
e) Less than Significant. The proposed Master Plan would not alter the ingress, egress to the
high school. The driveway as designed in the site plan would provide adequate emergency
access. There would be no blockage of access or traffic pattern disturbance that would
significantly affect emergency access. Red curb will be used along interior roadways and
driveways to provide sufficient response time for emergency vehicles. The fire lane must
be a minimum of 18 feet in width and must be kept clear at all times. The project’s effect
would be less than significant.
f) Less than Significant with Mitigation. The City of Palo Alto requires one parking space
for every five students, plus one space for each four teaching stations. The proposed daily
population for the high school is approximately 2,300 students and 92 teachers (1 for every
25 students), thus requiring 483 parking spaces. Using the current parking demand of
approximately 440 spaces on a typical weekday, the future demand rate with buildout of
the Master Plan would be approximately 533 spaces, however, with implementation of
Mitigation Measure TRAN-2, the future parking demand would be reduced through TDM
measures; therefore, the project’s effect would be less than significant.
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The high school has an existing parking demand management program which limits student
driving to campus though permits. The program is enforced through cooperation with the
City police, which uses parking enforcement (tickets) to ensure adherence to the program.
g) Less than Significant with Mitigation. The project is located in an established urban area,
and buildout of the Master Plan would not conflict with adopted policies, plans, or
programs supporting alternative transportation.
The increase in students and employees could increase the use of alternative transportation
modes. The high school has, and will continue to implement, a Transportation Demand
Management (TDM) program that shifts students to alternative modes of travel through
implementation of Mitigation Measure TRAN-2. Decreasing the volume of vehicular
traffic to the school through the promotion of alternative modes of travel, including
carpooling, biking, or use of public transit, is fundamental to any TDM program. The
project’s effect would be less than significant with mitigation.
Sources
Institute of Transportation Engineers Trip Generation (8th edition), 2008.
Santa Clara Valley Transportation Authority (VTA), Transit and Rail Map,
http://www.vta.org/schedules/pdf/bus_rail_map_a.pdf. Accessed August 18, 2009.
Santa Clara Valley Transportation Authority (VTA), Bike Map,
http://www.vta.org/schedules/pdf/vta_bike_map_a.pdf. Accessed August 18, 2009.
Transportation Research Board, Highway Capacity Manual, 2000.
Wilson Engineering. On-Site Traffic Study for Gunn High School. Prepared for the Palo Alto
Unified School District. May 2009.
Wilson Engineering. An Assessment of Gunn and Play High Schools Trip Generation, Traffic
Assignment and LOS Assessment Associated with Measure B. Prepared for the Palo Alto
Unified School District. August 7, 2009.
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Gunn High School Master Plan 87 ESA / 209002
Initial Study September 2009
Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
16. Utilities and Service Systems
Would the project:
a) Exceed wastewater treatment requirements of the
applicable Regional Water Quality Control Board?
b) Require or result in the construction of new water or
wastewater treatment facilities or expansion of
existing facilities, the construction of which could
cause significant environmental effects?
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?
d) Have sufficient water supplies available to serve the
project from existing entitlements and resources, or
are new or expanded entitlements needed?
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 project’s projected
demand in addition to the provider’s existing
commitments?
f) Be served by a landfill with sufficient permitted
capacity to accommodate the project’s solid waste
disposal needs?
g) Comply with federal, state, and local statutes and
regulations related to solid waste?
Setting
Water supply to the City of Palo Alto is provided by the City Utilities Department through
purchases from the San Francisco Public Utilities Commission’s Hetch Hetchy water supply
system. On average, 85 percent of this water is derived from snow melt flowing into the Hetch
Hetchy Reservoir in Yosemite National Park, and the balance is from runoff stored in San
Francisco Bay Area reservoirs on the Peninsula and in the East Bay. There are five wells in Palo
Alto that are maintained as an emergency source of supply. Palo Alto also uses recycled water
from the Regional Water Quality Control Plant (RWQCP) to irrigate the municipal golf course,
Greer Park, and landscaping around the RWQCP.
The City owns and operates an approximate 200-mile wastewater collection system and operates
the Regional Water Quality Control Plant (RWQCP). The RWQCP also serves Mountain View,
Los Altos, Los Altos Hills, East Palo Alto, and Stanford University. Approximately 26 million
gallons of wastewater are processed on a daily basis at the RWQCP and 9.5 billion gallons
annually (3.3 billion gallons from Palo Alto).
The City also provides weekly waste, yard waste and recycling collection service to all homes
and businesses in the City. Yard waste is currently composted at the Palo Alto Landfill. Waste
collected at the curbside goes to the Sunnyvale Materials Recovery and Transfer Station or to
another facility for additional sorting. The processed waste is ultimately placed in a landfill at the
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Initial Study September 2009
Kirby Canyon Landfill in San Jose. The Palo Alto Landfill, which is scheduled to close in 2011,
currently accepts waste from self-haul and City vehicles. The City is required by State law to
divert 50 percent of its waste stream from landfills. In 2006, the City diverted 62 percent of its
waste stream.
Discussion
a, e) Less than Significant. Minimal growth in student and staff populations would occur over
the duration of the Master Plan. As discussed in the Project Description, the proposed
Master Plan identifies an increase in the student enrollment at the high school through
2017. The student capacity over the eight-year period of the Master Plan would increase by
approximately 350 students, or about 44 students per year. This increase would not result in
substantial increases in wastewater generation over existing conditions at the project site
such that the wastewater treatment requirements would be exceeded.
Furthermore, the City of Palo Alto’s General Plan EIR found that overall population
growth that would occur in the City (of which future PAUSD students and staff would be a
part) would not create significant amounts of wastewater that would exceed the RWQCP
treatment capacity or require expansion of the treatment plant. Therefore, the proposed
project would result in a less than significant impact regarding wastewater treatment
requirements.
b, d) Less than Significant. The proposed project would result in the development of a
combined maximum total of approximately 124,000-square feet of new educational uses on
the project site. These new uses (e.g., new classrooms, gymnasium, labs, etc.), and the
minor increases in student and staff population they would accommodate over the Master
Plan’s eight-year planning period would incrementally increase local water demand and
wastewater generation at the project site, as discussed above.
As noted in the General Plan EIR, the City would have access to adequate water supplies
and wastewater treatment capacity to serve anticipated population growth. Therefore, the
proposed project would not require new or expanded water or wastewater facilities and
effects to water treatment facilities would be less than significant.
c) Less than Significant. New buildings and other structures proposed under the Master Plan
would require connection to the existing on-site stormwater drainage system. Stormwater
runoff from the project site would be routed to the municipal stormwater collection system.
As discussed in Section 8, Hydrology and Water Quality, and as required by Mitigation
Measure HYD-1, the PAUSD would be required to develop a Storm Water Pollution
Prevention Plan that would identify Best Management Practices to ensure that construction
of new on-site stormwater infrastructure would not result in adverse impacts to water
quality.
f, g) Less than Significant. Gunn High School student and staff population growth would be
relatively stable over the eight-year Master Plan horizon. The Kirby Canyon Landfill has
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Initial Study September 2009
adequate capacity until 2022, and as such, the General Plan’s regional growth, including
minor increases in local student and staff populations at the project site, would not
adversely affect capacity at the Kirby Canyon Landfill; therefore, impacts to solid waste
would be less than significant.
Additionally, in conformance with Mitigation Measure HAZ-1, the proposed project would
not affect compliance with solid waste statutes and regulations.
Sources
California Integrated Waste Management Board (CIWMB), Active Landfills Profile for Kirby
Canyon Recycling and Disposal Facility, www.ciwmb.ca.gov/profiles/facility/landfill,
accessed July 23, 2009.
CIWMB, Jurisdiction Profile for City of Palo Alto, www.ciwmb.ca.gov/profiles/Juris, accessed
July 23, 2009.
City of Palo Alto, All About Your Utilities: Palo Alto’s Homegrown Asset, April 10, 2007.
City of Palo Alto, Comprehensive Plan Update, 1996.
City of Palo Alto, Draft and Final Environmental Impact Report, Comprehensive Plan Update,
1996.
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Initial Study September 2009
Issues (and Supporting Information Sources):
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporation
Less Than
Significant
Impact No Impact
17. Mandatory Findings of Significance
Would the project:
a) Does the project have the potential to 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?
b) Does the project have impacts that are individually limited, but cumulative considerable? (“Cumulative 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)?
c) Does the project have environmental effects which will cause substantial adverse effects on human beings, either directly or indirectly?
Discussion
a) Less than Significant. Based upon background research, site reconnaissance, and the
project description, the project does not have the potential to 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. Any potential short-term increases
in potential effects to the environment during construction are mitigated to a less than
significant level, as described throughout the Initial Study.
b) Less than Significant with Mitigation. In accordance with CEQA Guidelines Section
15183, the environmental analysis in this Initial Study was conducted to determine if there
were any project-specific effects that are peculiar to the project or its site. No project-
specific significant effects peculiar to the project or its site were identified that could not be
mitigated to a less than significant level. The proposed project would contribute to
environmental effects in the areas of biological resources (e.g., loss of trees), temporary
increases in construction-generated dust and noise, temporary increase in sedimentation
and water quality effects during construction, and operational traffic and circulation
impacts. Mitigation measures incorporated herein mitigate any potential contribution to
cumulative impacts associated with these environmental issues. Therefore, the proposed
project does not have impacts that are individually limited, but cumulatively considerable.
c) Less than Significant. The project may have significant adverse effects on human beings
in the areas of air quality, noise and traffic during construction, and with geologic/seismic
considerations with new development. Mitigation measures identified in the relevant
sections of this Initial Study would reduce the effects to a less than significant level.