ERC Packet 06-20-2019CITY OF CUPERTINO
AGENDA
ENVIRONMENTAL REVIEW COMMITTEE
9:30 AM
10300 Torre Avenue, City Hall Conference Room C
Thursday, June 20, 2019
ROLL CALL
APPROVAL OF MINUTES
Subject: Draft Minutes of December 13, 2018
Recommended Action: approve or modify the Draft Minutes of December 13, 2018
Draft Minutes of December 13, 2018
ORAL COMMUNICATIONS
This portion of the meeting is reserved for persons wishing to address the members on
any matter not on the agenda. Speakers are limited to three (3) minutes. In most cases,
State law will prohibit the members from making any decisions with respect to a matter
not listed on the agenda
WRITTEN COMMUNICATIONS
PUBLIC HEARINGS
OLD BUSINESS
NEW BUSINESS
Subject: Welcome new Committee members
Recommended Action: Welcome the new members and review the role and
responsibilities of the Committee
Chapter 2.84; Environmental Review Committee
Example - Initial Study and ERC approval
STAFF AND COMMITTEE REPORTS
ADJOURNMENT
Page 1
June 20, 2019Environmental Review Committee AGENDA
In compliance with the Americans with Disabilities Act (ADA), anyone who is planning
to attend the next meeting who is visually or hearing impaired or has any disability
that needs special assistance should call the City Clerk's Office at 408-777-3223, 48
hours in advance of the meeting to arrange for assistance. Upon request, in advance,
by a person with a disability, meeting agendas and writings distributed for the meeting
that are public records will be made available in the appropriate alternative format.
Also upon request, in advance, an assistive listening device can be made available for
use during the meeting.
Any writings or documents provided to a majority of the members after publication of
the agenda will be made available for public inspection. Please contact the City
Clerk’s Office in City Hall located at 10300 Torre Avenue during normal business
hours.
IMPORTANT NOTICE: Please be advised that pursuant to Cupertino Municipal
Code 2.08.100 written communications sent to the Cupertino City Council,
Commissioners or City staff concerning a matter on the agenda are included as
supplemental material to the agendized item. These written communications are
accessible to the public through the City’s website and kept in packet archives. You are
hereby admonished not to include any personal or private information in written
communications to the City that you do not wish to make public; doing so shall
constitute a waiver of any privacy rights you may have on the information provided to
the City.
Members of the public are entitled to address the members concerning any item that is
described in the notice or agenda for this meeting, before or during consideration of
that item. If you wish to address the members on any other item not on the agenda, you
may do so during the public comment.
Page 2
Community Development Department
Cupertino, CA 95014
(408) 777-3308
DRAFT MINUTES OF THE SPECIAL MEETING OF THE ENVIRONMENTAL
REVIEW COMMITTEE HELD ON December 13, 2018
Committee Members:Geoff Paulsen
Aarti Shrivastava
Steven Scharf
Timm Borden
Amy Chan
Committee Members absent:Darcy Paul
Staff present:Erick Serrano, Associate Planner
David Stillman, Transportation Manager
Chad Mosley, Civil Engineer
Consultant Presenters:Michael Strahs, Kimco Realty
Terri McCracken,Placeworks (Initial Study)
Jessica Setiawan, Placeworks (Initial Study)
APPROVAL OF MINUTES:
August 31, 2018
The minutes of the August 31, 2018 meeting were approved as written
ORAL COMMUNICATIONS
(Reserved for persons wishing to address the Committee on issues that are not already
included in the regular Order of Business)
None
PUBLIC HEARING:
1.Application No.(s):EA-2017-06, GPA-2017-05, DP-2018-04, DA-2017-01, ASA-2017-09,
TR-2017-46
Applicant(s):Michael Strahs (Kimco Realty)
Location: 10801 N Wolfe Rd APN # 316-45-017
The project Applicant is proposing the Cupertino Village Hotel Project which would construct a
boutique hotel on a 1.72-acre site in the Cupertino Village Shopping Center. The project would
also involve demolition of two existing commercial buildings on the sites. The development
would be a new 5-story, 185-room boutique hotel including event meeting rooms, a restaurant,
and rooftop lounge and bar. A Mitigated Negative Declaration is proposed.
Geologic/Soils
o Standard construction techniques for earthquake zones are incorporated in the
construction calculations
Hydrology
o The Initial Study indicated that there is less than a significant impact on the exiting
sewer system, however, a mitigation measure has been drafted which be implemented
should the hotel’s operation exceed the contractual limit
Trees/Landscaping
o 68 trees are on site
o City trees along Wolfe Road will not be removed
Air Quality/Traffic
o Mitigation measures will be employed during construction for dust control
o One driveway will be closed but the trip count shift to other driveways is minimal
o A shuttle service program, joint with other local businesses, will be explored in the
future
o Both of the parking garages on the site are available to hotel guests and retail shoppers
creating more parking spaces than are required by the Ordinance
Archeological/Cultural/Biological
o There will be a Stop Work Order in the construction documents should any remains
or artifacts be discovered on site.
o A tribal resource specific mitigation has been incorporated into the Iinitial Study
o No known habitats have been identified, however, should construction fall during
nesting season, all measures will be taken to ensure the safety of the nests
Noise
o Construction Best Management Practices will be employed to reduce construction
noise to the surrounding businesses and neighbors
Additional Discussion
o Valet parking service will be offered to customers to the shopping center during
construction
o The hotel location on the site hopefully will encourage more pedestrian traffic than
car traffic by hotel guests
ACTION: Recommendation for approval of a Mitigated Negative Declaration for EA-2017-06
MOTION: Paulsen
SECOND: Scharf
NOES: none
VOTE: 5-0-0
OLD BUSINESS
None
NEW BUSINESS
None
ADJOURNMENT
Respectfully submitted,
/s/Beth Ebben
Beth Ebben
Deputy Board Clerk
CITY OF CUPERTINO
COMMUNITY DEVELOPMENT DEPARTMENT
Alcalde Road Lot Split Project
INITIAL STUDY/MITIGATED NEGATIVE
DECLARATION
January 2018
1501 Sports Drive, Suite A, Sacramento CA 95834
Office 916.372.6100 Fax 916.419.610
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
i January 2018
TABLE OF CONTENTS
A. BACKGROUND ............................................................................................................................ 1
B. SOURCES ....................................................................................................................................... 2
C. ENVIRONMENTAL FACTORS POTENTIALLY AFFECTED ............................................. 3
D. DETERMINATION ...................................................................................................................... 4
E. BACKGROUND AND INTRODUCTION .................................................................................. 5
F. PROJECT DESCRIPTION .......................................................................................................... 5
G. ENVIRONMENTAL CHECKLIST .......................................................................................... 11
I. AESTHETICS........................................................................................................12
II. AGRICULTURE AND FOREST RESOURCES. .................................................14
III. AIR QUALITY. .....................................................................................................16
IV. BIOLOGICAL RESOURCES. ..............................................................................24
V. CULTURAL RESOURCES. .................................................................................27
VI. GEOLOGY AND SOILS. .....................................................................................30
VII. GREENHOUSE GAS EMISSIONS. .....................................................................33
VIII. HAZARDS AND HAZARDOUS MATERIALS. ...............................................36
IX. HYDROLOGY AND WATER QUALITY. ..........................................................42
X. LAND USE AND PLANNING. ............................................................................46
XI. MINERAL RESOURCES. ....................................................................................47
XII. NOISE. ...................................................................................................................48
XIII. POPULATION AND HOUSING. .........................................................................51
XIV. PUBLIC SERVICES. ............................................................................................52
XV. RECREATION. .....................................................................................................54
XVI. TRANSPORTATION AND CIRCULATION. .....................................................55
XVII. TRIBAL CULTURAL RESOURCES. ..................................................................58
XVIII. UTILITIES AND SERVICE SYSTEMS. .............................................................59
XIX. MANDATORY FINDINGS OF SIGNIFICANCE. .............................................62
Appendix
Air Quality and GHG Modeling Results
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
1 January 2018
INITIAL STUDY
January 2018
A. BACKGROUND
1. Project Title: Alcalde Road Lot Split Project
2. Lead Agency Name and Address: City of Cupertino
Community Development Department
10300 Torre Avenue
Cupertino, CA 95014-3255
3. Contact Person and Phone Number: Gian Paolo Martire
Associate Planner
(408) 777-3319
4. Project Location: 22561 Alcalde Road
Cupertino, CA 95014
5. Project Sponsor’s Name and Address: Cindy Hsu
Greenleaf Group LLC
10229 Scenic Boulevard
Cupertino, CA 95014
6. General Plan Designation: Low/Medium Density (5-10 du/ac.)
7. Zoning Designation: Single-Family Residential (R1-7.5)]
8. Project Description Summary:
The Alcalde Road Lot Split Project is located at 22561 Alcalde Road in the City of
Cupertino, California. The proposed project site is bordered by Alcalde Road to the south,
and by existing one- and two-story, single-family residential development to the north,
east, and west. Additional single-family homes are located south of the site across Alcalde
Road. The project would include demolition of a small number of existing on-site
structures and subdivision of the 19,562-square-foot property into two approximately
8,892-square-foot lots. The site would be redeveloped with two single-family two-story
residences. In addition, the proposed project would include widening of the Alcalde Road
right-of-way along the project frontage.
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
2 January 2018
B. SOURCES
The following documents are referenced information sources used for purposes of this Initial
Study/Mitigated Negative Declaration:
1. Bay Area Air Quality Management District. Plans & Climate. Available at:
http://www.baaqmd.gov/plans-and-climate. Accessed September 2017.
2. Bay Area Air Quality Management District. Air Quality Standards and Attainment Status.
Available at: http://www.baaqmd.gov/research-and-data/air-quality-standards-and-
attainment-status. Accessed November 2017.
3. Bay Area Air Quality Management District. CalEEMod Air Quality and Greenhouse Gas
Emissions Estimates for the Proposed Alcalde Road Lot Split Project, Cupertino,
California. January 2018.
4. Bay Area Air Quality Management District. California Environmental Quality Act, Air
Quality Guidelines. May 2017.
5. California Air Pollution Control Officer’s Association (CAPCOA). California Emissions
Estimator Model, User’s Guide, Version 2016.3.2. November 2017.
6. California Department of Conservation. Santa Clara County Important Farmland Map
2014. Published October 2016.
7. California Department of Conservation. Special Studies Zones, Cupertino Quadrangle.
Effective July 1, 1974.
8. California Department of Forestry and Fire Protection. Santa Clara County, Very High
Fire Hazard Severity Zones in LRA. October 8, 2008.
9. California Department of Toxic Substances Control. Hazardous Waste and Substances Site
List. Available at: http://www.dtsc.ca.gov/SiteCleanup/Cortese_List.cfm. Accessed March
2017.
10. California Department of Transportation. California Scenic Highway Mapping System.
Available at:
http://www.dot.ca.gov/hq/LandArch/16_livability/scenic_highways/index.htm. Accessed
March 2017.
11. California Department of Transportation. Transportation and Construction Vibration,
Guidance Manual. September 2013.
12. California Environmental Protection Agency, California Air Resources Board. Air Quality
and Land Use Handbook: A Community Health Perspective. April 2005.
13. City of Cupertino. Emergency Operations Plan. September 2005.
14. City of Cupertino. General Plan Amendment, Housing Element Update, and Associated
Rezoning Draft EIR. June 18, 2014.
15. City of Cupertino. General Plan: Community Vision 2015 – 2040. Adopted October 20,
2015.
16. Institute of Transportation Engineers. Trip Generation Handbook, 9th Edition. September
2012.
17. PIERS Environmental Services. Addendum to Report of Subsurface Investigation and
Transmittal of Additional Results, 22561 Alcalde Road, Cupertino, California. January 8,
2018.
18. PIERS Environmental Services. Phase I Environmental Site Assessment, 22561 Alcalde
Road, Cupertino, California 95014. July 17, 2017.
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
3 January 2018
19. PIERS Environmental Services. Report of Limited Phase II Subsurface Investigation,
22561 Alcalde Road, Cupertino, California 95014. August 19, 2017.
C. ENVIRONMENTAL FACTORS POTENTIALLY AFFECTED
The environmental factors checked below would be potentially affected by this project, involving
at least one impact that is “Less than Significant with Mitigation Incorporated” as indicated by the
checklist on the following pages.
Aesthetics Agriculture and Forest
Resources
Air Quality
Biological Resources Cultural Resources Geology and Soils
Greenhouse Gas Emissions Hazards and Hazardous
Materials
Hydrology and Water Quality
Land Use and Planning Mineral Resources Noise
Population and Housing Public Services Recreation
Transportation and Circulation Tribal Cultural
Resources
Utilities and Service Systems
Mandatory Findings of
Significance
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
4 January 2018
D. DETERMINATION
On the basis of this initial study:
I find that the Proposed Project COULD NOT have a significant effect on the environment,
and a NEGATIVE DECLARATION will be prepared.
I find that although the Proposed Project could have a significant effect on the environment,
there will not be a significant effect in this case because revisions in the project have been
made by or agreed to by the applicant. A MITIGATED NEGATIVE DECLARATION will
be prepared.
I find that the Proposed Project MAY have a significant effect on the environment, and an
ENVIRONMENTAL IMPACT REPORT is required.
I find that the proposed project MAY have a “potentially significant impact” or “potentially
significant unless mitigated” on the environment, but at least one effect 1) has been
adequately analyzed in an earlier document pursuant to applicable legal standards, and 2)
has been addressed by mitigation measures based on the earlier analysis as described on
attached sheets. An ENVIRONMENTAL IMPACT REPORT is required, but it must
analyze only the effects that remain to be addressed.
I find that although the proposed project could have a significant effect on the environment,
because all potentially significant effects (a) have been analyzed adequately in an earlier
EIR pursuant to applicable standards, and (b) have been avoided or mitigated pursuant to
that earlier EIR, including revisions or mitigation measures that are imposed upon the
proposed project, nothing further is required.
Signature Date
Gian Paolo Martire, Associate Planner City of Cupertino
Printed Name For
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
5 January 2018
E. BACKGROUND AND INTRODUCTION
This Initial Study identifies and analyzes the potential environmental impacts of the Alcalde Road
Lot Split Project (proposed project). The information and analysis presented in this document is
organized in accordance with the order of the California Environmental Quality Act (CEQA)
checklist in Appendix G of the CEQA Guidelines. Where the analysis provided in this document
identifies potentially significant environmental effects of the project, mitigation measures are
prescribed.
The mitigation measures prescribed for environmental effects described in this Initial
Study/Mitigated Negative Declaration (IS/MND) would be implemented in conjunction with the
project, as required by CEQA. The mitigation measures would be incorporated into the project
through project conditions of approval. The City would adopt findings and a Mitigation
Monitoring/Reporting Program for the project in conjunction with approval of the project.
On October 20, 2015, the City of Cupertino adopted an amended General Plan 1 and an associated
Environmental Impact Report (EIR).2 The General Plan EIR is a program EIR, prepared pursuant
to Section 15168 of the CEQA Guidelines (Title 14, California Code of Regulations, Sections
15000 et seq.). The General Plan EIR analyzed full implementation of the General Plan and
identified measures to mitigate the significant adverse impacts associated with buildout of the
General Plan. The proposed project would be consistent with the General Plan; therefore, in
accordance with Section 15150 of the CEQA Guidelines (Section 21083.3 of the Public Resources
Code), this IS/MND will tier from the previously certified EIR (SCH# 2014032007) prepared for
the City’s General Plan where appropriate.
F. PROJECT DESCRIPTION
The following provides a description of the project site’s current location and setting, as well as
the proposed project components and the discretionary actions required for the project.
Project Location and Setting
The proposed project site consists of an approximately 19,562-square-foot (0.45-acre) property
located at 22561 Alcalde Road in the City of Cupertino, California (see Figure 1). The site is
identified by Assessor’s Parcel Number (APN) 341-29-063 and is zoned Single-Family Residential
with a minimum lot size of 7,500 (R1-7.5). The City’s General Plan designates the site as
Low/Medium Density (5-10 du/ac). The proposed project site is bordered by Alcalde Road to the
south, and by existing one- and two-story, single-family residential development to the north, east,
and west (see Figure 2). Additional single-family homes are located south of the site across Alcalde
Road. The nearest major roadway, South Foothill Boulevard, is located approximately 165 feet
east of the site.
1 City of Cupertino. General Plan: Community Vision 2015 – 2040. Adopted October 20, 2015.
2 City of Cupertino. General Plan Amendment, Housing Element Update, and Associated Rezoning Draft EIR. June
18, 2014.
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
6 January 2018
Figure 1
Regional Location
N
Project Location
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
7 January 2018
Figure 2
Project Vicinity Map
Project Site
N
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
8
January 2018
The proposed project site currently contains a residence (approximately 2,520 square feet). Access
to the residence is provided by a concrete driveway from Alcalde Road. A 180-square-foot shed
and a concrete patio are also present on the site. Vegetation on the site consists primarily of
landscaping associated with the residence, including some grass and shrubs, as well as nine trees.
Aquatic or riparian habitat on or in the vicinity of the site does not exist. Currently sidewalks do
not exist along the frontage of the project site. Existing sidewalks along Alcalde Road are
discontinuous in the vicinity of the project site, particularly towards the west of the site; however,
portions of the existing sidewalks along Alcalde Road connect to other nearby roadways including
Santa Lucia Road and Lockwood Drive to the west of the project site, and South Foothill
Boulevard to the east.
Project Components
The proposed project would include demolition of the existing on-site residence and associated
structures, removal of seven of the on-site trees, subdivision of the 19,562-square-foot lot into two
approximately 8,892-square-foot lots, and redevelopment of the site with two single-family two-
story residences (see Figure 3). In addition, the proposed project would include widening of the
Alcalde Road right-of-way by ten feet at the widest point (an approximately 370-square-foot area)
along the project frontage, which would be dedicated to the City. The project would be consistent
with the existing zoning and General Plan land use designations for the site.
Both of the proposed single-family residences would be two stories. As shown in Figure 4, the
proposed single-family residences would include attached garages, and front and rear porch areas.
Sewer and water service for the proposed residences would be provided by the City by way of
connections to existing sanitary sewer and water supply lines located in Alcalde Road. New paved
driveways would connect the garages of the two residences to the widened roadway.
On-site runoff would be captured by a new series of downspouts on the eastern and western sides
of both of the proposed residences (see Figure 4). Runoff from the downspouts would enter a six-
inch perforated pipe continuing into a bubbler drain system that would collect and route the water
onto vegetated areas within the front yards of the proposed residences.
Discretionary Action
Implementation of the proposed project would require City approval of a Tentative Parcel Map to
subdivide the proposed project site into two approximately 8,892-square-foot lots.
.
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
9
January 2018
Figure 3
Conceptual Site Plan
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
10
January 2018
Figure 4
Conceptual Grading and Drainage Plan
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
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January 2018
G. ENVIRONMENTAL CHECKLIST
The following Checklist contains the environmental checklist form presented in Appendix G of
the CEQA Guidelines. The checklist form is used to describe the impacts of the proposed project.
A discussion follows each environmental issue identified in the checklist. Included in each
discussion are project-specific mitigation measures recommended, as appropriate, as part of the
proposed project.
For this checklist, the following designations are used:
Potentially Significant Impact: An impact that could be significant, and for which no mitigation
has been identified. If any potentially significant impacts are identified, an EIR must be prepared.
Less Than Significant with Mitigation Incorporated: An impact that requires mitigation to
reduce the impact to a less-than-significant level.
Less-Than-Significant Impact: Any impact that would not be considered significant under
CEQA relative to existing standards.
No Impact: The project would not have any impact
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
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January 2018
I. AESTHETICS.
Would the project:
Potentially
Significant
Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-Than-
Significant
Impact
No
Impact
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. Examples of typical scenic vistas would include mountain ranges, ridgelines, or bodies of
water as viewed from a highway, public space, or other area designated for the express
purpose of viewing and sightseeing. In general, a project’s impact to a scenic vista would
occur if development of the project would substantially change or remove a scenic vista.
Given that the proposed project site is currently developed and is located in a residential
neighborhood, redevelopment of the site with two single-family two-story homes would
not obstruct views of a scenic vista. Furthermore, according to the California Scenic
Highway Mapping System, the proposed project site is located approximately 4.5 miles
north of the nearest State Scenic Highway, State Route (SR) 9, and approximately 1.2 miles
south of Interstate 280 (I-280), an Eligible State Scenic Highway.3 Neither SR 9 or I-280
are visible from the project site.
Based on the above discussion, the proposed project would not have a substantial adverse
effect on a scenic vista and would not substantially damage scenic resources, including,
but not limited to, trees, rock outcroppings, and historic buildings within a State Scenic
Highway. Thus, no impact would occur related to such.
c. Distinguishing between public and private views is important when evaluating changes to
visual character or quality, because private views are views seen from privately-owned
land and are typically associated with individual viewers, including views from private
residences. Public views are experienced by the collective public, and include views of
significant landscape features and along scenic roads. According to CEQA (Pub. Resources
Code, § 21000 et seq.) case law, only public views, not private views, are protected under
CEQA. For example, in Association for Protection etc. Values v. City of Ukiah (1991) 2
Cal.App.4th 720 [3 Cal. Rptr.2d 488], the court determined that “we must differentiate
between adverse impacts upon particular persons and adverse impacts upon the
environment of persons in general. As recognized by the court in Topanga Beach Renters
3 California Department of Transportation. California Scenic Highway Mapping System. Available at:
http://www.dot.ca.gov/hq/LandArch/16_livability/scenic_highways/index.htm. Accessed March 2017.
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
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January 2018
Assn. v. Department of General Services (1976) 58 Cal.App.3d 188 [129 Cal.Rptr. 739]:
‘[A]ll government activity has some direct or indirect adverse effect on some persons. The
issue is not whether [the project] will adversely affect particular persons but whether [the
project] will adversely affect the environment of persons in general.’” Therefore, the focus
in this section is on potential impacts to public views. Sensitive public viewers in the
surrounding area would primarily consist of motorists, pedestrians, and bicyclists travelling
on Alcalde Road.
Views of the proposed project site from Alcalde Road currently consist of the existing on-
site single-family residence, the existing on-site driveway, and various trees and shrubs
located on the southern portion of the site. The project site is bordered on the east and west
by two-story, single-family residences. The proposed project would include demolition of
the existing on-site structures, removal of a majority of the on-site vegetation, and
redevelopment of the site with two single-family two-story residences and new landscape
plantings. As discussed previously, Alcalde Road would be widened along the project
frontage. The proposed residences would be designed to be visually congruous with the
existing residences to the east and west of the project site.
Given that the site is already developed with a residential use, and the project would be
consistent with the surrounding single-family residential development, the project would
not substantially degrade the aesthetic character or quality of the site for motorists,
pedestrians, and bicyclists travelling along Alcalde Road. In addition, the project would be
consistent with the site’s existing zoning and General Plan land use designations. As such,
changes to aesthetic character and quality associated with buildout of the site have been
previously analyzed in the General Plan EIR. Therefore, impacts related to degrading the
existing visual character of the site and its surroundings would be less than significant.
d. The project site is currently developed with a residential structure, and, thus, the site
contains existing sources of light and glare associated with such, including, but not limited
to, headlights on cars using the on-site driveway, exterior light fixtures, and interior light
spilling through windows. In addition, the site is surrounded by existing residential
development that currently generates similar light and glare in the area. Therefore,
redevelopment of the site with two residential homes would not introduce new sources of
substantial light or glare to the site which would adversely affect day or nighttime views in
the area, and implementation of the proposed project would result in a less-than-significant
impact.
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
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January 2018
II. AGRICULTURE AND FOREST
RESOURCES.
Would the project:
Potentially
Significant
Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-Than-
Significant
Impact
No
Impact
a. Convert Prime Farmland, Unique Farmland, or
Farmland of Statewide Importance (Farmland), as
shown on the maps prepared pursuant to the
Farmland Mapping Program of the California
Resources Agency, to non-agricultural use?
b. Conflict with existing zoning for agricultural use,
or a Williamson Act contract?
c. Conflict with existing zoning for, or cause
rezoning of, forest land (as defined in Public
Resources Code section 12220(g)), timberland (as
defined by Public Resources Code section 4526),
or timberland zoned Timberland Production (as
defined by Government Code section 51104(g))?
d. Result in the loss of forest land or conversion of
forest land to non-forest use?
e. Involve other changes in the existing environment
which, due to their location or nature, could
individually or cumulatively result in loss of
Farmland to non-agricultural use?
Discussion
a,e. The proposed project site is currently developed with a residential use and is surrounded
by existing residential development. While the project site and vicinity to the north and
east historically consisted of orchards, the site was developed with the existing residence
in 1962. 4 Thus, the site has not been used for agricultural production for some time and is
currently designated as “Urban and Built-Up Land” on the Santa Clara County Important
Farmland map.5 Furthermore, the site is not zoned or designated in the General Plan for
agricultural uses. Given the designation of the site as Urban and Built-Up Land,
development of the proposed project would not convert Prime Farmland, Unique Farmland,
or Farmland of Statewide Importance to a non-agricultural use, or otherwise result in the
loss of Farmland to non-agricultural use. Therefore, no impact would occur as a result of
the proposed project.
b. The proposed project site is not under a Williamson Act contract and is not designated or
zoned for agricultural uses. Therefore, buildout of the proposed project would not conflict
with existing zoning for agricultural use or a Williamson Act contract, and no impact
would occur.
4 PIERS Environmental Services. Report of Limited Phase II Subsurface Investigation, 22561 Alcalde Road,
Cupertino, California 95014. August 19, 2017.
5 California Department of Conservation. Santa Clara County Important Farmland Map 2014. Published October
2016.
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
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January 2018
c,d. The project site is not considered forest land (as defined in Public Resources Code section
12220[g]), timberland (as defined by Public Resources Code section 4526), and is not
zoned Timberland Production (as defined by Government Code section 51104[g]). The
General Plan land use designation for the project site is Low/Medium Density Residential.
The zoning designation for the project site is Single-Family Residential. Therefore, the
proposed project would have no impact with regard to conversion of forest land or any
potential conflict with forest land, timberland, or Timberland Production zoning.
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
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January 2018
III. AIR QUALITY.
Would the project:
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporated
Less-Than-
Significant Impact
No
Impact
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. Create objectionable odors affecting a substantial
number of people?
a,b. The City of Cupertino is located in the San Francisco Bay Area Air Basin (SFBAAB),
which is under the jurisdiction of the Bay Area Air Quality Management District
(BAAQMD). The SFBAAB is currently designated as a nonattainment area for the State
and federal ozone, State and federal fine particulate matter 2.5 microns in diameter (PM2.5),
and State respirable particulate matter 10 microns in diameter (PM10) ambient air quality
standards (AAQS). The SFBAAB is designated attainment or unclassified for all other
AAQS. It should be noted that on January 9, 2013, the U.S. Environmental Protection
Agency (USEPA) issued a final rule to determine that the Bay Area has attained the 24-
hour PM2.5 federal AAQS. Nonetheless, the Bay Area must continue to be designated as
nonattainment for the federal PM2.5 AAQS until such time as the BAAQMD submits a
redesignation request and a maintenance plan to the USEPA, and the USEPA approves the
proposed redesignation.
In compliance with regulations, due to the nonattainment designations of the area, the
BAAQMD periodically prepares and updates air quality plans that provide emission
reduction strategies to achieve attainment of the AAQS, including control strategies to
reduce air pollutant emissions through regulations, incentive programs, public education,
and partnerships with other agencies. The current air quality plans are prepared in
cooperation with the Metropolitan Transportation Commission (MTC) and the Association
of Bay Area Governments (ABAG).
The most recent federal ozone plan is the 2001 Ozone Attainment Plan, which was adopted
on October 24, 2001 and approved by the California Air Resources Board (CARB) on
November 1, 2001. The plan was submitted to the USEPA on November 30, 2001 for
review and approval. The most recent State ozone plan is the 2010 Clean Air Plan (CAP),
adopted on September 15, 2010. The 2010 CAP was developed as a multi-pollutant plan
that provides an integrated control strategy to reduce ozone, PM, toxic air contaminants
(TACs), and greenhouse gases (GHGs). Although a plan for achieving the State PM10
standard is not required, the BAAQMD has prioritized measures to reduce PM in
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developing the control strategy for the 2010 CAP. The control strategy serves as the
backbone of the BAAQMD’s current PM control program.
The aforementioned air quality plans contain mobile source controls, stationary source
controls, and transportation control measures to be implemented in the region to attain the
State and federal AAQS within the SFBAAB. Adopted BAAQMD rules and regulations,
as well as the thresholds of significance, have been developed with the intent to ensure
continued attainment of AAQS, or to work towards attainment of AAQS for which the area
is currently designated nonattainment, consistent with applicable air quality plans. The
BAAQMD’s established significance thresholds associated with development projects for
emissions of the ozone precursors reactive organic gases (ROG) and oxides of nitrogen
(NOx), as well as for PM10, and PM2.5, expressed in pounds per day (lbs/day) and tons per
year (tons/yr), are listed in Table 1. By exceeding the BAAQMD’s mass emission
thresholds for operational emissions of ROG, NOX, PM10, or PM2.5 a project would be
considered to conflict with or obstruct implementation of the BAAQMD’s air quality
planning efforts.
Table 1
BAAQMD Thresholds of Significance
Pollutant
Construction Operational
Average Daily
Emissions (lbs/day)
Average Daily
Emissions (lbs/day)
Maximum Annual
Emissions (tons/year)
ROG 54 54 10
NOx 54 54 10
PM10 (exhaust) 82 82 15
PM2.5 (exhaust) 54 54 10
Source: BAAQMD, CEQA Guidelines, May 2017.
The proposed project’s construction and operational emissions were quantified using the
California Emissions Estimator Model (CalEEMod) software version 2016.3.2 - a
Statewide model designed to provide a uniform platform for government agencies, land
use planners, and environmental professionals to quantify air quality emissions, including
GHG emissions, from land use projects. The model applies inherent default values for
various land uses, including construction data, trip generation rates based on the Institute
of Transportation Engineers (ITE) Trip Generation Manual, 9th Edition, vehicle mix, trip
length, average speed, etc. In addition, the model assumes compliance with the most recent
2016 Title 24 Standards. However, where project-specific information is available, such
information should be applied in the model. Accordingly, the proposed project’s modeling
assumed the following:
• Construction would occur over an approximately five-month period;
• The existing structures to be demolished was assumed to consist of a total of
approximately 5,166 square feet;
• A total of approximately 0.45-acre of land would be disturbed during site
preparation;
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• A total of 130 cubic yards of material would be imported during site preparation;
and
• A total of 363 cubic yards of material could be exported during site preparation as
part of the soil remediation activities discussed in Section VIII, Hazards and
Hazardous Materials, of this IS/MND. It should be noted that the actual volume of
soil to be removed would likely be less; however, the soil amount assumed is based
on a worst-case scenario in order to provide a conservative analysis.
All CalEEMod results are included as an appendix to this IS/MND.
The proposed project’s estimated emissions associated with construction and operations
are presented and discussed in further detail below. A discussion of the proposed project’s
contribution to cumulative air quality conditions is provided below as well.
Construction Emissions
According to the CalEEMod results, the proposed project would result in maximum
unmitigated construction criteria air pollutant emissions as shown in Table 2. As shown in
the table, the proposed project’s construction emissions would be below the applicable
thresholds of significance for ROG, NOX, PM10, and PM2.5.
Table 2
Maximum Unmitigated Construction Emissions (lbs/day)
Pollutant
Proposed Project
Emissions
Threshold of
Significance Exceeds Threshold?
ROG 1.89 54 NO
NOX 30.31 54 NO
PM10 (exhaust) 0.86 82 NO
PM10 (fugitive) 1.66 None N/A
PM2.5 (exhaust) 0.80 54 NO
PM2.5 (fugitive) 0.44 None N/A
Source: CalEEMod, January 2018 (see appendix).
Although thresholds of significance for mass emissions of fugitive dust PM10 and PM2.5 have not been identified by the City of Cupertino or BAAQMD, the proposed project’s
estimated fugitive dust emissions have been included for informational purposes. All
projects within the jurisdiction of the BAAQMD are required to implement all of the
BAAQMD’s Basic Construction Mitigation Measures, which include the following:
1. All haul trucks transporting soil, sand, or other loose material off-site shall be
covered.
2. All visible mud or dirt track-out onto adjacent public roads shall be removed using
wet power vacuum street sweepers at least once per day. The use of dry power
sweeping is prohibited.
3. All vehicle speeds on unpaved roads shall be limited to 15 mph.
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4. All roadways, driveways, and sidewalks to be paved shall be completed as soon as
possible. Building pads shall be laid as soon as possible after grading unless seeding
or soil binders are used.
5. Idling times shall be minimized either by shutting equipment off when not in use
or reducing the maximum idling time to five minutes (as required by the California
airborne toxics control measure Title 13, Section 2485 of California Code of
Regulations [CCR]). Clear signage shall be provided for construction workers at all
access points.
6. All construction equipment shall be maintained and properly tuned in accordance
with manufacturer‘s specifications. All equipment shall be checked by a certified
visible emissions evaluator.
7. Post a publicly visible sign with the telephone number and person to contact at the
lead agency regarding dust complaints. This person shall respond and take
corrective action within 48 hours. The Air District’s phone number shall also be
visible to ensure compliance with applicable regulations.
The proposed project’s implementation of the BAAQMD’s Basic Construction Mitigation
Measures listed above would help to further minimize construction-related emissions.
Because the proposed project would be below the applicable thresholds of significance for
construction emissions, the proposed project would not be considered to result in a
significant air quality impact during construction.
Operational Emissions
According to the CalEEMod results, the proposed project would result in maximum
unmitigated operational criteria air pollutant emissions as shown in Table 3. As shown in
the table, the proposed project’s operational emissions would be below the applicable
thresholds of significance. Because the proposed project’s operational emissions would be
below the applicable thresholds of significance, the proposed project would result in a less-
than-significant air quality impact during operations.
Table 3
Maximum Unmitigated Operational Emissions
Pollutant
Proposed Project Emissions Threshold of Significance Exceeds
Threshold? lbs/day tons/yr lbs/day tons/yr
ROG 2.20 0.04 54 10 NO
NOX 0.22 0.03 54 10 NO
PM10 (exhaust) 0.38 0.00 82 15 NO
PM10 (fugitive) 0.09 0.02 None None N/A
PM2.5 (exhaust) 0.38 0.00 54 10 NO
PM2.5 (fugitive) 0.03 0.00 None None N/A
Source: CalEEMod, January 2018 (see appendix).
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Conclusion
As stated previously, the applicable regional air quality plans include the 2001 Ozone
Attainment Plan and the 2010 CAP. According to BAAQMD, if a project would not result
in significant and unavoidable air quality impacts after the application of all feasible
mitigation, the project may be considered consistent with the air quality plans. Because the
proposed project would result in emissions below BAAQMD’s thresholds of significance,
the proposed project would not be considered to conflict with or obstruct the
implementation of any regional air quality plans, violate any air quality standard, or
contribute substantially to an existing or projected air quality violation. Therefore, a less-
than-significant impact would occur.
c. Past, present and future development projects contribute to the region’s adverse air quality
impacts on a cumulative basis. By nature, air pollution is largely a cumulative impact. A
single project is not sufficient in size to, by itself, result in nonattainment of AAQS. Instead,
a project’s individual emissions contribute to existing cumulatively significant adverse air
quality impacts. If a project’s contribution to the cumulative impact is considerable, then
the project’s impact on air quality would be considered significant.
In developing thresholds of significance for air pollutants, BAAQMD considered the
emission levels for which a project’s individual emissions would be cumulatively
considerable. The thresholds of significance presented in Table 1 represent the levels at
which a project’s individual emissions of criteria air pollutants or precursors would result
in a cumulatively considerable contribution to the SFBAAB’s existing air quality
conditions. If a project exceeds the significance thresholds presented in Table 1, the
proposed project’s emissions would be cumulatively considerable, resulting in significant
adverse cumulative air quality impacts to the region’s existing air quality conditions.
Because the proposed project would result in emissions below the applicable thresholds of
significance for both construction and operation, the project would not result in a
cumulatively considerable contribution to the region’s existing air quality conditions.
Based on the above, the proposed project would not 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. Thus, a less-than-significant
impact would result.
d. Some land uses are considered more sensitive to air pollution than others, due to the types
of population groups or activities involved. Heightened sensitivity may be caused by health
problems, proximity to the emissions source, and/or duration of exposure to air pollutants.
Children, pregnant women, the elderly, and those with existing health problems are
especially vulnerable to the effects of air pollution. Sensitive receptors are typically defined
as facilities where sensitive receptor population groups (i.e., children, the elderly, the
acutely ill, and the chronically ill) are likely to be located. Accordingly, land uses that are
typically considered to be sensitive receptors include residences, schools, playgrounds,
childcare centers, retirement homes, convalescent homes, hospitals, and medical clinics.
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The nearest existing sensitive receptors to the project site would be the single-family
residences located immediately to the east, north, and west of the site.
The major pollutant concentrations of concern are localized carbon monoxide (CO)
emissions and TAC emissions, which are addressed in further detail below.
Localized CO Emissions
Localized concentrations of CO are related to the levels of traffic and congestion along
streets and at intersections. High levels of localized CO concentrations are only expected
where background levels are high, and traffic volumes and congestion levels are high.
Emissions of CO are of potential concern, as the pollutant is a toxic gas that results from
the incomplete combustion of carbon-containing fuels such as gasoline or wood. CO
emissions are particularly related to traffic levels.
In order to provide a conservative indication of whether a project would result in localized
CO emissions that would exceed the applicable threshold of significance, the BAAQMD
has established screening criteria for localized CO emissions. According to BAAQMD, a
proposed project would result in a less-than-significant impact related to localized CO
emission concentrations if all of the following conditions are true for the project:
• The project is consistent with an applicable congestion management program
established by the county congestion management agency for designated roads or
highways, regional transportation plan, and local congestion management agency
plans;
• The project traffic would not increase traffic volumes at affected intersections to
more than 44,000 vehicles per hour; and
• The project traffic would not increase traffic volumes at affected intersections to
more than 24,000 vehicles per hour where vertical and/or horizontal mixing is
substantially limited (e.g., tunnel, parking garage, underpass, etc.).
The applicable Congestion Management Plan (CMP) for the proposed project site is the
Santa Clara Valley Transportation Authority (VTA) CMP.6 As discussed in the
Transportation and Circulation section of this IS/MND, the proposed project would not
conflict with the VTA CMP. In addition, the proposed project would be anticipated to
generate a total of 19 average daily trips (ADT). Given the relatively small number of trips
that would be generated, the project would not substantially affect traffic volumes at
intersections in the project vicinity. Furthermore, areas where vertical and/or horizontal
mixing is limited due to tunnels, underpasses, or similar features do not exist in the project
area. As such, based on the BAAQMD screening criteria, the proposed project would not
be expected to result in substantial levels of localized CO at surrounding intersections or
generate localized concentrations of CO that would exceed standards.
6 Santa Clara Valley Transportation Authority. 2013 Congestion Management Program. October 2013.
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TAC Emissions
Another category of environmental concern is TACs. The CARB’s Air Quality and Land
Use Handbook: A Community Health Perspective (Handbook) provides recommended
setback distances for sensitive land uses from major sources of TACs, including, but not
limited to, freeways and high traffic roads, distribution centers, and rail yards. The CARB
has identified diesel particulate matter (DPM) from diesel-fueled engines as a TAC; thus,
high volume freeways, stationary diesel engines, and facilities attracting heavy and
constant diesel vehicle traffic are identified as having the highest associated health risks
from DPM. Health risks associated with TACs are a function of both the concentration of
emissions and the duration of exposure, where the higher the concentration and/or the
longer the period of time that a sensitive receptor is exposed to pollutant concentrations
would correlate to a higher health risk.
The proposed project would not involve any land uses or operations that would be
considered major sources of TACs, including DPM. As such, the proposed project would
not generate any substantial pollutant concentrations during operations. However, short-
term, construction-related activities could result in the generation of TACs, specifically
DPM, from on-road haul trucks and off-road equipment exhaust emissions. Nevertheless,
construction is temporary and occurs over a relatively short duration in comparison to the
operational lifetime of the proposed project. All construction equipment and operation
thereof would be regulated per the In-Use Off-Road Diesel Vehicle Regulation, which is
intended to help reduce emissions associated with off-road diesel vehicles and equipment,
including DPM. Project construction would also be required to comply with all applicable
BAAQMD rules and regulations, particularly associated with permitting of air pollutant
sources. In addition, construction activity (except for street construction) would be limited
to daytime hours per Section 10.48.053 of the City’s Municipal Code.
Because construction equipment on-site would not operate for long periods of time and
would occur on a relatively small scale, associated emissions of DPM would be minimal.
Due to the temporary nature of construction and the relatively short duration of potential
exposure to associated emissions, sensitive receptors in the area would not be exposed to
pollutants for a permanent or substantially extended period of time. Therefore, construction
of the proposed project would not be expected to expose nearby sensitive receptors to
substantial pollutant concentrations.
Conclusion
Based on the above, the proposed project would not expose any sensitive receptors to
substantial concentrations of localized CO or TACs from construction or operation.
Therefore, the proposed project would result in a less-than-significant impact related to
the exposure of sensitive receptors to substantial pollutant concentrations.
e. Due to the subjective nature of odor impacts, the number of variables that can influence
the potential for an odor impact, and the variety of odor sources, quantitative
methodologies to determine the presence of a significant odor impact do not exist. Typical
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odor-generating land uses include, but are not limited to, wastewater treatment plants,
landfills, and composting facilities. The proposed project would not introduce any such
land uses. Residential land uses, such as the proposed single-family homes, are not
typically associated with objectionable odors.
Construction activities often include diesel-fueled equipment and heavy-duty trucks, which
could create odors associated with diesel fumes that may be considered objectionable.
However, as discussed above, construction activities would be temporary, and operation of
construction equipment would be restricted to daytime hours per the City’s Municipal
Code. Project construction would also be required to comply with all applicable BAAQMD
rules and regulations, particularly associated with permitting of air pollutant sources. The
aforementioned regulations would help to minimize air pollutant emissions, as well as any
associated odors. Accordingly, substantial objectionable odors would not be expected to
occur during construction activities.
For the aforementioned reasons, construction and operation of the proposed project would
not create objectionable odors affecting a substantial number of people, and a less-than-
significant impact related to objectionable odors would result.
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IV. BIOLOGICAL RESOURCES.
Would the project:
Potentially
Significant
Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-Than-
Significant Impact
No
Impact
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 Wildlife 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, and
regulations or by the California Department of Fish
and Wildlife or US 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.) through direct
removal, filling, hydrological interruption, or other
means?
d. Interfere substantially with the movement of any
resident or migratory fish or wildlife species or with
established resident or migratory wildlife corridors,
or impede the use of wildlife nursery sites?
e. Conflict with any local policies or ordinances
protecting biological resources, such as a tree
preservation policy or ordinance?
f. Conflict with the provisions of an adopted Habitat
Conservation Plan, Natural Conservation
Community Plan, or other approved local, regional,
or state habitat conservation plan?
Discussion
a. The proposed project site comprises a 19,562-square-foot property located in a residential
neighborhood. The site is currently developed with a residential use and is highly disturbed
as a result. Vegetation on the site consists of landscaping associated with the residence,
including some grass and shrubs, as well as nine trees (seven of which are to be removed).
The proposed project site does not contain any aquatic or riparian habitat.
A query of CNDDB was performed in order to determine the potential plant and wildlife
species that could occur within the proposed project area. The Cupertino Quad was used
as the search area. The CNDDB query results indicate 18 special-status plant and wildlife
species that are known to occur within the project vicinity. However, due to the highly-
disturbed nature of the project site, the requisite habitat types for any of the identified
special-status species do not occur on-site. For example, the species require aquatic,
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woodland, chaparral, or proximate open grassland habitat, which does not occur on-site or
in the immediate project vicinity.
While special-status species would not occur on-site, migratory birds have the potential to
nest within the on-site trees and shrubs. Birds and their nests are protected under California
Fish and Game Code (Sections 3503, 3503.5, 3513), and the Migratory Bird Treaty Act
(MBTA). The proposed project would include removal of trees during construction, and,
thus, could result in impacts to nesting raptors and/or migratory birds, potentially occurring
in the trees. Therefore, the proposed project could have a substantial adverse effect, either
directly or through habitat modifications, on species identified as a candidate, sensitive, or
special-status in local or regional plans, policies, or regulations, or by the California
Department of Fish and Wildlife or U.S. Fish and Wildlife Service, and a potentially
significant impact could result.
Mitigation Measure(s)
Implementation of the following mitigation measure would reduce the above impact to a
less-than-significant level.
IV-1. A pre-construction survey for nesting birds shall be conducted for the
project site and a 250-foot radius around the project site by a qualified
biologist not more than two weeks prior to site disturbance during the
breeding season (February 1 to August 31). If site disturbance commences
outside the breeding season, a pre-construction survey for nesting birds is
not required. If active nests of migratory birds are not detected within
approximately 250 feet of the project site, further mitigation is not required.
Results of the survey shall be submitted to the Community Development
Department.
If nesting raptors or other migratory birds are detected on or within 250
feet of the site during the survey, a suitable construction-free buffer shall be
established around all active nests. The dimensions of the buffer shall be a
minimum of 75 feet for passerine birds and 250 feet for raptors. The buffer
size may vary depending on location and species. The buffer areas shall be
enclosed with temporary fencing, and construction equipment and workers
shall not enter the enclosed setback areas. Buffers shall remain in place for
the duration of the breeding season or until a qualified biologist has
confirmed that all chicks have fledged and are independent of their parents.
b,c. The project site is currently developed with a residential use, and, thus, is highly disturbed.
The site does not contain any aquatic features or riparian habitat, and sensitive plant
communities, including wetlands, do not exist on or near the site. As a result, the proposed
project would not have a substantial adverse effect on riparian habitat, sensitive natural
communities, or federally protected wetlands. Thus, no impact would occur.
d. The project site is surrounded by existing development and is not linked to any open space
areas through which wildlife movement would occur. As noted above, the project does not
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contain streams or other waterways that could be used by migratory fish or as a wildlife
corridor for other wildlife species. As such, the project would not interfere substantially
with the movement of any resident or migratory fish or wildlife species or with established
resident or migratory wildlife corridors, or impede the use of wildlife nursery sites. Thus,
no impact would occur.
e. Based on the project plans, as shown in Figure 3, the project would involve the removal of
seven trees, some of which may be considered protected trees pursuant to Section
14.18.050 of the City’s Municipal Code. If the on-site trees to be removed are indeed
protected trees, the applicant must first obtain a tree removal permit from the City’s
Community Development Department and pay the permit fee. The information required
when submitting a tree removal permit application, includes, but is not limited to, the
following:
• A drawing outlining the location of the tree(s) and proposed tree replacements.
• A written explanation of why the tree(s) should be removed.
In conjunction with the tree removal permit, the City would impose tree replacement
standards or in-lieu fees pursuant to Section 14.18.160 of the Municipal Code.
Furthermore, per Section 14.18.060 of the Municipal Code, the project applicant would be
required to adopt a maintenance plan for any protected trees that would be retained as part
of the project. Compliance with Chapter 14.18 of the City’s Municipal Code, as described
above, would ensure that the proposed project would not conflict with the City’s tree
preservation policies and ordinances. Therefore, the project would not conflict with any
local policies or ordinances protecting biological resources, such as a tree preservation
policy or ordinance, and a less-than-significant impact would occur.
f. The City of Cupertino is not currently participatory to a Habitat Conservation Plan/Natural
Community Conservation Plan (HCP/NCCP). Therefore, the project site is not located in
an area with an approved HCP/NCCP, or local, regional, or State habitat conservation plan,
and no impact would occur regarding a conflict with the provisions of such a plan.
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V. CULTURAL RESOURCES.
Would the project:
Potentially
Significant
Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-Than-
Significant Impact
No
Impact
a. Cause a substantial adverse change in the
significance of a historical resource as defined in
Section 15064.5?
b. Cause a substantial adverse change in the
significance of a unique archaeological resource
pursuant to Section 15064.5?
c. Directly or indirectly destroy a unique
paleontological resource on site or unique geologic
features?
d. Disturb any human remains, including those
interred outside of formal cemeteries.
Discussion
a. Historical resources are features that are associated with the lives of historically-important
persons and/or historically-significant events, or that embody the distinctive characteristics
of a type, period, region, or method of construction. Examples of typical historical
resources include, but are not limited to, buildings, farmsteads, rail lines, bridges, and trash
scatters containing objects such as colored glass and ceramics. As discussed previously,
the proposed project site currently contains a residential structure and a shed.
According to a Phase I Environmental Site Assessment (ESA) prepared for the proposed
project by PIERS Environmental Services, the on-site residence was constructed circa
1962. In order to determine whether the on-site structures constitute historical resources,
the structures were evaluated using the California Register of Historic Resources (CRHR)
and National Register of Historic Places (NRHP) eligibility criteria.
CRHR Criteria
The CRHR eligibility criteria include the following:
(1) It is associated with events that have made a significant contribution to the broad
patterns of local or regional history, or the cultural heritage of California or the
U.S.;
(2) It is associated with the lives of persons important to local, California, or national
history;
(3) It embodies the distinctive characteristics of a type, period, region, or method of
construction, or represents the work of a master or possesses high artistic values; or
(4) It has yielded, or has the potential to yield, information important to the prehistory
or history of the local area, California, or the nation.
In addition, the resource must retain integrity. Integrity is evaluated with regard to the
retention of location, design, setting, materials, workmanship, feeling, and association.
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NRHP Criteria
The NRHP eligibility criteria include the following: “The quality of significance in
American history, architecture, archaeology, and culture is present in districts, sites,
buildings, structures, and objects of state and local importance that possess aspects of
integrity of location, design, setting, materials, workmanship, feeling, association, and
(a) is associated with events that have made a significant contribution to the broad
patterns of our history;
(b) is associated with the lives of a person or persons significance in our past;
(c) embodies the distinctive characteristics of a type, period or method of construction,
or represents the work of a master, or possesses high artistic value, or represents a
significant and distinguishable entity whose components may lack individual
distinction; or
(d) has yielded or may be likely to yield information important in prehistory or history.
In addition, the resource must be at least 50 years old, except in exceptional circumstances.
Evaluation
The existing on-site structures are not associated with any significant historical events or
narratives in the City of Cupertino or California, and are not likely to yield information
important to the prehistory or history of the local area, California, or the nation. The site
has not been occupied or owned by any persons important to local, State, or national
history, and, thus, is not associated with the lives of a person or persons of significance.
Additionally, the residence does not embody the distinctive characteristics of a type, period
or method of construction, represent the work of a master, possess high artistic value, or
represent a significant and distinguishable entity whose components may lack individual
distinction.
Conclusion
Based on the above, the on-site structures are not eligible for consideration as historical
resources per the CRHR or NRHP eligibility criteria, and, thus, would not be considered
historical resources. Therefore, the project would not cause a substantial adverse change in
the significance of a historical resource, and a less-than-significant impact would occur.
b-d. The proposed project site is currently developed with a residential structure, and, thus, is
highly disturbed. In addition, the site is located within a residential neighborhood. Due to
the disturbed nature of the site and the surrounding area, the discovery of underlying
archeological, paleontological, and/or tribal resources is not expected. However, unknown
archaeological resources, including human bone, have the potential to be uncovered during
ground-disturbing construction activities at the proposed project site.
In compliance with State law (Section 7050.5 of the Health and Safety Code and Section
5097.94 of the Public Resources Code), as well as the City’s standard conditions of
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approval, in the event human remains are encountered during grading and construction, all
work within 50 feet of the find would be stopped, and the Santa Clara County Coroner’s
office would be notified. If the remains are determined to be Native American, the Coroner
would notify the Native American Heritage Commission to identify the “Most Likely
Descendant” (MLD). The City of Cupertino, in consultation with the MLD, would then
prepare a plan for treatment, study, and re-internment of the remains.
Therefore, given the low likelihood of encountering resources, and the proposed project’s
compliance with the City’s standard conditions of approval regarding cultural resources,
the project would not cause a substantial adverse change in the significance of a unique
archaeological resource pursuant to CEQA Guidelines Section 15064.5, directly or
indirectly destroy a unique paleontological resource or geological feature on site, or disturb
human remains, including those interred outside of formal cemeteries. Therefore, impacts
would be considered less than significant.
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VI. GEOLOGY AND SOILS.
Would the project:
Potentially
Significant
Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-Than-
Significant Impact
No
Impact
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 based on other
substantial evidence of a known fault (Refer to
Division of Mines and Geology Special Pub.
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 a geologic unit or soil that is
unstable, or that would become unstable as a result
of the project, and potentially result in on- or off-
site landslide, lateral spreading, subsidence,
liquefaction or collapse?
d. Be located on expansive soil, as defined in Table
18-1B of the Uniform Building Code (1994),
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?
a,c. According to the California Geological Survey Alquist-Priolo Earthquake Fault Zone
Maps, the proposed project site is not located within the vicinity of an Alquist-Priolo
Earthquake Fault Zone.7 Figure HS-5 in the City’s General Plan identifies areas in the City
that are potentially at risk for fault rupture, landslides, and liquefaction/inundation. Areas
mapped as Liquefaction/Inundation Zones by the City are also generally at risk for lateral
spreading hazards.8 Per Figure HS-5, the site is located within a Valley Zone, which is
defined as an area with relatively low levels of geologic hazard risk. Therefore, the
proposed project would not be at risk for fault rupture impacts, seismic-related ground
failure (including liquefaction, lateral spreading and subsidence), or landslides. In addition,
the project would be designed to comply with all applicable State and local regulations,
including the California Building Code (CBC), which would minimize any potential risks
associated with seismic ground shaking.
7 California Department of Conservation. Special Studies Zones, Cupertino Quadrangle. Effective July 1, 1974.
8 City of Cupertino. General Plan: Community Vision 2015 – 2040 [pg. E-5]. Adopted October 20, 2015.
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Consequently, the proposed project would not expose people or structures to potential
adverse effects, including the risk of loss, injury, or death involving rupture of a known
earthquake fault, strong seismic ground shaking, seismic-related ground failure, and/or
liquefaction or landslides. Therefore, a less-than-significant impact would result.
b. The proposed project would require excavation and grading of the site prior to construction,
including soil excavation and off-haul associated with on-site soil remediation (see Section
VIII for additional discussion). During such early stages of construction, topsoil would be
exposed. After grading and prior to overlaying the ground surface with structures, while
topsoil would be exposed, the potential exists for wind and/or water erosion to occur, which
could affect the project area and potentially inadvertently transport eroded soils to
downstream waterways. However, topsoil exposure would be temporary during site
preparation and would cease once development of the proposed single-family homes
occurs.
The City’s Municipal Code requires applicants to provide and comply with an Interim
Erosion and Sediment Control Plan (Interim Plan). The Interim Plan shall show the
location of erosion control measures and erosion control planting shall be shown on the
site map/grading plan. The applicant shall provide the following information with respect
to conditions existing on the site during land-disturbing or filling activities or stockpiling
of soil:
1. A delineation and brief description of the measures to be undertaken to retain
sediment on the site, including, but not limited to, the designs and specifications or
berms and sediment detention basins, and a schedule for their maintenance and
upkeep;
2. A delineation and brief description of the surface runoff and erosion control
measures to be implemented, including, but not limited, to types and methods of
applying mulches, and designs and specifications for diverters, dikes and drains,
and a schedule for their maintenance and upkeep;
3. A delineation and brief description of the vegetative measures to be undertaken,
including, but not limited to, seeding methods, and type, location and extent of
preexisting and undisturbed vegetation types, and a schedule for maintenance and
upkeep.
Because the project would comply with the City’s interim erosion control requirements,
the project would not result in substantial soil erosion or loss of topsoil. Therefore, a less-
than-significant impact would occur.
d. Expansive soils increase in volume when they absorb water and have the potential to crack
or otherwise compromise the integrity of building foundations. According to the City’s
General Plan EIR, the proposed project site is not located in an area of the City known to
contain highly expansive soils.9 Furthermore, the proposed project would be subject to
applicable CBC regulations and provisions, as adopted in Chapter 16.04 of the City’s
9 City of Cupertino. General Plan Amendment, Housing Element Update, and Associated Rezoning Draft EIR [4.5-
18]. June 18, 2014.
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Municipal Code. Therefore, the proposed project would not be located on expansive soil,
as defined in Table 18-1B of the Uniform Building Code, and a less-than-significant
impact would occur.
e. The proposed project would connect to the City’s existing sewer system and would not
require the use of a septic tank or other alternative waste water disposal method. Therefore,
no impact would occur related to having soils incapable of adequately supporting the use
of septic tanks or alternate wastewater disposal systems.
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VII. GREENHOUSE GAS EMISSIONS.
Would the project:
Potentially
Significant
Impact
Less Than
Significant
with
Mitigation
Incorporated
Less-Than-
Significant
Impact
No
Impact
a. Generate greenhouse gas emissions, either directly
or indirectly, that may have a significant impact on
the environment?
b. Conflict with an applicable plan, policy or regulation
adopted for the purpose of reducing the emissions of
greenhouse gasses?
a,b. Emissions of greenhouse gases (GHGs) contributing to global climate change are
attributable in large part to human activities associated with the industrial/manufacturing,
utility, transportation, residential, and agricultural sectors. Therefore, the cumulative global
emissions of GHGs contributing to global climate change can be attributed to every nation,
region, and city, and virtually every individual on earth. An individual project’s GHG
emissions are at a micro-scale level relative to global emissions and effects to global
climate change; however, an individual project could result in a cumulatively considerable
incremental contribution to a significant cumulative macro-scale impact. As such, impacts
related to emissions of GHG are inherently considered cumulative impacts.
Implementation of the proposed project would cumulatively contribute to increases of
GHG emissions. Estimated GHG emissions attributable to future development would be
primarily associated with increases of carbon dioxide (CO2) and, to a lesser extent, other
GHG pollutants, such as methane (CH4) and nitrous oxide (N2O) associated with area
sources, mobile sources or vehicles, utilities (electricity and natural gas), water usage,
wastewater generation, and the generation of solid waste. The primary source of GHG
emissions for the project would be mobile source emissions. The common unit of
measurement for GHG is expressed in terms of annual metric tons of CO2 equivalents
(MTCO2e/yr).
A number of regulations currently exist related to GHG emissions, predominantly
Assembly Bill (AB 32), Executive Order S-3-05, and Senate Bill (SB 32). AB 32 sets forth
a statewide GHG emissions reduction target of 1990 levels by 2020. Executive Order S-3-
05 sets forth a transitional reduction target of 2000 levels by 2010, the same target as AB
32 of 1990 levels by 2020, and further builds upon the AB 32 target by requiring a reduction
to 80 percent below 1990 levels by 2050. SB 32 also builds upon AB 32 and sets forth a
transitional reduction target of 40 percent below 1990 levels by 2030. In order to implement
the statewide GHG emissions reduction targets, local jurisdictions are encouraged to
prepare and adopt area-specific GHG reduction plans and/or thresholds of significance for
GHG emissions.
A discussion of the City’s Climate Action Plan (CAP), as well as applicable BAAQMD
thresholds related to GHG emissions, is provided below.
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Climate Action Plan
As a means of achieving the statewide GHG emissions reduction goals, the City has
adopted a CAP. The targets are consistent with statewide goals. In addition, the CAP
includes a number of reduction measures intended to be implemented by the City in order
to accomplish the reduction goals. The emissions reduction strategies developed by the
City follows the BAAQMD’s CEQA Guidelines and the corresponding criteria for a
Qualified Greenhouse Gas Emissions Reduction Program as defined by the BAAQMD.
Because the provisions included in the CAP mirror the elements required per Section
15.183.5 of the CEQA Guidelines, the CAP is consistent with existing State regulations
related to GHG emissions, as well as BAAQMD thresholds of significance. It should be
noted that a quantitative threshold for GHG emissions for individual development projects
has not been established by the City or set forth in the CAP.
The GHG inventory contained in the City’s CAP was derived based on the land use
designations and associated densities defined in the City’s General Plan. The proposed
project would be consistent with the project site’s existing General Plan land use
designation, and would not modify the type of use previously anticipated for the site by the
City. It should be noted that the project would result in a slight increase in development
intensity relative to existing site uses; however, associated increases in GHG emissions
related to such would not be substantial.
BAAQMD Thresholds
The proposed project is located within the jurisdictional boundaries of the BAAQMD. The
BAAQMD threshold of significance for project-level operational GHG emissions is 1,100
MTCO2e/yr. BAAQMD’s approach to developing a threshold of significance for GHG
emissions is to identify the emissions level for which a project would not be expected to
substantially conflict with existing California legislation adopted to reduce statewide GHG
emissions needed to move towards climate stabilization. If a project would generate GHG
emissions above the threshold level, the project would be considered to generate significant
GHG emissions and conflict with applicable GHG regulations.
The proposed project’s estimated construction and operational GHG emissions were
quantified using CalEEMod, using the same assumptions as presented in the Air Quality
section of this IS/MND. The proposed project’s required compliance with the current
California Building Energy Efficiency Standards Code was assumed in the modeling. In
addition, the CO2 intensity factor within the model was adjusted to reflect the Pacific Gas
& Electric Company’s anticipated progress towards statewide renewable portfolio standard
goals. All CalEEMod results are included as an appendix to this IS/MND.
Based on the results of the modeling, the project would result in total construction
emissions of approximately 78.99 MTCO2e/yr. While neither the City nor BAAQMD has
established GHG emissions thresholds for construction, construction emissions associated
with the proposed project would be far below the BAAQMD’s adopted operational
threshold of 1,100 MTCO2e/yr. Construction-related GHG emissions are a one-time
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35 January 2018
release and are, therefore, not typically expected to generate a significant contribution to
global climate change, as global climate change is inherently a cumulative effect that
occurs over a long period of time. Furthermore, construction activity associated with the
proposed project would occur over a short duration and be limited in scope.
The project’s estimated operational emissions are summarized in Table 4 below. As shown
in the table, the proposed project would result in operational GHG emissions well below
the 1,100 MTCO2e/yr threshold. Therefore, the proposed project would not result in
operational impacts related to GHG emissions.
Table 4
Project Operational GHG Emissions
Emission Source Annual GHG Emissions (MTCO2e/yr)
Area 0.36
Energy 7.53
Mobile 18.84
Solid Waste 1.27
Water 0.36
TOTAL ANNUAL GHG EMISSIONS 28.36
Source: CalEEMod, November 2017.
Conclusion
Based on the above, the proposed project would be consistent with the City’s adopted CAP.
In addition, the estimated annual operational and construction GHG emissions would be
below the applicable BAAQMD thresholds of significance. As such, the proposed project
would not be considered to generate GHG emissions, either directly or indirectly, that may
have a significant impact on the environment, or conflict with any applicable plan, policy,
or regulation adopted for the purpose of reducing the emissions of GHGs. Therefore,
impacts would be considered less than significant.
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VIII. HAZARDS AND HAZARDOUS
MATERIALS.
Would the project:
Potentially
Significant
Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-Than-
Significant
Impact
No
Impact
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 likely 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 the risk of loss, injury
or death involving wildland fires, including where
wildlands are adjacent to urbanized areas or where
residences are intermixed with wildlands?
Discussion
a. Residential land uses are not typically associated with the routine transport, use, disposal,
or generation of substantial amounts of hazardous materials. Future residents may use
common household cleaning products, fertilizers, and herbicides on-site, any of which
could contain potentially hazardous chemicals; however, such products would be expected
to be used in accordance with label instructions. Due to the regulations governing use of
such products and the amount that would be used on the site, routine use of such products
would not represent a substantial risk to public health or the environment. Therefore, the
project would not create a significant hazard to the public or the environment through the
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routine transport, use, or disposal of hazardous materials, and a less-than-significant
impact would occur.
b. The following discussion includes an analysis of hazardous and toxic materials that could
be used on the proposed project site during construction activities, as well as existing
hazardous materials known to be present on the site.
Construction Equipment
Construction activities associated with the proposed project would involve the use of heavy
equipment, which would contain fuels and oils, and various other products such as
concrete, paints, and adhesives. Small quantities of potentially toxic substances (e.g.,
petroleum and other chemicals used to operate and maintain construction equipment)
would be used at the project site and transported to and from the site during construction.
However, the project contractor would be required to comply with all California Health
and Safety Codes and local City and County ordinances regulating the handling, storage,
and transportation of hazardous and toxic materials. Compliance with such regulations
would ensure that the proposed project would not create a significant hazard to the public
or the environment through reasonably foreseeable upset and accident conditions involving
the likely release of hazardous materials into the environment during construction
activities, particularly associated with construction equipment.
Existing Soil Contamination
A Phase I ESA was prepared for the proposed project by PIERS Environmental Services
in July 2017.10 The Phase I ESA did not reveal evidence of Recognized Environmental
Conditions (RECs), Historical RECs (HRECs), or Controlled RECs (CRECs). As
discussed previously, the proposed project site has historically been used for agricultural
purposes, particularly as an orchard. As such, pesticides and herbicides may have been
used on the site. To comply with the City of Cupertino Planning Department requirements,
and to investigate any residual effects of the former use of the project site as an orchard, a
Limited Phase II Subsurface Investigation (Phase II) was prepared for the proposed project
by PIERS Environmental Services.11 As part of the Phase II, and in accordance with DTSC
guidelines for sampling for agricultural chemicals, four soil samples were collected on-site
on August 10, 2017 and analyzed for organochlorine pesticides (including, but not limited
to, chlordane, a-Chlordane, g-Chlordane, p, p-DDD, p, p-DDE, p, p-DDT, dieldrin, and
heptachlor), arsenic, and lead. The soil samples were located in future landscape areas, as
the landscape areas would not be covered by impervious surfaces and, as a result, exposure
to soil contaminants in such areas could occur. Concentrations of organochlorides
pesticides, arsenic, and lead were compared to the applicable Environmental Screening
Levels (ESLs), which are the concentrations of contaminants in soils and groundwater
established by the Regional Water Quality Control Board (RWQCB) used to determine the
10 PIERS Environmental Services. Phase I Environmental Site Assessment, 22561 Alcalde Road, Cupertino,
California 95014. July 17, 2017.
11 PIERS Environmental Services. Report of Limited Phase II Subsurface Investigation, 22561 Alcalde Road,
Cupertino, California 95014. August 19, 2017.
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relative risks to human health and the environment. Generally, the presence of a chemical
in soil or groundwater at concentrations below the corresponding ESL can be assumed to
not pose a significant threat to human health or the environment. The ESLs for soil
differentiate between residential and commercial usage, although in some cases the values
are the same.
The only organochlorine pesticide detected above the residential ESL of 0.48 parts per
million (ppm), was chlordane, which was detected in two soil samples (S1 and S2) at
concentrations ranging up to 2.3 ppm at a depth of 0.4 feet.12 Although arsenic was detected
in all four soil samples at concentrations ranging between 1.2 ppm and 5.4 ppm, which
exceeds the residential ESL of 0.067 ppm, the concentrations are within the range of
naturally-occurring background concentrations (0.6 ppm to 11 ppm) that are typical for
Bay Area soils. Lead was detected in all four soil samples at concentrations ranging up to
15 ppm, which is below the residential ESL of 80 ppm, and in the range of, or below,
naturally-occurring background concentrations. In order to better characterize the vertical
extent of the soil contamination, PIERS Environmental Services conducted further soil
sampling and analysis at the same sample points at a depth of 0.5 feet below grade.
According to the addendum prepared by PIERS Environmental Services on January 8,
2018, the results of the additional soil sampling determined that the concentration for all
contaminants was below the relative ESL at a depth of 0.5 feet (or six inches).
While the reported chlordane levels in the two samples are above the residential ESLs, they
are below the construction worker ESL of 14 mg/kg, thereby alleviating short duration
construction worker exposure concerns. However, based on the above, future occupants
could be exposed to soil contaminants. Therefore, the proposed project could create a
significant hazard to the public or the environment through reasonably foreseeable upset
and accident conditions involving the likely release of hazardous materials into the
environment, particularly related to existing soil contamination at the site.
Asbestos-Containing Materials and Lead-Based Paint
Asbestos is the name for a group of naturally occurring silicate minerals that are considered
to be “fibrous” and, through processing, can be separated into smaller and smaller fibers.
The fibers are strong, durable, chemical resistant, and resistant to heat and fire. They are
also long, thin, and flexible, such that they can be woven into cloth. Because of the above
qualities, asbestos was considered an ideal product and has been used in thousands of
consumer, industrial, maritime, automotive, scientific, and building products. However,
later discoveries found that, when inhaled, the material caused serious illness.
For buildings constructed prior to 1980, the Code of Federal Regulations (29 CFR
1926.1101) states that all thermal system insulation (boiler insulation, pipe lagging, and
related materials) and surface materials must be designated as “presumed asbestos-
containing material” unless proven otherwise through sampling in accordance with the
standards of the Asbestos Hazard Emergency Response Act. Because the existing residence
12 PIERS Environmental Services. Addendum to Report of Subsurface Investigation and Transmittal of Additional
Results, 22561 Alcalde Road, Cupertino, California. January 8, 2018.
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was built prior to 1980, the potential exists that asbestos-containing materials were used in
the construction of the on-site residence.
Lead-based paint (LBP) is defined by federal guidelines as any paint, varnish, stain, or
other applied coating that has one milligram of lead per square centimeter or greater. Lead
is a highly toxic material that may cause a range of serious illnesses, and in some cases
death. In buildings constructed after 1978, the presence of LBP is unlikely. Structures built
prior to 1978, and especially prior to the 1960s, are expected to contain LBP. As previously
mentioned, the existing residence on the property was constructed in 1962, before the
phase-out of LBPs. Therefore, the potential exists that LBPs are present in the on-site
residence.
Based on the age of the existing on-site residence, asbestos-containing materials and LBP
are presumed to be present. The proposed project would include demolition of all on-site
structures. Therefore, without implementation of the appropriate safety measures, the
proposed project could potentially expose construction workers during demolition
activities to LBP and asbestos-containing materials.
Conclusion
Based on the above, development of the proposed project could create a significant hazard
to the public or the environment through reasonably foreseeable upset and accident
conditions involving the likely release of hazardous materials into the environment,
particularly associated with contaminated soils, asbestos-containing materials, and LBPs.
Therefore, a potentially significant impact would occur.
Mitigation Measure(s)
Implementation of the following mitigation measure would reduce the above impact to a
less-than-significant level.
VIII-1. Prior to issuance of any grading permits, the following measures shall be
reflected on the project grading and foundation plans, subject to review and
approval by the City Engineer:
• Six inches of soil shall be removed within the proposed
landscape areas along the northern and western boundaries of
the project site. The aforementioned landscape areas shall
subsequently be capped with a minimum of 0.5 feet of clean
imported fill.
• The top six inches of soils removed within the aforementioned
landscape areas shall be off-hauled by a licensed hazardous
waste contractor (Class A) and contractor personnel that have
completed 40-hour OSHA hazardous training, and shall be
disposed of appropriately in accordance with applicable
federal, State, and local regulations associated with hazardous
waste.
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The project applicant shall provide proof of implementation of the above
measures to the Community Development Department.
VIII-2. After demolition and removal of on-site structures and hardscapes, but
prior to initiation of grading, the applicant shall conduct additional soil
sampling within the previously inaccessible on-site areas to determine if the
underlying soils contain contaminants in excess of the applicable
Environmental Screening Levels (ESLs) set by the Regional Water Quality
Control Board. The results of soil sampling shall be submitted to the
Community Development Department prior to initiation of grading. If
contaminants are not detected above applicable ESLs, then further
mitigation is not required. If contaminants are detected above the
applicable ESLs, then the soils shall be remediated by off-hauling to a
licensed landfill facility.
VIII-3. Prior to issuance of a demolition permit for any on-site structures, the
project applicant shall consult with certified Asbestos and/or Lead Risk
Assessors to complete and submit for review to the Community
Development Department an asbestos and lead survey. If asbestos-
containing materials or lead-containing materials are not discovered
during the survey, further mitigation related to asbestos-containing
materials or lead containing materials shall not be required. If asbestos-
containing materials and/or lead-containing materials are discovered by
the survey, the project applicant shall prepare a work plan to demonstrate
how the on-site asbestos-containing materials and/or lead-containing
materials shall be removed in accordance with current California
Occupational Health and Safety (Cal-OSHA) Administration regulations
and disposed of in accordance with all CalEPA regulations, prior to the
demolition and/or removal of the on-site structures. The plan shall include
the requirement that work shall be conducted by a Cal-OSHA registered
asbestos and lead abatement contractor in accordance with Title 8 CCR
1529 and Title 8 CCR 1532.1 regarding asbestos and lead training,
engineering controls, and certifications. The applicant shall submit the
work plan to the Community Development Department for review and
approval. Materials containing more than one (1) percent asbestos that is
friable are also subject to BAAQMD regulations. Removal of materials
containing more than one (1) percent friable asbestos shall be completed in
accordance with BAAQMD Section 11-2-303.
c. The proposed project would not be located within one-quarter mile of a school. Therefore,
the project would have no impact related to hazardous emissions or the handling of
hazardous or acutely hazardous materials, substances, or waste within one-quarter mile of
an existing or proposed school.
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d. The proposed project would not be located on a site that is included on a list of hazardous
materials sites compiled pursuant to Government Code Section 65962.5.13 Therefore, the
project would not create a significant hazard to the public or the environment related to
such, and no impact would occur.
e,f. The nearest airport to the project site is the San Jose International Airport, located
approximately 8.2 miles northeast of the site. As such, the proposed project site is not
located within two miles of any public airports or private airstrips and does not fall within
an airport land use plan area. Therefore, no impact related to a safety hazard for people
residing or working in the project area would occur related to such.
g. The City of Cupertino Office of Emergency Services is responsible for coordinating agency
response to disasters or other large‐scale emergencies in the City of Cupertino, with
assistance from the Santa Clara County Office of Emergency Services and the Santa Clara
County Fire Department (SCCFD). The Cupertino Emergency Operations Plan establishes
policy direction for emergency planning, mitigation, response, and recovery activities
within the City.14
Implementation of the proposed project would include widening of the Alcalde Road right-
of-way by ten feet at the widest point (an approximately 370-square-foot area) along the
project frontage, however, such modifications would not physically interfere with the
Emergency Operations Plan, particularly with identified emergency routes. Furthermore,
the proposed project would not include land uses or operations that could impair
implementation of the plan. Therefore, the proposed project would not interfere with an
emergency evacuation or response plan, and a less-than-significant impact would occur.
h. According to the California Department of Forestry and Fire Protection (CAL FIRE) Fire
and Resource Assessment Program, the proposed project site is not located within a Very
High Fire Hazard Severity Zone.15 In addition, the site is currently developed, surrounded
by existing development, and is not located adjacent to wildlands. Therefore, the proposed
project would not expose people or structures to the risk of loss, injury or death involving
wildland fires, including where wildlands are adjacent to urbanized areas or where
residences are intermixed with wildlands, and a less-than-significant impact would occur.
13 California Department of Toxic Substances Control. Hazardous Waste and Substances Site List. Available at:
http://www.dtsc.ca.gov/SiteCleanup/Cortese_List.cfm. Accessed March 2017.
14 City of Cupertino. Emergency Operations Plan. September 2005.
15 California Department of Forestry and Fire Protection. Santa Clara County, Very High Fire Hazard Severity
Zones in LRA. October 8, 2008.
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IX. HYDROLOGY AND WATER QUALITY.
Would the project:
Potentially
Significant
Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-Than-
Significant
Impact
No
Impact
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 (i.e., 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 or 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 floodplain, 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 floodplain 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 by seiche, tsunami, or mudflow?
Discussion
a,f. The following section describes the project’s consistency with applicable water quality
standards and waste discharge requirements during construction and operation.
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Construction
The proposed project site is currently developed with a residential use. As such, the site
contains a substantial amount of impervious areas. Nonetheless, during the early stages of
construction activities, topsoil would be exposed due to grading of the site. After grading
and prior to overlaying the ground surface with impervious surfaces and structures, the
potential exists for wind and water erosion to discharge sediment and/or urban pollutants
into stormwater runoff, which could adversely affect water quality downstream.
The State Water Resources Control Board (SWRCB) regulates stormwater discharges
associated with construction activities where clearing, grading, or excavation results in a
land disturbance of one or more acres. The project site is 19,562 square feet (0.45-acre),
and, thus, construction activities would not be regulated by the SWRCB. However, the
City’s Municipal Code requires applicants to provide and comply with an Interim Erosion
and Sediment Control Plan (Interim Plan). The Interim Plan shall show the location of
erosion control measures and erosion control planting shall be shown on the site
map/grading plan. The applicant shall provide the following information with respect to
conditions existing on the site during land-disturbing or filling activities or stockpiling of
soil:
1. A delineation and brief description of the measures to be undertaken to retain
sediment on the site, including, but not limited to, the designs and specifications or
berms and sediment detention basins, and a schedule for their maintenance and
upkeep;
2. A delineation and brief description of the surface runoff and erosion control
measures to be implemented, including, but not limited, to types and methods of
applying mulches, and designs and specifications for diverters, dikes and drains,
and a schedule for their maintenance and upkeep;
3. A delineation and brief description of the vegetative measures to be undertaken,
including, but not limited to, seeding methods, and type, location and extent of
preexisting and undisturbed vegetation types, and a schedule for maintenance and
upkeep.
Because the project would comply with the City’s interim erosion control requirements,
the project would not violate any water quality standards or waste discharge requirements,
or otherwise degrade water quality, during construction.
Operation
The proposed residential use would not involve operations typically associated with the
generation or discharge of polluted water. Thus, typical operations on the project site would
not violate any water quality standards or waste discharge requirements, nor degrade water
quality. However, the potential for urban runoff would be increased with the addition of
impervious surfaces on the site, which could contain pollutants if the runoff comes into
contact with vehicle fluids on parking surfaces and/or landscape fertilizers and herbicides
prior to reaching downstream waters.
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44 January 2018
As of December 1, 2012, detached single-family homes that create or replace 2,500 square
feet or more of impervious surface are required by the City of Cupertino to install one or
more of the following design measures:
• Direct roof runoff onto vegetated areas (standard condition of approval, unless
infeasible);
• Direct roof runoff into cisterns or rain barrels for reuse;
• Direct runoff from sidewalks, walkways, and/or patios onto vegetated areas;
• Direct runoff from driveways and/or uncovered parking lots onto vegetated areas;
• Construct sidewalks, walkways and/or patios with permeable surface; or
• Construct bike lanes, driveways and or uncovered parking lots with permeable
surfaces.
As discussed previously, the proposed project would include a series of downspouts and
storm drains that capture runoff created by impervious areas on the project site. Runoff
from the downspouts would enter a six-inch perforated pipe continuing into a bubbler drain
system that would collect and route the water onto vegetated areas in the front yards of the
proposed residences. The proposed drainage system would satisfy City requirements by
routing on-site runoff through vegetated areas prior to entering the City’s storm drain
system. Therefore, during operation, the project would comply with all relevant water
quality standards and waste discharge requirements, and, thus, would not degrade water
quality during operation.
Conclusion
Based on the above, the project would comply with all applicable water quality and waste
discharge regulations during construction and operation, and would not involve uses
associated with the generation or discharge of polluted water. Therefore, a less-than-
significant impact would occur related to a violation of water quality standards or waste
discharge requirements or degradation of water quality.
b. As discussed previously, the project site is currently developed with an existing residence.
The proposed project site would not substantially increase demand for water supplies
associated with the site, including groundwater, and the proposed on-site drainage system
would allow for stormwater to percolate into the underlying soils, contributing to the
recharge of groundwater. Therefore, the proposed project would not substantially deplete
groundwater supplies or interfere substantially with groundwater recharge, and a less-than-
significant impact would occur.
c-e. The proposed project site is currently developed with an existing residence and other
impervious surfaces such as a driveway, a concrete patio, and shed. As such, development
of the proposed project would not result in a substantial increase in impervious surfaces or
runoff from what currently exists on-site. In addition, as discussed above, the project would
include a drainage system that would manage all on-site runoff without directly connecting
to the City’s existing stormwater drainage system. Runoff entering the perforated drainage
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Initial Study/Mitigated Negative Declaration
45 January 2018
pipes and the bubbler drain system would be able to infiltrate the soil and erosion, siltation,
and/or flooding would not occur.
In conclusion, the proposed project would not substantially alter the existing drainage
pattern of the site or area in a manner which would result in erosion, siltation, or flooding
on- or off-site, or 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. Consequently, the proposed project would result in a less-than-
significant impact related to such.
g-i. According to the City’s General Plan,16 as well as the Federal Emergency Management
Agency (FEMA) Flood Insurance Rate Map (FIRM) Number 06085C0204H,17 the
proposed project site is located in Zone X, which is an area of minimal flood hazard, outside
of the 100-year floodplain. As a result, the project would not place housing or structures
within the 100-year floodplain, nor 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. Therefore, no impact would result.
j. Tsunamis are defined as sea waves created by undersea fault movement, whereas a seiche
is a long-wavelength, large-scale wave action set up in a closed body of water such as a
lake or reservoir. Tsunamis typically affect coastlines and areas up to one-quarter mile
inland. The project area is located over 20 miles from the Pacific Ocean. Due to the
project’s distance from the coast, the project site would not be exposed to flooding risks
associated with tsunamis. Seiches do not pose a risk to the proposed project, as the project
site is not located in close proximity to any large closed bodies of water. Mudflows
typically occur on steep, unstable slopes. Given that the proposed project site is relatively
flat and not located on a slope, mudflows would not pose an issue. Based on the above, no
impact would occur related to inundation by seiche, tsunami, or mudflow.
16 City of Cupertino. General Plan: Community Vision 2015 – 2040 [pg. E-5]. Adopted October 20, 2015.
17 Federal Emergency Management Agency. FEMA’s National Flood Hazard Layer (Official), Panel
#06085C0208H. Available at:
http://fema.maps.arcgis.com/home/webmap/viewer.html?webmap=cbe088e7c8704464aa0fc34eb99e7f30&exte
nt=-122.05675800688134,37.31906767684711,-122.0534481609565,37.32047549983092. Accessed October
2017.
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X. LAND USE AND PLANNING.
Would the project:
Potentially
Significant
Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-Than-
Significant
Impact
No
Impact
a. Physically divide an established community?
b. Conflict with any applicable land use plans,
policies, or regulations 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 communities conservation plan?
Discussion
a. A project risks dividing an established community if the project would introduce
infrastructure or alter land use so as to change the land use conditions in the surrounding
community, or isolate an existing land use. The proposed project site currently contains a
single-family residence, which would be demolished as part of the proposed project. Given
that the proposed project would include redevelopment of the site with two new single-
family residences, the proposed project would not alter the land use of the site.
Accordingly, the proposed project would not change the land use conditions in the area or
isolate an existing land use. In addition, the project would be consistent with the site’s
existing zoning and General Plan land use designations. As such, the proposed project
would not physically divide an established community and a less-than-significant impact
would occur.
b. The City of Cupertino General Plan designates the 19,562-square-foot site as Low/Medium
Density (5-10 du/ac), and the site is currently zoned Single-Family Residential (R1-7.5).
The proposed project would include division of the site into two approximately 8,892-
square-foot lots and dedication of approximately 370 square feet of land to the City to allow
for the widening of the Alcalde Road right-of-way along the project frontage. The two new
lots would maintain the existing zoning and General Plan land use designations for the site,
and would be consistent with Sections 19.28.050 and 19.28.060 of the City’s Municipal
Code relating to zoning districts and site development regulations. Therefore, the project
would not conflict with any applicable land use plans, policies, or regulations 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. As a result, the proposed project would result in a less-
than-significant impact.
c. As discussed previously, the project site is not located in an area with an approved
HCP/NCCP. As a result, no impact would occur.
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XI. MINERAL RESOURCES.
Would the project:
Potentially
Significant
Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-Than-
Significant Impact
No
Impact
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. The proposed project site is located in a developed area and is currently developed with
residential use. According to the City’s General Plan, the project site is located in an area
which is unsuitable for mineral extraction.18 Therefore, no impact to mineral resources
would occur as a result of the proposed project.
18 City of Cupertino. General Plan: Community Vision 2015 – 2040 [pg. ES-10]. Adopted October 20, 2015.
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XII. NOISE.
Would the project result in:
Potentially
Significant
Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-Than-
Significant Impact
No
Impact
a. Exposure of persons to or generation of noise
levels in excess of standards established in the local
general plan or noise ordinance, or applicable
standards of other agencies?
b. Exposure of persons to or generation of excessive
groundborne vibration or groundborne noise
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,c. The existing noise environment of the site is currently defined by traffic noise on Alcalde
Road. Such traffic is primarily generated by the surrounding residences in the project
vicinity, as well as the occupied single-family residence currently located on the project
site. The proposed project would include demolition of the existing on-site structures and
redevelopment of the site with two single-family two-story residences. The project could
be considered to result in a potentially significant impact if the net increase in traffic
generated by the proposed project would cause an exceedance of noise levels established
in the City’s Municipal Code or an increase in the ambient noise levels in the project
vicinity.
As discussed in the Transportation and Circulation section of this IS/MND, the proposed
project would be anticipated to generate a total of 19 ADT. A total of 19 new vehicle trips
spread over a 24-hour period would not result in a substantial permanent increase in
ambient noise levels in the project vicinity above levels existing without the project.
Furthermore, approximately half of the trips generated by the project would replace trips
currently generated by the occupied single-family residence on the project site. Therefore,
given that the proposed project would not substantially increase the number of vehicle trips
associated with the project site, the project would not result in the exposure of persons to
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49 January 2018
or generation of noise levels in excess of standards established in City of Cupertino
Municipal Code, or substantially increase ambient noise levels in the project vicinity above
levels existing without the project. Thus, a less-than-significant impact would occur.
b. Heavy-duty construction equipment would be used during construction of the proposed
project (e.g., tractors, pavers, bulldozers). Such equipment has the potential to generate
groundborne vibration. Levels of vibration include imperceptible vibrations at low levels,
low rumbling and minor vibration at moderate levels, and structural or architectural
damage at high levels. For structural damage, the California Department of Transportation
(Caltrans) uses a vibration limit of 0.5 inches per second, peak particle velocity (in/sec,
PPV) for buildings structurally sound and designed to modern engineering standards, and
0.2 in/sec PPV for buildings that are found to be structurally sound but where structural
damage is a major concern. The threshold of 0.2 in/sec PPV is also used by Caltrans as the
threshold for human annoyance caused by vibration. Although all surrounding structures
are assumed to be structurally sound, the 0.2 in/sec PPV threshold offers a conservative
value with regard to structural damage and is used as the threshold of significance for the
analysis within this IS/MND.
The primary vibration-generating activities associated with the project would occur during
demolition of the existing on-site structures, construction of the two proposed single-family
residences, and widening of the Alcalde Road right-of-way. Table 5 below presents typical
vibration levels that could be expected from construction equipment at a distance of 25
feet.
Table 5
Vibration Source Levels for Construction Equipment
Equipment PPV at 25 ft (in/sec)
Large Bulldozer 0.089
Caisson drilling 0.089
Loaded trucks 0.076
Jackhammer 0.035
Small bulldozer 0.003
Source: Caltrans, Transportation and Construction Vibration Guidance Manual, September 2013.
The most significant source of ground-borne vibrations during project construction would
be the use of large bulldozers, which, as shown above, would generate vibrations of
approximately 0.089 in/sec PPV at a distance of 25 feet.19 The nearest buildings relative to
the proposed project site are the existing single-family residences located to the north, east,
and west of the site. The residences are situated approximately 15 feet at the closest point
from the nearest proposed construction areas. Using the maximum vibration level
anticipated during construction of 0.089 in/sec PPV at 25 feet and adjusting for a distance
of 15 feet,20 the maximum vibration levels anticipated at the nearest residences would be
approximately 0.16 in/sec PPV during construction activities associated with the project,
19 California Department of Transportation. Transportation and Construction Vibration, Guidance Manual.
September 2013.
20 California Department of Transportation. Transportation and Construction Vibration, Guidance Manual
[Equation 12, pg. 37]. September 2013.
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which would be below the applicable 0.2 in/sec PPV threshold. As such, groundborne
vibrations associated with development on the project site would not damage any existing
buildings. Additionally, construction activities would be temporary in nature and would be
limited to normal daytime working hours in accordance with Section 10.48.053 of the
City’s Municipal Code. Therefore, a less-than-significant impact would occur related to
exposure of persons to or generation of excessive groundborne vibration or groundborne
noise levels.
d. During demolition of the existing on-site structures, construction of the proposed
residences, and widening of the Alcalde Road right-of-way, noise from such activities
would temporarily add to the noise environment in the project vicinity. Noise would also
be generated during the construction phase by truck traffic associated with transport of
heavy materials and equipment to and from the project site. However, per Section
10.48.053 of the City’s Municipal Code, grading, construction, and demolition activities
are permitted to exceed the City’s established noise limits during daytime hours provided
that any piece of equipment involved in such activities has high-quality noise mufflers and
abatement devices installed, is in good condition, and the activities meet certain established
criteria. Compliance with the Municipal Code requirements would be verified as part of
the City’s standard conditions of approval.
Furthermore, noise associated with construction activities would be temporary, would
occur intermittently throughout implementation of the proposed project, and would occur
on a relatively small scale. Thus, while demolition and construction activities associated
with the project could result in temporary increases in noise levels at nearby noise-sensitive
receptors, such increases would not be substantial, would be minimized through
compliance with the City’s Municipal Code, and would be typical of residential
construction activities. Therefore, a less-than-significant impact would occur.
e,f. The project site is located approximately 8.2 miles southwest of the nearest airport, which
is the San Jose International Airport. Given the distance between the airport and the project
site, noise levels resulting from aircraft traffic at the nearest airport would be negligible at
the proposed project site. Therefore, a less-than-significant impact would occur.
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51 January 2018
XIII. POPULATION AND HOUSING.
Would the project:
Potentially
Significant
Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-Than-
Significant
Impact
No
Impact
a. Induce substantial population growth in an area,
either directly (for example, by proposing new
homes and businesses) or indirectly (e.g., through
projects in an undeveloped area or extension of
major 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. The proposed project would include the demolition of the existing on-site residence and
the construction of two new single-family homes. The increase of one home would not
result in a substantial increase in population, and, thus, the project would not be considered
to induce substantial population growth through the construction of new homes. In
addition, the project would be consistent with the existing zoning and General Plan land
use designations for the site. Consequently, a less-than-significant impact would occur
with regard to the project inducing substantial population growth.
b,c. The proposed project currently contains a single-family residence. The on-site structure
would be demolished as part of the proposed project, and the site would be redeveloped
with two new single-family residences. Given that the project would provide new housing
to replace the existing residence, the proposed project would not displace a substantial
number of existing housing or people and would not necessitate the construction of
replacement housing elsewhere. Therefore, a less-than-significant impact would occur.
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52 January 2018
XIV. PUBLIC SERVICES.
Would the project result in substantial adverse physical
impacts associated with the provision of new or
physically altered governmental facilities, need for new
or physically altered governmental facilities, the
construction of which could cause significant
environmental impacts, in order to maintain acceptable
service ratios, response times or other performance
objectives for any of the public services:
Potentially Significant
Impact
Less-Than-
Significant with
Mitigation Incorporated
Less-
Than-Significant
Impact
No Impact
a. Fire protection?
b. Police protection?
c. Schools?
d. Parks?
e. Other Public Facilities?
Discussion
a. Fire protection services to the project area are provided by the Santa Clara County Fire
Department (SCCFD), which serves Santa Clara County and the communities of Campbell,
Cupertino, Los Altos, Los Altos Hills, Los Gatos, Monte Sereno, and Saratoga. The
SCCFD operates 17 fire stations; the Cupertino Fire Station, located at 20215 Stevens
Creek Boulevard, currently serves the project site. The SCCFD would continue to provide
service following construction of the proposed project. Given that the proposed project
would be consistent with the existing land uses on the site and the General Plan land use
designation for the site, provision of fire protection services to the project site has been
previously anticipated by the City. In addition, demand for fire protection services would
not substantially increase, as the site is currently developed with a residential use.
Per Section 16.40.060 of the City’s Municipal Code, the proposed project would be
required to pay applicable fire protection fees to the SCCFD. In addition, the proposed
residential buildings would be constructed in accordance with the fire protection
requirements of the 2016 California Fire Code, which contain provisions to minimize fire
hazard risks. Therefore, the proposed project would have a less-than-significant impact
related to the need for new or physically altered fire protection facilities, the construction
of which could cause significant environmental impacts.
b. The City of Cupertino contracts with the Santa Clara County Sheriff’s Office (Sheriff’s
Office) and the West Valley Patrol Division for police protection services. The West Valley
Patrol Division is headquartered at the Westside Sheriff’s Substation at 1601 South De
Anza Boulevard in Cupertino. Given that the proposed project site is already developed
with a residential use and provided with police protection services, and the project would
be consistent with the City’s General Plan land use designation, the project would not
substantially increase the demand for police protection services at the site from what
currently occurs or what has been anticipated by the City for the site. Therefore, the
proposed project would have a less-than-significant impact related to the need for new or
physically altered police protection facilities, the construction of which could cause
significant environmental impacts.
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53 January 2018
c. Public schools in the City of Cupertino are managed by the Cupertino Union School
District (CUSD) and the Fremont Union High School District (FUHSD). The proposed
project would be required to pay the school impact fees specified in the City’s General
Plan.21 As noted in the General Plan, in accordance with Senate Bill 50, school impact
mitigation fees are presumed to fully mitigate any school impacts associated with
development. Because the project applicant would be required to pay the applicable school
impact fees, the proposed project would result in a less-than-significant impact regarding
an increase in demand for schools.
d,e. The City of Cupertino assesses park maintenance fees for new residential development
based on the density of the proposed development. Given that the proposed project would
include the construction of single-family housing, the project applicant would be required
to pay the appropriate park maintenance fee to the City. Pursuant to Section 14.05.060 of
the City’s Municipal Code, the final amount of the fee would be determined by the Director
of Public Works. The in-lieu fees would fund improvements to and expansion of park
facilities within the City. Therefore, the proposed project would have a less-than-
significant impact related to the need for new or physically altered parks or other public
facilities, the construction of which could cause significant environmental impacts.
21 City of Cupertino. General Plan: Community Vision 2015 – 2040 [pg. B-83]. Adopted October 20, 2015.
Alcalde Road Lot Split Project
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XV. RECREATION.
Would the project:
Potentially
Significant Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-
Than-
Significant
Impact
No Impact
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?
Discussion
a,b. The proposed project would include the construction of two new single-family homes.
Residents of the proposed homes would likely use existing neighborhood, regional, parks
and/or other recreational facilities. However, given that the project site is currently
developed with a residential use, the proposed project would not be anticipated to
substantially increase the demand for parks or other recreational facilities associated with
the site. In addition, development of the site with residential uses has been previously
anticipated in the City’s General Plan. As discussed in Section XIV, Public Services,
above, the project applicant would be required to pay applicable park maintenance fees to
the City.
Therefore, the proposed project would not be expected to result in substantial physical
deterioration of any existing neighborhood or regional parks or other recreational facilities,
and would not require the construction or expansion of facilities which might have an
adverse physical effect on the environment. Thus, a less-than-significant impact would
occur.
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XVI. TRANSPORTATION AND CIRCULATION.
Would the project:
Potentially
Significant
Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-Than-
Significant Impact
No
Impact
a. Conflict with an applicable plan, ordinance or policy
establishing measures of effectiveness for the
performance of the circulation system, taking into
account all modes of transportation including mass
transit and non-motorized travel and relevant
components of the circulation system, including but
not limited to intersections, streets, highways and
freeways, pedestrian and bicycle paths, and mass
transit?
b. Conflict with an applicable congestion management
program, including, but not limited to level of
service standards and travel demand measures, or
other standards 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 design features
(e.g., sharp curves or dangerous intersections) or
incompatible uses (e.g., farm equipment)?
e. Result in inadequate emergency access?
f. Conflict with adopted policies, plans, or programs
regarding public transit, bicycle, or pedestrian
facilities, or otherwise decrease the performance or
safety of such facilities?
Discussion
a,b. The Institute of Traffic Engineer’s (ITE) Trip Generation Handbook was used to estimate
weekday AM, PM, and daily trip generation forecasts for the proposed project based on the
proposed single-family residential land use.22 As shown in Table 6 below, implementation
of the proposed project would be expected to result in a total of 19 ADT, with two trips
occurring during the AM peak hour and two trips occurring during the PM peak hour.
Table 6
Weekday Project Trip Generation Rates and Estimates
Units Rate
Daily
Trips
AM Peak Hour PM Peak Hour
Rate In Out Total Rate In Out Total
2 9.52 19 0.75 1 1 2 1.00 1 1 2
Source: Institute of Transportation Engineers, 2012.
22 Institute of Transportation Engineers. Trip Generation Handbook, 9th Edition. September 2012.
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According to the Santa Clara VTA, projects anticipated to generate fewer than 100 peak
hour trips are not subject to review by the VTA.23 Because the project would generate fewer
than 100 peak hour trips, preparation of a traffic impact study for the proposed project is
not required and the project is not subject to review by the VTA.
Because the project would result in less than 100 peak hour trips, and traffic associated
with buildout of the site has been previously analyzed in the General Plan EIR, the project
would not be expected to adversely impact levels of service at nearby signalized
intersections or roadways. Therefore, the proposed project would not conflict with an
applicable plan, ordinance, or policy establishing measures of effectiveness for the
performance of the circulation system, and would not conflict with the applicable CMP.
Consequently, a less-than-significant impact would occur.
c. The proposed project is not located near an airport and does not include any improvements
to airports or a change in air traffic patterns. The nearest airport to the site is San Jose
International Airport, located approximately 8.2 miles northeast of the site. Therefore,
because the proposed project would not result in a change in air traffic patterns, including
either an increase in air traffic levels or a change in location that results in substantial safety
risks, no impact would occur.
d,e. The proposed project would include widening of the Alcalde Road right-of-way by ten feet
at the widest point (an approximately 370-square-foot area) along the project frontage,
which would be dedicated to the City. Both of the proposed single-family residences would
include paved driveways, which would connect to the widened roadway. Thus, adequate
emergency access would be provided to the site. In addition, as previously mentioned,
sidewalks do not currently exist along the frontage of the project site; however,
implementation of the proposed project would include the addition of a sidewalk that would
help to improve the currently discontinuous sidewalks along Alcalde Road. Thus, the
addition of a sidewalk along the frontage of the project site would increase the pedestrian
network in the project vicinity, and, thus, would increase access to the project site.
Residential uses associated with the proposed project would be considered consistent and
compatible with the existing residential development in the surrounding area. Thus,
implementation of the proposed project would not substantially increase hazards due to
design features. In addition, emergency vehicles would have reasonable access to the
proposed residences from the existing roadways and project frontage. Based on the above,
the project would not substantially increase hazards due to design features or incompatible
uses, and emergency access to the site would be adequate. Therefore, the project would
result in a less-than-significant impact.
f. The proposed project site is located in a residential subdivision. While bike lanes are not
present on the surrounding roadway network, bicycle travel in the project vicinity remains
a viable transportation option due to the low levels of traffic experienced on the
neighborhood roadways. As noted above, the proposed project would include the provision
of a sidewalk at the project frontage, which would improve the pedestrian network in the
23 Santa Clara Valley Transportation Authority. 2013 Congestion Management Program [pg. 12]. October 2013.
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57 January 2018
area. Thus, the project would be consistent with Policy M-3.2 of the City’s General Plan,
which requires new development and redevelopment to increase pedestrian connectivity.
The nearest transit stop relative to the project site is located at the intersection of Stevens
Creek Boulevard and South Foothill Boulevard, approximately less than half a mile north
of the project site. Thus, residents of the proposed single-family homes would be provided
with reasonable access to the City’s public transportation system.
Given the presence of existing transit and pedestrian facilities, and incorporation of a new
sidewalk along the project frontage, the project would result in a less-than-significant
impact with respect to conflicts with adopted policies, plans, or programs regarding public
transit, bicycle, or pedestrian facilities, or with respect to degradation of such facilities.
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
58 January 2018
XVII. TRIBAL CULTURAL RESOURCES.
Would the project cause a substantial adverse change
in the significance of a tribal cultural resource, defined
in Public Resources Code section 21074 as either a
site, feature, place, cultural landscape that is
geographically defined in terms of the size and scope of
the landscape, sacred place, or object with cultural
value to a California Native American Tribe, and that
is:
Potentially Significant
Impact
Less-Than-
Significant with
Mitigation Incorporated
Less-
Than-Significant
Impact
No Impact
a. Listed or eligible for listing in the California
Register of Historical Resources, or in a local
register of historical resources as defined in Public
Resources Code section 5020.1(k)?
b. A resource determined by the lead agency, in its
discretion and supported by substantial evidence, to
be significant pursuant to criteria set forth in
subdivision (c) of Public Resources Code Section
5024.1? In applying the criteria set forth in
subdivision (c) of Public Resources Code Section
5024.1, the lead agency shall consider the
significance of the resource to a California Native
American tribe.
Discussion
a,b. As discussed in Section V, Cultural Resources, of this IS/MND, the proposed project site
does not contain any existing permanent structures or any other known resources listed or
eligible for listing in the CRHR, NRHP, or in a local register of historical resources as
defined in Public Resources Code section 5020.1(k), and does not contain known resources
that could be considered historic pursuant to the criteria set forth in subdivision (c) of
Public Resources Code Section 5024.1. Furthermore, the potential for unrecorded Native
American resources to exist within the project site is relatively low based on the highly-
disturbed nature of the site, and Native American resources have not been identified within
the vicinity of the project site. Given that the project would be required to comply with the
City’s standard conditions of approval regarding cultural resources, construction of the
proposed project would not result in a substantial adverse change in the significance of a
tribal cultural resource, and a less-than-significant impact to tribal cultural resources could
occur.
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
59 January 2018
XVIII. UTILITIES AND SERVICE SYSTEMS.
Would the project:
Potentially
Significant
Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-Than-
Significant
Impact
No
Impact
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?
Discussion
a,b,e. Wastewater service at the proposed project site would be provided by the Cupertino
Sanitary District (CSD). The proposed project would connect to the CSD’s existing
sanitary sewer system by way of connections to existing sewer lines in Alcalde Road. The
CSD collection system directs wastewater to the San Jose/Santa Clara Water Pollution
Control Plant (SJ/SCWPCP), a joint powers authority.
The project area is currently provided sewer services by the CSD, including the existing
on-site residence. The proposed project would demolish the existing residence and
construct two new single-family residences. The net increase of one residence on the
project site would not substantially increase the demand for wastewater services associated
with the site and would not affect the available capacity of the SJ/SCWPCP. Furthermore,
wastewater generation associated with buildout of the project site has been anticipated by
the City, as the project would be consistent with the existing General Plan land use
designation of the site. In addition, the proposed project would involve typical household
wastewater generation, which would not have the potential to exceed any wastewater
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
60 January 2018
treatment requirements of the RWQCB. Based on the above, the proposed project would
result in a less-than-significant impact related to wastewater.
c. As discussed in further detail in Section IX, Hydrology and Water Quality, of this IS/MND,
the proposed project would not include direct connections to the City’s existing stormwater
drainage facilities, and, thus, would not necessitate the expansion of such facilities. Rather,
runoff from the downspouts would enter a new six-inch perforated pipe continuing into a
bubbler drain system that would collect and route the water onto vegetated areas in the
front yard areas of the proposed residences. Therefore, the proposed project would have a
less-than-significant impact with respect to requiring or resulting in the construction of
new stormwater drainage facilities or expansion of existing facilities, the construction of
which could cause significant environmental effects.
d. Water service to the proposed project site is currently provided under contract with San
Jose Water. The proposed project would connect to existing water supply infrastructure
located in Alcalde Road. The proposed project would demolish the existing on-site
residence and construct two new single-family residences. The net increase of one
residence on the project site would not substantially increase the demand for water supplies
associated with the site. In addition, the proposed project would be consistent with the
existing General Plan land use designation of the site, and, thus, the City has previously
anticipated the demand for water supplies associated with buildout of the site. Therefore,
sufficient water supplies would be available to serve the proposed project from existing
entitlements and resources, and new or expanded entitlements would not be needed. In
addition, the project would not necessitate the construction of new water supply facilities.
Thus, a less-than-significant impact would occur.
f,g. The City contracts with Recology South Bay (Recology) for solid waste collection services.
All non-hazardous solid waste collected under the Recology franchise agreement is taken
to Newby Island Sanitary Landfill for processing. Under the agreement recyclable
materials also are handled by Recology. Of the 27,593 tons of solid waste disposed in 2012,
25,440 tons, or 92 percent was disposed of at the Newby Island Landfill. The Monterey
Peninsula Landfill, the Guadalupe Sanitary Landfill and the Altamont Landfill and
Resource Recovery Facility accepted the next highest amounts of waste from Cupertino,
respectively receiving 1,260 tons (4.6 percent of total), 321 tons (1.2 percent) and 238 tons
(0.9 percent) of all waste. Per the General Plan EIR, sufficient landfill capacity is available
to serve buildout of the General Plan.
The proposed project site is currently developed with a residential use and is designated as
Low/Medium Density Residential in the City’s General Plan. The proposed project would
demolish the existing on-site residence and construct two new single-family residences.
The net increase of one residence on the project site would not substantially increase the
solid waste generation associated with the site. In addition, the proposed project would be
consistent with the General Plan land use designation for the site. As such, generation of
solid waste associated with the project site has been previously anticipated by the City.
Based on the above, the project would not increase solid waste generation such that the
capacity of any landfills serving the City would be exceeded. In addition, construction and
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
61 January 2018
any demolition debris associated with the project would be subject to Chapter 16.72 of the
City’s Municipal Code, which requires that a minimum of 60 percent of construction and
demolition debris be diverted from a landfill. Therefore, the proposed project would be
served by a landfill with sufficient permitted capacity to accommodate the project’s solid
waste disposal needs and would comply with federal, State, and local statutes and
regulations related to solid waste. Accordingly, a less-than-significant impact would
occur.
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
62 January 2018
XIX. MANDATORY FINDINGS OF
SIGNIFICANCE.
Potentially
Significant
Impact
Less-Than-
Significant
with
Mitigation
Incorporated
Less-Than-
Significant
Impact
No
Impact
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 cumulatively considerable?
("Cumulatively considerable" means that the
incremental effects of a project are considerable
when viewed in connection with the effects of past
projects, the effects of other current projects, and
the effects of probable future projects)?
c. Does the project have environmental effects which
will cause substantial adverse effects on human
beings, either directly or indirectly?
Discussion
a. As described throughout this IS/MND, impacts related to special-status plants and cultural
resources would be less than significant. In addition, potential impacts related to reducing
the habitat for nesting migratory birds would be reduced to less-than-significant levels with
implementation of the mitigation measures required by this IS/MND, as well as compliance
with General Plan policies and all applicable sections of the Municipal Code. As such,
development of the proposed project would not: 1) degrade the quality of the environment;
2) substantially reduce or impact the habitat of fish or wildlife species; 3) cause fish or
wildlife populations to drop below self-sustaining levels; 4) threaten to eliminate a plant or
animal community; 5) reduce the number or restrict the range of a rare or endangered plant
or animal; or 6) eliminate important examples of the major periods of California history or
prehistory. Therefore, a less-than-significant impact would occur.
b. The proposed project in conjunction with other development within the City of Cupertino
could incrementally contribute to cumulative impacts in the area. However, as
demonstrated in this IS/MND, all potential environmental impacts that could occur as a
result of project implementation would be reduced to a less-than-significant level with
implementation of project-specific mitigation measures, as well as compliance with
applicable General Plan policies and Municipal Code standards. In addition, the site has
been anticipated by the City for residential development. Thus, buildout of the site with
residential uses was considered in the cumulative analysis of buildout of the General Plan.
When viewed in conjunction with other closely related past, present, or reasonably
foreseeable future projects, development of the proposed project would not substantially
Alcalde Road Lot Split Project
Initial Study/Mitigated Negative Declaration
63 January 2018
contribute to cumulative impacts in the City of Cupertino, and the project’s cumulative
impact would be less than significant.
c. As described in this IS/MND, implementation of the proposed project could result in
potential impacts related to existing soil contamination at the site. However, the proposed
project would implement the project-specific mitigation measures within this IS/MND, as
well as applicable General Plan policies, which would ensure that any potential direct or
indirect effects to human beings would be reduced to less-than-significant levels.
Therefore, the proposed project would have a less-than-significant impact.
APPENDIX
AIR QUALITY AND GHG MODELING RESULTS
Project Characteristics - Intensity Factors for CO2 adjusted based on PG&E RPS reductions
Land Use - Applicant provided
Construction Phase - Applicant provided
Grading - Applicant provided
Demolition - Applicant provided
Vehicle Trips - Based on ITE rate (Single Family Homes, 210)
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population
Single Family Housing 2.00 Dwelling Unit 0.45 3,600.00 6
1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
5
Wind Speed (m/s)Precipitation Freq (Days)2.2 64
1.3 User Entered Comments & Non-Default Data
1.0 Project Characteristics
Utility Company Pacific Gas & Electric Company
2019Operational Year
CO2 Intensity
(lb/MWhr)
409.81 0.029CH4 Intensity
(lb/MWhr)
0.006N2O Intensity
(lb/MWhr)
Alcalde Road Lot Split
Bay Area AQMD Air District, Annual
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Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
2.0 Emissions Summary
Table Name Column Name Default Value New Value
tblConstructionPhase NumDays 5.00 100.00
tblConstructionPhase PhaseEndDate 11/21/2018 11/28/2018
tblConstructionPhase PhaseEndDate 11/7/2018 11/14/2018
tblConstructionPhase PhaseEndDate 11/14/2018 6/27/2018
tblConstructionPhase PhaseStartDate 11/15/2018 7/12/2018
tblConstructionPhase PhaseStartDate 6/21/2018 6/28/2018
tblConstructionPhase PhaseStartDate 11/8/2018 6/21/2018
tblGrading AcresOfGrading 0.50 0.45
tblGrading MaterialExported 0.00 363.00
tblGrading MaterialImported 0.00 130.00
tblLandUse LotAcreage 0.65 0.45
tblProjectCharacteristics CO2IntensityFactor 641.35 409.81
tblVehicleTrips ST_TR 9.91 9.52
tblVehicleTrips SU_TR 8.62 9.52
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Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
2.1 Overall Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year tons/yr MT/yr
2018 0.1046 0.7497 0.5547 8.7000e-
004
5.5200e-
003
0.0483 0.0538 1.3600e-
003
0.0451 0.0465 0.0000 78.4962 78.4962 0.0197 0.0000 78.9878
Maximum 0.1046 0.7497 0.5547 8.7000e-
004
5.5200e-
003
0.0483 0.0538 1.3600e-
003
0.0451 0.0465 0.0000 78.4962 78.4962 0.0197 0.0000 78.9878
Unmitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year tons/yr MT/yr
2018 0.1046 0.7497 0.5547 8.7000e-
004
5.5200e-
003
0.0483 0.0538 1.3600e-
003
0.0451 0.0465 0.0000 78.4961 78.4961 0.0197 0.0000 78.9877
Maximum 0.1046 0.7497 0.5547 8.7000e-
004
5.5200e-
003
0.0483 0.0538 1.3600e-
003
0.0451 0.0465 0.0000 78.4961 78.4961 0.0197 0.0000 78.9877
Mitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
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Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Area 0.0288 4.3000e-
004
0.0321 4.0000e-
005
2.5500e-
003
2.5500e-
003
2.5500e-
003
2.5500e-
003
0.2542 0.0867 0.3409 5.0000e-
004
1.0000e-
005
0.3578
Energy 4.6000e-
004
3.9000e-
003
1.6600e-
003
2.0000e-
005
3.2000e-
004
3.2000e-
004
3.2000e-
004
3.2000e-
004
0.0000 7.4848 7.4848 3.0000e-
004
1.3000e-
004
7.5298
Mobile 6.0800e-
003
0.0287 0.0686 2.1000e-
004
0.0164 2.6000e-
004
0.0166 4.4000e-
003
2.5000e-
004
4.6400e-
003
0.0000 18.8212 18.8212 7.8000e-
004
0.0000 18.8408
Waste 0.0000 0.0000 0.0000 0.0000 0.5115 0.0000 0.5115 0.0302 0.0000 1.2673
Water 0.0000 0.0000 0.0000 0.0000 0.0413 0.1845 0.2259 4.2600e-
003
1.0000e-
004
0.3630
Total 0.0354 0.0331 0.1023 2.7000e-
004
0.0164 3.1300e-
003
0.0195 4.4000e-
003
3.1200e-
003
7.5100e-
003
0.8071 26.5772 27.3843 0.0361 2.4000e-
004
28.3588
Unmitigated Operational
Quarter Start Date End Date Maximum Unmitigated ROG + NOX (tons/quarter)Maximum Mitigated ROG + NOX (tons/quarter)
1 6-4-2018 9-3-2018 0.4626 0.4626
2 9-4-2018 9-30-2018 0.1440 0.1440
Highest 0.4626 0.4626
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Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Area 0.0288 4.3000e-
004
0.0321 4.0000e-
005
2.5500e-
003
2.5500e-
003
2.5500e-
003
2.5500e-
003
0.2542 0.0867 0.3409 5.0000e-
004
1.0000e-
005
0.3578
Energy 4.6000e-
004
3.9000e-
003
1.6600e-
003
2.0000e-
005
3.2000e-
004
3.2000e-
004
3.2000e-
004
3.2000e-
004
0.0000 7.4848 7.4848 3.0000e-
004
1.3000e-
004
7.5298
Mobile 6.0800e-
003
0.0287 0.0686 2.1000e-
004
0.0164 2.6000e-
004
0.0166 4.4000e-
003
2.5000e-
004
4.6400e-
003
0.0000 18.8212 18.8212 7.8000e-
004
0.0000 18.8408
Waste 0.0000 0.0000 0.0000 0.0000 0.5115 0.0000 0.5115 0.0302 0.0000 1.2673
Water 0.0000 0.0000 0.0000 0.0000 0.0413 0.1845 0.2259 4.2600e-
003
1.0000e-
004
0.3630
Total 0.0354 0.0331 0.1023 2.7000e-
004
0.0164 3.1300e-
003
0.0195 4.4000e-
003
3.1200e-
003
7.5100e-
003
0.8071 26.5772 27.3843 0.0361 2.4000e-
004
28.3588
Mitigated Operational
3.0 Construction Detail
Construction Phase
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
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Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Demolition Demolition 6/4/2018 6/15/2018 5 10
2 Site Preparation Site Preparation 6/16/2018 6/18/2018 5 1
3 Grading Grading 6/19/2018 6/20/2018 5 2
4 Building Construction Building Construction 6/28/2018 11/14/2018 5 100
5 Paving Paving 6/21/2018 6/27/2018 5 5
6 Architectural Coating Architectural Coating 7/12/2018 11/28/2018 5 100
OffRoad Equipment
Residential Indoor: 7,290; Residential Outdoor: 2,430; Non-Residential Indoor: 0; Non-Residential Outdoor: 0; Striped Parking Area: 0
(Architectural Coating – sqft)
Acres of Grading (Site Preparation Phase): 0.45
Acres of Grading (Grading Phase): 0
Acres of Paving: 0
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Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor
Architectural Coating Air Compressors 1 6.00 78 0.48
Paving Cement and Mortar Mixers 4 6.00 9 0.56
Demolition Concrete/Industrial Saws 1 8.00 81 0.73
Grading Concrete/Industrial Saws 1 8.00 81 0.73
Building Construction Cranes 1 4.00 231 0.29
Building Construction Forklifts 2 6.00 89 0.20
Site Preparation Graders 1 8.00 187 0.41
Paving Pavers 1 7.00 130 0.42
Paving Rollers 1 7.00 80 0.38
Demolition Rubber Tired Dozers 1 1.00 247 0.40
Grading Rubber Tired Dozers 1 1.00 247 0.40
Building Construction Tractors/Loaders/Backhoes 2 8.00 97 0.37
Demolition Tractors/Loaders/Backhoes 2 6.00 97 0.37
Grading Tractors/Loaders/Backhoes 2 6.00 97 0.37
Paving Tractors/Loaders/Backhoes 1 7.00 97 0.37
Site Preparation Tractors/Loaders/Backhoes 1 8.00 97 0.37
Trips and VMT
Phase Name Offroad Equipment
Count
Worker Trip
Number
Vendor Trip
Number
Hauling Trip
Number
Worker Trip
Length
Vendor Trip
Length
Hauling Trip
Length
Worker Vehicle
Class
Vendor
Vehicle Class
Hauling
Vehicle Class
Demolition 4 10.00 0.00 23.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Site Preparation 2 5.00 0.00 62.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Grading 4 10.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Building Construction 5 1.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Paving 7 18.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Architectural Coating 1 0.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
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Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
3.2 Demolition - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 2.5400e-
003
0.0000 2.5400e-
003
3.8000e-
004
0.0000 3.8000e-
004
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 5.3200e-
003
0.0472 0.0389 6.0000e-
005
3.1100e-
003
3.1100e-
003
2.9700e-
003
2.9700e-
003
0.0000 5.3041 5.3041 1.0200e-
003
0.0000 5.3297
Total 5.3200e-
003
0.0472 0.0389 6.0000e-
005
2.5400e-
003
3.1100e-
003
5.6500e-
003
3.8000e-
004
2.9700e-
003
3.3500e-
003
0.0000 5.3041 5.3041 1.0200e-
003
0.0000 5.3297
Unmitigated Construction On-Site
3.1 Mitigation Measures Construction
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Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
3.2 Demolition - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 1.1000e-
004
3.7900e-
003
7.2000e-
004
1.0000e-
005
1.9000e-
004
2.0000e-
005
2.1000e-
004
5.0000e-
005
1.0000e-
005
7.0000e-
005
0.0000 0.8999 0.8999 5.0000e-
005
0.0000 0.9011
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 2.0000e-
004
1.5000e-
004
1.5400e-
003
0.0000 4.0000e-
004
0.0000 4.0000e-
004
1.1000e-
004
0.0000 1.1000e-
004
0.0000 0.3684 0.3684 1.0000e-
005
0.0000 0.3687
Total 3.1000e-
004
3.9400e-
003
2.2600e-
003
1.0000e-
005
5.9000e-
004
2.0000e-
005
6.1000e-
004
1.6000e-
004
1.0000e-
005
1.8000e-
004
0.0000 1.2684 1.2684 6.0000e-
005
0.0000 1.2698
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 2.5400e-
003
0.0000 2.5400e-
003
3.8000e-
004
0.0000 3.8000e-
004
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 5.3200e-
003
0.0472 0.0389 6.0000e-
005
3.1100e-
003
3.1100e-
003
2.9700e-
003
2.9700e-
003
0.0000 5.3041 5.3041 1.0200e-
003
0.0000 5.3296
Total 5.3200e-
003
0.0472 0.0389 6.0000e-
005
2.5400e-
003
3.1100e-
003
5.6500e-
003
3.8000e-
004
2.9700e-
003
3.3500e-
003
0.0000 5.3041 5.3041 1.0200e-
003
0.0000 5.3296
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 9 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
3.2 Demolition - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 1.1000e-
004
3.7900e-
003
7.2000e-
004
1.0000e-
005
1.9000e-
004
2.0000e-
005
2.1000e-
004
5.0000e-
005
1.0000e-
005
7.0000e-
005
0.0000 0.8999 0.8999 5.0000e-
005
0.0000 0.9011
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 2.0000e-
004
1.5000e-
004
1.5400e-
003
0.0000 4.0000e-
004
0.0000 4.0000e-
004
1.1000e-
004
0.0000 1.1000e-
004
0.0000 0.3684 0.3684 1.0000e-
005
0.0000 0.3687
Total 3.1000e-
004
3.9400e-
003
2.2600e-
003
1.0000e-
005
5.9000e-
004
2.0000e-
005
6.1000e-
004
1.6000e-
004
1.0000e-
005
1.8000e-
004
0.0000 1.2684 1.2684 6.0000e-
005
0.0000 1.2698
Mitigated Construction Off-Site
3.3 Site Preparation - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 2.7000e-
004
0.0000 2.7000e-
004
3.0000e-
005
0.0000 3.0000e-
005
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 3.9000e-
004
4.8800e-
003
2.1300e-
003
0.0000 2.1000e-
004
2.1000e-
004
1.9000e-
004
1.9000e-
004
0.0000 0.4458 0.4458 1.4000e-
004
0.0000 0.4492
Total 3.9000e-
004
4.8800e-
003
2.1300e-
003
0.0000 2.7000e-
004
2.1000e-
004
4.8000e-
004
3.0000e-
005
1.9000e-
004
2.2000e-
004
0.0000 0.4458 0.4458 1.4000e-
004
0.0000 0.4492
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 10 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
3.3 Site Preparation - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 3.0000e-
004
0.0102 1.9500e-
003
3.0000e-
005
5.2000e-
004
4.0000e-
005
5.6000e-
004
1.4000e-
004
4.0000e-
005
1.8000e-
004
0.0000 2.4259 2.4259 1.3000e-
004
0.0000 2.4291
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 1.0000e-
005
1.0000e-
005
8.0000e-
005
0.0000 2.0000e-
005
0.0000 2.0000e-
005
1.0000e-
005
0.0000 1.0000e-
005
0.0000 0.0184 0.0184 0.0000 0.0000 0.0184
Total 3.1000e-
004
0.0102 2.0300e-
003
3.0000e-
005
5.4000e-
004
4.0000e-
005
5.8000e-
004
1.5000e-
004
4.0000e-
005
1.9000e-
004
0.0000 2.4443 2.4443 1.3000e-
004
0.0000 2.4475
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 2.7000e-
004
0.0000 2.7000e-
004
3.0000e-
005
0.0000 3.0000e-
005
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 3.9000e-
004
4.8800e-
003
2.1300e-
003
0.0000 2.1000e-
004
2.1000e-
004
1.9000e-
004
1.9000e-
004
0.0000 0.4458 0.4458 1.4000e-
004
0.0000 0.4492
Total 3.9000e-
004
4.8800e-
003
2.1300e-
003
0.0000 2.7000e-
004
2.1000e-
004
4.8000e-
004
3.0000e-
005
1.9000e-
004
2.2000e-
004
0.0000 0.4458 0.4458 1.4000e-
004
0.0000 0.4492
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 11 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
3.3 Site Preparation - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 3.0000e-
004
0.0102 1.9500e-
003
3.0000e-
005
5.2000e-
004
4.0000e-
005
5.6000e-
004
1.4000e-
004
4.0000e-
005
1.8000e-
004
0.0000 2.4259 2.4259 1.3000e-
004
0.0000 2.4291
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 1.0000e-
005
1.0000e-
005
8.0000e-
005
0.0000 2.0000e-
005
0.0000 2.0000e-
005
1.0000e-
005
0.0000 1.0000e-
005
0.0000 0.0184 0.0184 0.0000 0.0000 0.0184
Total 3.1000e-
004
0.0102 2.0300e-
003
3.0000e-
005
5.4000e-
004
4.0000e-
005
5.8000e-
004
1.5000e-
004
4.0000e-
005
1.9000e-
004
0.0000 2.4443 2.4443 1.3000e-
004
0.0000 2.4475
Mitigated Construction Off-Site
3.4 Grading - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 7.5000e-
004
0.0000 7.5000e-
004
4.1000e-
004
0.0000 4.1000e-
004
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 1.0600e-
003
9.4300e-
003
7.7800e-
003
1.0000e-
005
6.2000e-
004
6.2000e-
004
5.9000e-
004
5.9000e-
004
0.0000 1.0608 1.0608 2.0000e-
004
0.0000 1.0659
Total 1.0600e-
003
9.4300e-
003
7.7800e-
003
1.0000e-
005
7.5000e-
004
6.2000e-
004
1.3700e-
003
4.1000e-
004
5.9000e-
004
1.0000e-
003
0.0000 1.0608 1.0608 2.0000e-
004
0.0000 1.0659
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 12 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
3.4 Grading - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 4.0000e-
005
3.0000e-
005
3.1000e-
004
0.0000 8.0000e-
005
0.0000 8.0000e-
005
2.0000e-
005
0.0000 2.0000e-
005
0.0000 0.0737 0.0737 0.0000 0.0000 0.0737
Total 4.0000e-
005
3.0000e-
005
3.1000e-
004
0.0000 8.0000e-
005
0.0000 8.0000e-
005
2.0000e-
005
0.0000 2.0000e-
005
0.0000 0.0737 0.0737 0.0000 0.0000 0.0737
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 7.5000e-
004
0.0000 7.5000e-
004
4.1000e-
004
0.0000 4.1000e-
004
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 1.0600e-
003
9.4300e-
003
7.7800e-
003
1.0000e-
005
6.2000e-
004
6.2000e-
004
5.9000e-
004
5.9000e-
004
0.0000 1.0608 1.0608 2.0000e-
004
0.0000 1.0659
Total 1.0600e-
003
9.4300e-
003
7.7800e-
003
1.0000e-
005
7.5000e-
004
6.2000e-
004
1.3700e-
003
4.1000e-
004
5.9000e-
004
1.0000e-
003
0.0000 1.0608 1.0608 2.0000e-
004
0.0000 1.0659
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 13 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
3.4 Grading - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 4.0000e-
005
3.0000e-
005
3.1000e-
004
0.0000 8.0000e-
005
0.0000 8.0000e-
005
2.0000e-
005
0.0000 2.0000e-
005
0.0000 0.0737 0.0737 0.0000 0.0000 0.0737
Total 4.0000e-
005
3.0000e-
005
3.1000e-
004
0.0000 8.0000e-
005
0.0000 8.0000e-
005
2.0000e-
005
0.0000 2.0000e-
005
0.0000 0.0737 0.0737 0.0000 0.0000 0.0737
Mitigated Construction Off-Site
3.5 Building Construction - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.0542 0.5516 0.3876 5.7000e-
004
0.0354 0.0354 0.0326 0.0326 0.0000 52.0058 52.0058 0.0162 0.0000 52.4106
Total 0.0542 0.5516 0.3876 5.7000e-
004
0.0354 0.0354 0.0326 0.0326 0.0000 52.0058 52.0058 0.0162 0.0000 52.4106
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 14 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
3.5 Building Construction - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 2.0000e-
004
1.5000e-
004
1.5400e-
003
0.0000 4.0000e-
004
0.0000 4.0000e-
004
1.1000e-
004
0.0000 1.1000e-
004
0.0000 0.3684 0.3684 1.0000e-
005
0.0000 0.3687
Total 2.0000e-
004
1.5000e-
004
1.5400e-
003
0.0000 4.0000e-
004
0.0000 4.0000e-
004
1.1000e-
004
0.0000 1.1000e-
004
0.0000 0.3684 0.3684 1.0000e-
005
0.0000 0.3687
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.0542 0.5516 0.3876 5.7000e-
004
0.0354 0.0354 0.0326 0.0326 0.0000 52.0058 52.0058 0.0162 0.0000 52.4105
Total 0.0542 0.5516 0.3876 5.7000e-
004
0.0354 0.0354 0.0326 0.0326 0.0000 52.0058 52.0058 0.0162 0.0000 52.4105
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 15 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
3.5 Building Construction - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 2.0000e-
004
1.5000e-
004
1.5400e-
003
0.0000 4.0000e-
004
0.0000 4.0000e-
004
1.1000e-
004
0.0000 1.1000e-
004
0.0000 0.3684 0.3684 1.0000e-
005
0.0000 0.3687
Total 2.0000e-
004
1.5000e-
004
1.5400e-
003
0.0000 4.0000e-
004
0.0000 4.0000e-
004
1.1000e-
004
0.0000 1.1000e-
004
0.0000 0.3684 0.3684 1.0000e-
005
0.0000 0.3687
Mitigated Construction Off-Site
3.6 Paving - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 2.3000e-
003
0.0219 0.0181 3.0000e-
005
1.2800e-
003
1.2800e-
003
1.1800e-
003
1.1800e-
003
0.0000 2.4270 2.4270 6.8000e-
004
0.0000 2.4441
Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 2.3000e-
003
0.0219 0.0181 3.0000e-
005
1.2800e-
003
1.2800e-
003
1.1800e-
003
1.1800e-
003
0.0000 2.4270 2.4270 6.8000e-
004
0.0000 2.4441
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 16 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
3.6 Paving - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 1.8000e-
004
1.4000e-
004
1.3900e-
003
0.0000 3.6000e-
004
0.0000 3.6000e-
004
9.0000e-
005
0.0000 1.0000e-
004
0.0000 0.3316 0.3316 1.0000e-
005
0.0000 0.3318
Total 1.8000e-
004
1.4000e-
004
1.3900e-
003
0.0000 3.6000e-
004
0.0000 3.6000e-
004
9.0000e-
005
0.0000 1.0000e-
004
0.0000 0.3316 0.3316 1.0000e-
005
0.0000 0.3318
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 2.3000e-
003
0.0219 0.0181 3.0000e-
005
1.2800e-
003
1.2800e-
003
1.1800e-
003
1.1800e-
003
0.0000 2.4270 2.4270 6.8000e-
004
0.0000 2.4441
Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 2.3000e-
003
0.0219 0.0181 3.0000e-
005
1.2800e-
003
1.2800e-
003
1.1800e-
003
1.1800e-
003
0.0000 2.4270 2.4270 6.8000e-
004
0.0000 2.4441
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 17 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
3.6 Paving - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 1.8000e-
004
1.4000e-
004
1.3900e-
003
0.0000 3.6000e-
004
0.0000 3.6000e-
004
9.0000e-
005
0.0000 1.0000e-
004
0.0000 0.3316 0.3316 1.0000e-
005
0.0000 0.3318
Total 1.8000e-
004
1.4000e-
004
1.3900e-
003
0.0000 3.6000e-
004
0.0000 3.6000e-
004
9.0000e-
005
0.0000 1.0000e-
004
0.0000 0.3316 0.3316 1.0000e-
005
0.0000 0.3318
Mitigated Construction Off-Site
3.7 Architectural Coating - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Archit. Coating 0.0253 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 0.0149 0.1003 0.0927 1.5000e-
004
7.5300e-
003
7.5300e-
003
7.5300e-
003
7.5300e-
003
0.0000 12.7663 12.7663 1.2100e-
003
0.0000 12.7966
Total 0.0403 0.1003 0.0927 1.5000e-
004
7.5300e-
003
7.5300e-
003
7.5300e-
003
7.5300e-
003
0.0000 12.7663 12.7663 1.2100e-
003
0.0000 12.7966
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 18 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
3.7 Architectural Coating - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Archit. Coating 0.0253 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 0.0149 0.1003 0.0927 1.5000e-
004
7.5300e-
003
7.5300e-
003
7.5300e-
003
7.5300e-
003
0.0000 12.7663 12.7663 1.2100e-
003
0.0000 12.7966
Total 0.0403 0.1003 0.0927 1.5000e-
004
7.5300e-
003
7.5300e-
003
7.5300e-
003
7.5300e-
003
0.0000 12.7663 12.7663 1.2100e-
003
0.0000 12.7966
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 19 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
4.0 Operational Detail - Mobile
4.1 Mitigation Measures Mobile
3.7 Architectural Coating - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 20 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Mitigated 6.0800e-
003
0.0287 0.0686 2.1000e-
004
0.0164 2.6000e-
004
0.0166 4.4000e-
003
2.5000e-
004
4.6400e-
003
0.0000 18.8212 18.8212 7.8000e-
004
0.0000 18.8408
Unmitigated 6.0800e-
003
0.0287 0.0686 2.1000e-
004
0.0164 2.6000e-
004
0.0166 4.4000e-
003
2.5000e-
004
4.6400e-
003
0.0000 18.8212 18.8212 7.8000e-
004
0.0000 18.8408
4.2 Trip Summary Information
4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
Single Family Housing 19.04 19.04 19.04 43,975 43,975
Total 19.04 19.04 19.04 43,975 43,975
Miles Trip %Trip Purpose %
Land Use H-W or C-W H-S or C-C H-O or C-NW H-W or C-W H-S or C-C H-O or C-NW Primary Diverted Pass-by
Single Family Housing 10.80 4.80 5.70 31.00 15.00 54.00 86 11 3
5.0 Energy Detail
4.4 Fleet Mix
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH
Single Family Housing 0.570523 0.041853 0.194077 0.115893 0.018544 0.005373 0.016909 0.024079 0.002502 0.002562 0.005975 0.000872 0.000837
Historical Energy Use: N
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 21 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Electricity
Mitigated
0.0000 0.0000 0.0000 0.0000 0.0000 2.9677 2.9677 2.1000e-
004
4.0000e-
005
2.9859
Electricity
Unmitigated
0.0000 0.0000 0.0000 0.0000 0.0000 2.9677 2.9677 2.1000e-
004
4.0000e-
005
2.9859
NaturalGas
Mitigated
4.6000e-
004
3.9000e-
003
1.6600e-
003
2.0000e-
005
3.2000e-
004
3.2000e-
004
3.2000e-
004
3.2000e-
004
0.0000 4.5171 4.5171 9.0000e-
005
8.0000e-
005
4.5440
NaturalGas
Unmitigated
4.6000e-
004
3.9000e-
003
1.6600e-
003
2.0000e-
005
3.2000e-
004
3.2000e-
004
3.2000e-
004
3.2000e-
004
0.0000 4.5171 4.5171 9.0000e-
005
8.0000e-
005
4.5440
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr tons/yr MT/yr
Single Family
Housing
84647.5 4.6000e-
004
3.9000e-
003
1.6600e-
003
2.0000e-
005
3.2000e-
004
3.2000e-
004
3.2000e-
004
3.2000e-
004
0.0000 4.5171 4.5171 9.0000e-
005
8.0000e-
005
4.5440
Total 4.6000e-
004
3.9000e-
003
1.6600e-
003
2.0000e-
005
3.2000e-
004
3.2000e-
004
3.2000e-
004
3.2000e-
004
0.0000 4.5171 4.5171 9.0000e-
005
8.0000e-
005
4.5440
Unmitigated
5.1 Mitigation Measures Energy
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 22 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr tons/yr MT/yr
Single Family
Housing
84647.5 4.6000e-
004
3.9000e-
003
1.6600e-
003
2.0000e-
005
3.2000e-
004
3.2000e-
004
3.2000e-
004
3.2000e-
004
0.0000 4.5171 4.5171 9.0000e-
005
8.0000e-
005
4.5440
Total 4.6000e-
004
3.9000e-
003
1.6600e-
003
2.0000e-
005
3.2000e-
004
3.2000e-
004
3.2000e-
004
3.2000e-
004
0.0000 4.5171 4.5171 9.0000e-
005
8.0000e-
005
4.5440
Mitigated
5.3 Energy by Land Use - Electricity
Electricity
Use
Total CO2 CH4 N2O CO2e
Land Use kWh/yr MT/yr
Single Family
Housing
15965 2.9677 2.1000e-
004
4.0000e-
005
2.9859
Total 2.9677 2.1000e-
004
4.0000e-
005
2.9859
Unmitigated
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 23 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
6.1 Mitigation Measures Area
6.0 Area Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Mitigated 0.0288 4.3000e-
004
0.0321 4.0000e-
005
2.5500e-
003
2.5500e-
003
2.5500e-
003
2.5500e-
003
0.2542 0.0867 0.3409 5.0000e-
004
1.0000e-
005
0.3578
Unmitigated 0.0288 4.3000e-
004
0.0321 4.0000e-
005
2.5500e-
003
2.5500e-
003
2.5500e-
003
2.5500e-
003
0.2542 0.0867 0.3409 5.0000e-
004
1.0000e-
005
0.3578
5.3 Energy by Land Use - Electricity
Electricity
Use
Total CO2 CH4 N2O CO2e
Land Use kWh/yr MT/yr
Single Family
Housing
15965 2.9677 2.1000e-
004
4.0000e-
005
2.9859
Total 2.9677 2.1000e-
004
4.0000e-
005
2.9859
Mitigated
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 24 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory tons/yr MT/yr
Architectural
Coating
2.5300e-
003
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
0.0141 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 0.0118 2.6000e-
004
0.0171 4.0000e-
005
2.4700e-
003
2.4700e-
003
2.4700e-
003
2.4700e-
003
0.2542 0.0624 0.3166 4.8000e-
004
1.0000e-
005
0.3330
Landscaping 4.6000e-
004
1.7000e-
004
0.0149 0.0000 8.0000e-
005
8.0000e-
005
8.0000e-
005
8.0000e-
005
0.0000 0.0243 0.0243 2.0000e-
005
0.0000 0.0249
Total 0.0288 4.3000e-
004
0.0321 4.0000e-
005
2.5500e-
003
2.5500e-
003
2.5500e-
003
2.5500e-
003
0.2542 0.0867 0.3409 5.0000e-
004
1.0000e-
005
0.3578
Unmitigated
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 25 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
7.1 Mitigation Measures Water
7.0 Water Detail
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory tons/yr MT/yr
Architectural
Coating
2.5300e-
003
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
0.0141 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 0.0118 2.6000e-
004
0.0171 4.0000e-
005
2.4700e-
003
2.4700e-
003
2.4700e-
003
2.4700e-
003
0.2542 0.0624 0.3166 4.8000e-
004
1.0000e-
005
0.3330
Landscaping 4.6000e-
004
1.7000e-
004
0.0149 0.0000 8.0000e-
005
8.0000e-
005
8.0000e-
005
8.0000e-
005
0.0000 0.0243 0.0243 2.0000e-
005
0.0000 0.0249
Total 0.0288 4.3000e-
004
0.0321 4.0000e-
005
2.5500e-
003
2.5500e-
003
2.5500e-
003
2.5500e-
003
0.2542 0.0867 0.3409 5.0000e-
004
1.0000e-
005
0.3578
Mitigated
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 26 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
Total CO2 CH4 N2O CO2e
Category MT/yr
Mitigated 0.2259 4.2600e-
003
1.0000e-
004
0.3630
Unmitigated 0.2259 4.2600e-
003
1.0000e-
004
0.3630
7.2 Water by Land Use
Indoor/Out
door Use
Total CO2 CH4 N2O CO2e
Land Use Mgal MT/yr
Single Family
Housing
0.130308 /
0.0821507
0.2259 4.2600e-
003
1.0000e-
004
0.3630
Total 0.2259 4.2600e-
003
1.0000e-
004
0.3630
Unmitigated
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 27 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
8.1 Mitigation Measures Waste
7.2 Water by Land Use
Indoor/Out
door Use
Total CO2 CH4 N2O CO2e
Land Use Mgal MT/yr
Single Family
Housing
0.130308 /
0.0821507
0.2259 4.2600e-
003
1.0000e-
004
0.3630
Total 0.2259 4.2600e-
003
1.0000e-
004
0.3630
Mitigated
8.0 Waste Detail
Total CO2 CH4 N2O CO2e
MT/yr
Mitigated 0.5115 0.0302 0.0000 1.2673
Unmitigated 0.5115 0.0302 0.0000 1.2673
Category/Year
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 28 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
8.2 Waste by Land Use
Waste
Disposed
Total CO2 CH4 N2O CO2e
Land Use tons MT/yr
Single Family
Housing
2.52 0.5115 0.0302 0.0000 1.2673
Total 0.5115 0.0302 0.0000 1.2673
Unmitigated
Waste
Disposed
Total CO2 CH4 N2O CO2e
Land Use tons MT/yr
Single Family
Housing
2.52 0.5115 0.0302 0.0000 1.2673
Total 0.5115 0.0302 0.0000 1.2673
Mitigated
9.0 Operational Offroad
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 29 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
11.0 Vegetation
10.0 Stationary Equipment
Fire Pumps and Emergency Generators
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type
Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type
User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:58 AMPage 30 of 30
Alcalde Road Lot Split - Bay Area AQMD Air District, Annual
Project Characteristics - Intensity Factors for CO2 adjusted based on PG&E RPS reductions
Land Use - Applicant provided
Construction Phase - Applicant provided
Grading - Applicant provided
Demolition - Applicant provided
Vehicle Trips - Based on ITE rate (Single Family Homes, 210)
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population
Single Family Housing 2.00 Dwelling Unit 0.45 3,600.00 6
1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
5
Wind Speed (m/s)Precipitation Freq (Days)2.2 64
1.3 User Entered Comments & Non-Default Data
1.0 Project Characteristics
Utility Company Pacific Gas & Electric Company
2019Operational Year
CO2 Intensity
(lb/MWhr)
409.81 0.029CH4 Intensity
(lb/MWhr)
0.006N2O Intensity
(lb/MWhr)
Alcalde Road Lot Split
Bay Area AQMD Air District, Summer
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 1 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
2.0 Emissions Summary
Table Name Column Name Default Value New Value
tblConstructionPhase NumDays 5.00 100.00
tblConstructionPhase PhaseEndDate 11/21/2018 11/28/2018
tblConstructionPhase PhaseEndDate 11/7/2018 11/14/2018
tblConstructionPhase PhaseEndDate 11/14/2018 6/27/2018
tblConstructionPhase PhaseStartDate 11/15/2018 7/12/2018
tblConstructionPhase PhaseStartDate 6/21/2018 6/28/2018
tblConstructionPhase PhaseStartDate 11/8/2018 6/21/2018
tblGrading AcresOfGrading 0.50 0.45
tblGrading MaterialExported 0.00 363.00
tblGrading MaterialImported 0.00 130.00
tblLandUse LotAcreage 0.65 0.45
tblProjectCharacteristics CO2IntensityFactor 641.35 409.81
tblVehicleTrips ST_TR 9.91 9.52
tblVehicleTrips SU_TR 8.62 9.52
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 2 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
2.1 Overall Construction (Maximum Daily Emission)
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2018 1.8945 29.7849 9.6389 0.0607 1.6571 0.8593 2.1559 0.4356 0.8026 1.0304 0.0000 6,411.069
1
6,411.069
1
0.5838 0.0000 6,425.663
6
Maximum 1.8945 29.7849 9.6389 0.0607 1.6571 0.8593 2.1559 0.4356 0.8026 1.0304 0.0000 6,411.069
1
6,411.069
1
0.5838 0.0000 6,425.663
6
Unmitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2018 1.8945 29.7849 9.6389 0.0607 1.6571 0.8593 2.1559 0.4356 0.8026 1.0304 0.0000 6,411.069
1
6,411.069
1
0.5838 0.0000 6,425.663
6
Maximum 1.8945 29.7849 9.6389 0.0607 1.6571 0.8593 2.1559 0.4356 0.8026 1.0304 0.0000 6,411.069
1
6,411.069
1
0.5838 0.0000 6,425.663
6
Mitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 3 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 2.1686 0.0418 2.8464 5.0600e-
003
0.3800 0.3800 0.3800 0.3800 40.7567 12.6501 53.4067 0.0507 2.8800e-
003
55.5309
Energy 2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
Mobile 0.0380 0.1524 0.3891 1.2000e-
003
0.0935 1.4400e-
003
0.0949 0.0250 1.3600e-
003
0.0264 120.7671 120.7671 4.7800e-
003
120.8866
Total 2.2091 0.2156 3.2446 6.4000e-
003
0.0935 0.3831 0.4766 0.0250 0.3831 0.4081 40.7567 160.7008 201.4575 0.0560 3.3800e-
003
203.8632
Unmitigated Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 2.1686 0.0418 2.8464 5.0600e-
003
0.3800 0.3800 0.3800 0.3800 40.7567 12.6501 53.4067 0.0507 2.8800e-
003
55.5309
Energy 2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
Mobile 0.0380 0.1524 0.3891 1.2000e-
003
0.0935 1.4400e-
003
0.0949 0.0250 1.3600e-
003
0.0264 120.7671 120.7671 4.7800e-
003
120.8866
Total 2.2091 0.2156 3.2446 6.4000e-
003
0.0935 0.3831 0.4766 0.0250 0.3831 0.4081 40.7567 160.7008 201.4575 0.0560 3.3800e-
003
203.8632
Mitigated Operational
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 4 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
3.0 Construction Detail
Construction Phase
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Demolition Demolition 6/4/2018 6/15/2018 5 10
2 Site Preparation Site Preparation 6/16/2018 6/18/2018 5 1
3 Grading Grading 6/19/2018 6/20/2018 5 2
4 Building Construction Building Construction 6/28/2018 11/14/2018 5 100
5 Paving Paving 6/21/2018 6/27/2018 5 5
6 Architectural Coating Architectural Coating 7/12/2018 11/28/2018 5 100
OffRoad Equipment
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Residential Indoor: 7,290; Residential Outdoor: 2,430; Non-Residential Indoor: 0; Non-Residential Outdoor: 0; Striped Parking Area: 0
(Architectural Coating – sqft)
Acres of Grading (Site Preparation Phase): 0.45
Acres of Grading (Grading Phase): 0
Acres of Paving: 0
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 5 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor
Architectural Coating Air Compressors 1 6.00 78 0.48
Paving Cement and Mortar Mixers 4 6.00 9 0.56
Demolition Concrete/Industrial Saws 1 8.00 81 0.73
Grading Concrete/Industrial Saws 1 8.00 81 0.73
Building Construction Cranes 1 4.00 231 0.29
Building Construction Forklifts 2 6.00 89 0.20
Site Preparation Graders 1 8.00 187 0.41
Paving Pavers 1 7.00 130 0.42
Paving Rollers 1 7.00 80 0.38
Demolition Rubber Tired Dozers 1 1.00 247 0.40
Grading Rubber Tired Dozers 1 1.00 247 0.40
Building Construction Tractors/Loaders/Backhoes 2 8.00 97 0.37
Demolition Tractors/Loaders/Backhoes 2 6.00 97 0.37
Grading Tractors/Loaders/Backhoes 2 6.00 97 0.37
Paving Tractors/Loaders/Backhoes 1 7.00 97 0.37
Site Preparation Tractors/Loaders/Backhoes 1 8.00 97 0.37
Trips and VMT
Phase Name Offroad Equipment
Count
Worker Trip
Number
Vendor Trip
Number
Hauling Trip
Number
Worker Trip
Length
Vendor Trip
Length
Hauling Trip
Length
Worker Vehicle
Class
Vendor
Vehicle Class
Hauling
Vehicle Class
Demolition 4 10.00 0.00 23.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Site Preparation 2 5.00 0.00 62.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Grading 4 10.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Building Construction 5 1.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Paving 7 18.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Architectural Coating 1 0.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 6 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
3.2 Demolition - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.5085 0.0000 0.5085 0.0770 0.0000 0.0770 0.0000 0.0000
Off-Road 1.0643 9.4295 7.7762 0.0120 0.6228 0.6228 0.5943 0.5943 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Total 1.0643 9.4295 7.7762 0.0120 0.5085 0.6228 1.1313 0.0770 0.5943 0.6713 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Unmitigated Construction On-Site
3.1 Mitigation Measures Construction
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 7 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
3.2 Demolition - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0218 0.7425 0.1396 1.8700e-
003
0.0402 2.9800e-
003
0.0432 0.0110 2.8600e-
003
0.0139 199.7543 199.7543 0.0103 200.0107
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0421 0.0272 0.3350 8.8000e-
004
0.0822 5.5000e-
004
0.0827 0.0218 5.1000e-
004
0.0223 87.3564 87.3564 2.5500e-
003
87.4202
Total 0.0639 0.7697 0.4746 2.7500e-
003
0.1223 3.5300e-
003
0.1259 0.0328 3.3700e-
003
0.0362 287.1106 287.1106 0.0128 287.4309
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.5085 0.0000 0.5085 0.0770 0.0000 0.0770 0.0000 0.0000
Off-Road 1.0643 9.4295 7.7762 0.0120 0.6228 0.6228 0.5943 0.5943 0.0000 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Total 1.0643 9.4295 7.7762 0.0120 0.5085 0.6228 1.1313 0.0770 0.5943 0.6713 0.0000 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 8 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
3.2 Demolition - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0218 0.7425 0.1396 1.8700e-
003
0.0402 2.9800e-
003
0.0432 0.0110 2.8600e-
003
0.0139 199.7543 199.7543 0.0103 200.0107
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0421 0.0272 0.3350 8.8000e-
004
0.0822 5.5000e-
004
0.0827 0.0218 5.1000e-
004
0.0223 87.3564 87.3564 2.5500e-
003
87.4202
Total 0.0639 0.7697 0.4746 2.7500e-
003
0.1223 3.5300e-
003
0.1259 0.0328 3.3700e-
003
0.0362 287.1106 287.1106 0.0128 287.4309
Mitigated Construction Off-Site
3.3 Site Preparation - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.5330 0.0000 0.5330 0.0600 0.0000 0.0600 0.0000 0.0000
Off-Road 0.7858 9.7572 4.2514 9.7600e-
003
0.4180 0.4180 0.3846 0.3846 982.7113 982.7113 0.3059 990.3596
Total 0.7858 9.7572 4.2514 9.7600e-
003
0.5330 0.4180 0.9510 0.0600 0.3846 0.4445 982.7113 982.7113 0.3059 990.3596
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 9 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
3.3 Site Preparation - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.5872 20.0141 3.7621 0.0505 1.0831 0.0805 1.1636 0.2968 0.0770 0.3738 5,384.679
7
5,384.679
7
0.2766 5,391.594
0
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0211 0.0136 0.1675 4.4000e-
004
0.0411 2.8000e-
004
0.0414 0.0109 2.6000e-
004
0.0112 43.6782 43.6782 1.2800e-
003
43.7101
Total 0.6083 20.0277 3.9296 0.0509 1.1242 0.0807 1.2049 0.3077 0.0772 0.3849 5,428.357
9
5,428.357
9
0.2779 5,435.304
1
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.5330 0.0000 0.5330 0.0600 0.0000 0.0600 0.0000 0.0000
Off-Road 0.7858 9.7572 4.2514 9.7600e-
003
0.4180 0.4180 0.3846 0.3846 0.0000 982.7113 982.7113 0.3059 990.3596
Total 0.7858 9.7572 4.2514 9.7600e-
003
0.5330 0.4180 0.9510 0.0600 0.3846 0.4445 0.0000 982.7113 982.7113 0.3059 990.3596
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 10 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
3.3 Site Preparation - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.5872 20.0141 3.7621 0.0505 1.0831 0.0805 1.1636 0.2968 0.0770 0.3738 5,384.679
7
5,384.679
7
0.2766 5,391.594
0
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0211 0.0136 0.1675 4.4000e-
004
0.0411 2.8000e-
004
0.0414 0.0109 2.6000e-
004
0.0112 43.6782 43.6782 1.2800e-
003
43.7101
Total 0.6083 20.0277 3.9296 0.0509 1.1242 0.0807 1.2049 0.3077 0.0772 0.3849 5,428.357
9
5,428.357
9
0.2779 5,435.304
1
Mitigated Construction Off-Site
3.4 Grading - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.7528 0.0000 0.7528 0.4138 0.0000 0.4138 0.0000 0.0000
Off-Road 1.0643 9.4295 7.7762 0.0120 0.6228 0.6228 0.5943 0.5943 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Total 1.0643 9.4295 7.7762 0.0120 0.7528 0.6228 1.3755 0.4138 0.5943 1.0081 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 11 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
3.4 Grading - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0421 0.0272 0.3350 8.8000e-
004
0.0822 5.5000e-
004
0.0827 0.0218 5.1000e-
004
0.0223 87.3564 87.3564 2.5500e-
003
87.4202
Total 0.0421 0.0272 0.3350 8.8000e-
004
0.0822 5.5000e-
004
0.0827 0.0218 5.1000e-
004
0.0223 87.3564 87.3564 2.5500e-
003
87.4202
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.7528 0.0000 0.7528 0.4138 0.0000 0.4138 0.0000 0.0000
Off-Road 1.0643 9.4295 7.7762 0.0120 0.6228 0.6228 0.5943 0.5943 0.0000 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Total 1.0643 9.4295 7.7762 0.0120 0.7528 0.6228 1.3755 0.4138 0.5943 1.0081 0.0000 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 12 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
3.4 Grading - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0421 0.0272 0.3350 8.8000e-
004
0.0822 5.5000e-
004
0.0827 0.0218 5.1000e-
004
0.0223 87.3564 87.3564 2.5500e-
003
87.4202
Total 0.0421 0.0272 0.3350 8.8000e-
004
0.0822 5.5000e-
004
0.0827 0.0218 5.1000e-
004
0.0223 87.3564 87.3564 2.5500e-
003
87.4202
Mitigated Construction Off-Site
3.5 Building Construction - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.0848 11.0316 7.7512 0.0114 0.7087 0.7087 0.6520 0.6520 1,146.532
3
1,146.532
3
0.3569 1,155.455
5
Total 1.0848 11.0316 7.7512 0.0114 0.7087 0.7087 0.6520 0.6520 1,146.532
3
1,146.532
3
0.3569 1,155.455
5
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 13 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
3.5 Building Construction - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 4.2100e-
003
2.7200e-
003
0.0335 9.0000e-
005
8.2100e-
003
6.0000e-
005
8.2700e-
003
2.1800e-
003
5.0000e-
005
2.2300e-
003
8.7356 8.7356 2.6000e-
004
8.7420
Total 4.2100e-
003
2.7200e-
003
0.0335 9.0000e-
005
8.2100e-
003
6.0000e-
005
8.2700e-
003
2.1800e-
003
5.0000e-
005
2.2300e-
003
8.7356 8.7356 2.6000e-
004
8.7420
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.0848 11.0316 7.7512 0.0114 0.7087 0.7087 0.6520 0.6520 0.0000 1,146.532
3
1,146.532
3
0.3569 1,155.455
5
Total 1.0848 11.0316 7.7512 0.0114 0.7087 0.7087 0.6520 0.6520 0.0000 1,146.532
3
1,146.532
3
0.3569 1,155.455
5
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 14 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
3.5 Building Construction - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 4.2100e-
003
2.7200e-
003
0.0335 9.0000e-
005
8.2100e-
003
6.0000e-
005
8.2700e-
003
2.1800e-
003
5.0000e-
005
2.2300e-
003
8.7356 8.7356 2.6000e-
004
8.7420
Total 4.2100e-
003
2.7200e-
003
0.0335 9.0000e-
005
8.2100e-
003
6.0000e-
005
8.2700e-
003
2.1800e-
003
5.0000e-
005
2.2300e-
003
8.7356 8.7356 2.6000e-
004
8.7420
Mitigated Construction Off-Site
3.6 Paving - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.9202 8.7447 7.2240 0.0113 0.5109 0.5109 0.4735 0.4735 1,070.137
2
1,070.137
2
0.3017 1,077.679
8
Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 0.9202 8.7447 7.2240 0.0113 0.5109 0.5109 0.4735 0.4735 1,070.137
2
1,070.137
2
0.3017 1,077.679
8
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 15 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
3.6 Paving - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0758 0.0490 0.6030 1.5800e-
003
0.1479 1.0000e-
003
0.1489 0.0392 9.2000e-
004
0.0401 157.2415 157.2415 4.5900e-
003
157.3563
Total 0.0758 0.0490 0.6030 1.5800e-
003
0.1479 1.0000e-
003
0.1489 0.0392 9.2000e-
004
0.0401 157.2415 157.2415 4.5900e-
003
157.3563
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.9202 8.7447 7.2240 0.0113 0.5109 0.5109 0.4735 0.4735 0.0000 1,070.137
2
1,070.137
2
0.3017 1,077.679
8
Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 0.9202 8.7447 7.2240 0.0113 0.5109 0.5109 0.4735 0.4735 0.0000 1,070.137
2
1,070.137
2
0.3017 1,077.679
8
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 16 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
3.6 Paving - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0758 0.0490 0.6030 1.5800e-
003
0.1479 1.0000e-
003
0.1489 0.0392 9.2000e-
004
0.0401 157.2415 157.2415 4.5900e-
003
157.3563
Total 0.0758 0.0490 0.6030 1.5800e-
003
0.1479 1.0000e-
003
0.1489 0.0392 9.2000e-
004
0.0401 157.2415 157.2415 4.5900e-
003
157.3563
Mitigated Construction Off-Site
3.7 Architectural Coating - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 0.5068 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 0.2986 2.0058 1.8542 2.9700e-
003
0.1506 0.1506 0.1506 0.1506 281.4485 281.4485 0.0267 282.1171
Total 0.8055 2.0058 1.8542 2.9700e-
003
0.1506 0.1506 0.1506 0.1506 281.4485 281.4485 0.0267 282.1171
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 17 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
3.7 Architectural Coating - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 0.5068 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 0.2986 2.0058 1.8542 2.9700e-
003
0.1506 0.1506 0.1506 0.1506 0.0000 281.4485 281.4485 0.0267 282.1171
Total 0.8055 2.0058 1.8542 2.9700e-
003
0.1506 0.1506 0.1506 0.1506 0.0000 281.4485 281.4485 0.0267 282.1171
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 18 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
4.0 Operational Detail - Mobile
4.1 Mitigation Measures Mobile
3.7 Architectural Coating - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 19 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 0.0380 0.1524 0.3891 1.2000e-
003
0.0935 1.4400e-
003
0.0949 0.0250 1.3600e-
003
0.0264 120.7671 120.7671 4.7800e-
003
120.8866
Unmitigated 0.0380 0.1524 0.3891 1.2000e-
003
0.0935 1.4400e-
003
0.0949 0.0250 1.3600e-
003
0.0264 120.7671 120.7671 4.7800e-
003
120.8866
4.2 Trip Summary Information
4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
Single Family Housing 19.04 19.04 19.04 43,975 43,975
Total 19.04 19.04 19.04 43,975 43,975
Miles Trip %Trip Purpose %
Land Use H-W or C-W H-S or C-C H-O or C-NW H-W or C-W H-S or C-C H-O or C-NW Primary Diverted Pass-by
Single Family Housing 10.80 4.80 5.70 31.00 15.00 54.00 86 11 3
5.0 Energy Detail
4.4 Fleet Mix
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH
Single Family Housing 0.570523 0.041853 0.194077 0.115893 0.018544 0.005373 0.016909 0.024079 0.002502 0.002562 0.005975 0.000872 0.000837
Historical Energy Use: N
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 20 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
NaturalGas
Mitigated
2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
NaturalGas
Unmitigated
2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
Single Family
Housing
231.911 2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
Total 2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
Unmitigated
5.1 Mitigation Measures Energy
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 21 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
6.1 Mitigation Measures Area
6.0 Area Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 2.1686 0.0418 2.8464 5.0600e-
003
0.3800 0.3800 0.3800 0.3800 40.7567 12.6501 53.4067 0.0507 2.8800e-
003
55.5309
Unmitigated 2.1686 0.0418 2.8464 5.0600e-
003
0.3800 0.3800 0.3800 0.3800 40.7567 12.6501 53.4067 0.0507 2.8800e-
003
55.5309
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
Single Family
Housing
0.231911 2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
Total 2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
Mitigated
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 22 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
0.0139 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
0.0770 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 2.0726 0.0399 2.6806 5.0500e-
003
0.3791 0.3791 0.3791 0.3791 40.7567 12.3529 53.1096 0.0504 2.8800e-
003
55.2265
Landscaping 5.0800e-
003
1.9200e-
003
0.1658 1.0000e-
005
9.1000e-
004
9.1000e-
004
9.1000e-
004
9.1000e-
004
0.2971 0.2971 2.9000e-
004
0.3044
Total 2.1686 0.0418 2.8464 5.0600e-
003
0.3800 0.3800 0.3800 0.3800 40.7567 12.6500 53.4067 0.0507 2.8800e-
003
55.5309
Unmitigated
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 23 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
8.1 Mitigation Measures Waste
7.1 Mitigation Measures Water
7.0 Water Detail
8.0 Waste Detail
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
0.0139 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
0.0770 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 2.0726 0.0399 2.6806 5.0500e-
003
0.3791 0.3791 0.3791 0.3791 40.7567 12.3529 53.1096 0.0504 2.8800e-
003
55.2265
Landscaping 5.0800e-
003
1.9200e-
003
0.1658 1.0000e-
005
9.1000e-
004
9.1000e-
004
9.1000e-
004
9.1000e-
004
0.2971 0.2971 2.9000e-
004
0.3044
Total 2.1686 0.0418 2.8464 5.0600e-
003
0.3800 0.3800 0.3800 0.3800 40.7567 12.6500 53.4067 0.0507 2.8800e-
003
55.5309
Mitigated
9.0 Operational Offroad
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type
10.0 Stationary Equipment
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 24 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
11.0 Vegetation
Fire Pumps and Emergency Generators
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type
Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type
User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 9:59 AMPage 25 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Summer
Project Characteristics - Intensity Factors for CO2 adjusted based on PG&E RPS reductions
Land Use - Applicant provided
Construction Phase - Applicant provided
Grading - Applicant provided
Demolition - Applicant provided
Vehicle Trips - Based on ITE rate (Single Family Homes, 210)
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population
Single Family Housing 2.00 Dwelling Unit 0.45 3,600.00 6
1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
5
Wind Speed (m/s)Precipitation Freq (Days)2.2 64
1.3 User Entered Comments & Non-Default Data
1.0 Project Characteristics
Utility Company Pacific Gas & Electric Company
2019Operational Year
CO2 Intensity
(lb/MWhr)
409.81 0.029CH4 Intensity
(lb/MWhr)
0.006N2O Intensity
(lb/MWhr)
Alcalde Road Lot Split
Bay Area AQMD Air District, Winter
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 1 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
2.0 Emissions Summary
Table Name Column Name Default Value New Value
tblConstructionPhase NumDays 5.00 100.00
tblConstructionPhase PhaseEndDate 11/21/2018 11/28/2018
tblConstructionPhase PhaseEndDate 11/7/2018 11/14/2018
tblConstructionPhase PhaseEndDate 11/14/2018 6/27/2018
tblConstructionPhase PhaseStartDate 11/15/2018 7/12/2018
tblConstructionPhase PhaseStartDate 6/21/2018 6/28/2018
tblConstructionPhase PhaseStartDate 11/8/2018 6/21/2018
tblGrading AcresOfGrading 0.50 0.45
tblGrading MaterialExported 0.00 363.00
tblGrading MaterialImported 0.00 130.00
tblLandUse LotAcreage 0.65 0.45
tblProjectCharacteristics CO2IntensityFactor 641.35 409.81
tblVehicleTrips ST_TR 9.91 9.52
tblVehicleTrips SU_TR 8.62 9.52
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 2 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
2.1 Overall Construction (Maximum Daily Emission)
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2018 1.8947 30.3063 9.6373 0.0598 1.6571 0.8593 2.1575 0.4356 0.8026 1.0304 0.0000 6,320.589
0
6,320.589
0
0.5992 0.0000 6,335.569
5
Maximum 1.8947 30.3063 9.6373 0.0598 1.6571 0.8593 2.1575 0.4356 0.8026 1.0304 0.0000 6,320.589
0
6,320.589
0
0.5992 0.0000 6,335.569
5
Unmitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2018 1.8947 30.3063 9.6373 0.0598 1.6571 0.8593 2.1575 0.4356 0.8026 1.0304 0.0000 6,320.589
0
6,320.589
0
0.5992 0.0000 6,335.569
5
Maximum 1.8947 30.3063 9.6373 0.0598 1.6571 0.8593 2.1575 0.4356 0.8026 1.0304 0.0000 6,320.589
0
6,320.589
0
0.5992 0.0000 6,335.569
5
Mitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 3 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 2.1686 0.0418 2.8464 5.0600e-
003
0.3800 0.3800 0.3800 0.3800 40.7567 12.6501 53.4067 0.0507 2.8800e-
003
55.5309
Energy 2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
Mobile 0.0334 0.1613 0.3962 1.1200e-
003
0.0935 1.4600e-
003
0.0949 0.0250 1.3700e-
003
0.0264 112.9590 112.9590 4.8800e-
003
113.0809
Total 2.2045 0.2245 3.2517 6.3200e-
003
0.0935 0.3832 0.4766 0.0250 0.3831 0.4081 40.7567 152.8927 193.6494 0.0561 3.3800e-
003
196.0576
Unmitigated Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 2.1686 0.0418 2.8464 5.0600e-
003
0.3800 0.3800 0.3800 0.3800 40.7567 12.6501 53.4067 0.0507 2.8800e-
003
55.5309
Energy 2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
Mobile 0.0334 0.1613 0.3962 1.1200e-
003
0.0935 1.4600e-
003
0.0949 0.0250 1.3700e-
003
0.0264 112.9590 112.9590 4.8800e-
003
113.0809
Total 2.2045 0.2245 3.2517 6.3200e-
003
0.0935 0.3832 0.4766 0.0250 0.3831 0.4081 40.7567 152.8927 193.6494 0.0561 3.3800e-
003
196.0576
Mitigated Operational
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 4 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
3.0 Construction Detail
Construction Phase
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Demolition Demolition 6/4/2018 6/15/2018 5 10
2 Site Preparation Site Preparation 6/16/2018 6/18/2018 5 1
3 Grading Grading 6/19/2018 6/20/2018 5 2
4 Building Construction Building Construction 6/28/2018 11/14/2018 5 100
5 Paving Paving 6/21/2018 6/27/2018 5 5
6 Architectural Coating Architectural Coating 7/12/2018 11/28/2018 5 100
OffRoad Equipment
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Residential Indoor: 7,290; Residential Outdoor: 2,430; Non-Residential Indoor: 0; Non-Residential Outdoor: 0; Striped Parking Area: 0
(Architectural Coating – sqft)
Acres of Grading (Site Preparation Phase): 0.45
Acres of Grading (Grading Phase): 0
Acres of Paving: 0
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 5 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor
Architectural Coating Air Compressors 1 6.00 78 0.48
Paving Cement and Mortar Mixers 4 6.00 9 0.56
Demolition Concrete/Industrial Saws 1 8.00 81 0.73
Grading Concrete/Industrial Saws 1 8.00 81 0.73
Building Construction Cranes 1 4.00 231 0.29
Building Construction Forklifts 2 6.00 89 0.20
Site Preparation Graders 1 8.00 187 0.41
Paving Pavers 1 7.00 130 0.42
Paving Rollers 1 7.00 80 0.38
Demolition Rubber Tired Dozers 1 1.00 247 0.40
Grading Rubber Tired Dozers 1 1.00 247 0.40
Building Construction Tractors/Loaders/Backhoes 2 8.00 97 0.37
Demolition Tractors/Loaders/Backhoes 2 6.00 97 0.37
Grading Tractors/Loaders/Backhoes 2 6.00 97 0.37
Paving Tractors/Loaders/Backhoes 1 7.00 97 0.37
Site Preparation Tractors/Loaders/Backhoes 1 8.00 97 0.37
Trips and VMT
Phase Name Offroad Equipment
Count
Worker Trip
Number
Vendor Trip
Number
Hauling Trip
Number
Worker Trip
Length
Vendor Trip
Length
Hauling Trip
Length
Worker Vehicle
Class
Vendor
Vehicle Class
Hauling
Vehicle Class
Demolition 4 10.00 0.00 23.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Site Preparation 2 5.00 0.00 62.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Grading 4 10.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Building Construction 5 1.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Paving 7 18.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
Architectural Coating 1 0.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 6 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
3.2 Demolition - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.5085 0.0000 0.5085 0.0770 0.0000 0.0770 0.0000 0.0000
Off-Road 1.0643 9.4295 7.7762 0.0120 0.6228 0.6228 0.5943 0.5943 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Total 1.0643 9.4295 7.7762 0.0120 0.5085 0.6228 1.1313 0.0770 0.5943 0.6713 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Unmitigated Construction On-Site
3.1 Mitigation Measures Construction
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 7 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
3.2 Demolition - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0224 0.7617 0.1518 1.8400e-
003
0.0402 3.0500e-
003
0.0432 0.0110 2.9100e-
003
0.0139 196.5253 196.5253 0.0108 196.7962
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0446 0.0336 0.3184 8.1000e-
004
0.0822 5.5000e-
004
0.0827 0.0218 5.1000e-
004
0.0223 80.4787 80.4787 2.4100e-
003
80.5390
Total 0.0670 0.7953 0.4702 2.6500e-
003
0.1223 3.6000e-
003
0.1259 0.0328 3.4200e-
003
0.0362 277.0040 277.0040 0.0133 277.3352
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.5085 0.0000 0.5085 0.0770 0.0000 0.0770 0.0000 0.0000
Off-Road 1.0643 9.4295 7.7762 0.0120 0.6228 0.6228 0.5943 0.5943 0.0000 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Total 1.0643 9.4295 7.7762 0.0120 0.5085 0.6228 1.1313 0.0770 0.5943 0.6713 0.0000 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 8 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
3.2 Demolition - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0224 0.7617 0.1518 1.8400e-
003
0.0402 3.0500e-
003
0.0432 0.0110 2.9100e-
003
0.0139 196.5253 196.5253 0.0108 196.7962
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0446 0.0336 0.3184 8.1000e-
004
0.0822 5.5000e-
004
0.0827 0.0218 5.1000e-
004
0.0223 80.4787 80.4787 2.4100e-
003
80.5390
Total 0.0670 0.7953 0.4702 2.6500e-
003
0.1223 3.6000e-
003
0.1259 0.0328 3.4200e-
003
0.0362 277.0040 277.0040 0.0133 277.3352
Mitigated Construction Off-Site
3.3 Site Preparation - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.5330 0.0000 0.5330 0.0600 0.0000 0.0600 0.0000 0.0000
Off-Road 0.7858 9.7572 4.2514 9.7600e-
003
0.4180 0.4180 0.3846 0.3846 982.7113 982.7113 0.3059 990.3596
Total 0.7858 9.7572 4.2514 9.7600e-
003
0.5330 0.4180 0.9510 0.0600 0.3846 0.4445 982.7113 982.7113 0.3059 990.3596
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 9 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
3.3 Site Preparation - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.6048 20.5323 4.0911 0.0497 1.0831 0.0821 1.1652 0.2968 0.0786 0.3754 5,297.638
4
5,297.638
4
0.2921 5,304.940
4
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0223 0.0168 0.1592 4.0000e-
004
0.0411 2.8000e-
004
0.0414 0.0109 2.6000e-
004
0.0112 40.2393 40.2393 1.2100e-
003
40.2695
Total 0.6271 20.5491 4.2503 0.0501 1.1242 0.0824 1.2066 0.3077 0.0788 0.3865 5,337.877
7
5,337.877
7
0.2933 5,345.209
9
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.5330 0.0000 0.5330 0.0600 0.0000 0.0600 0.0000 0.0000
Off-Road 0.7858 9.7572 4.2514 9.7600e-
003
0.4180 0.4180 0.3846 0.3846 0.0000 982.7113 982.7113 0.3059 990.3596
Total 0.7858 9.7572 4.2514 9.7600e-
003
0.5330 0.4180 0.9510 0.0600 0.3846 0.4445 0.0000 982.7113 982.7113 0.3059 990.3596
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 10 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
3.3 Site Preparation - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.6048 20.5323 4.0911 0.0497 1.0831 0.0821 1.1652 0.2968 0.0786 0.3754 5,297.638
4
5,297.638
4
0.2921 5,304.940
4
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0223 0.0168 0.1592 4.0000e-
004
0.0411 2.8000e-
004
0.0414 0.0109 2.6000e-
004
0.0112 40.2393 40.2393 1.2100e-
003
40.2695
Total 0.6271 20.5491 4.2503 0.0501 1.1242 0.0824 1.2066 0.3077 0.0788 0.3865 5,337.877
7
5,337.877
7
0.2933 5,345.209
9
Mitigated Construction Off-Site
3.4 Grading - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.7528 0.0000 0.7528 0.4138 0.0000 0.4138 0.0000 0.0000
Off-Road 1.0643 9.4295 7.7762 0.0120 0.6228 0.6228 0.5943 0.5943 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Total 1.0643 9.4295 7.7762 0.0120 0.7528 0.6228 1.3755 0.4138 0.5943 1.0081 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 11 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
3.4 Grading - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0446 0.0336 0.3184 8.1000e-
004
0.0822 5.5000e-
004
0.0827 0.0218 5.1000e-
004
0.0223 80.4787 80.4787 2.4100e-
003
80.5390
Total 0.0446 0.0336 0.3184 8.1000e-
004
0.0822 5.5000e-
004
0.0827 0.0218 5.1000e-
004
0.0223 80.4787 80.4787 2.4100e-
003
80.5390
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.7528 0.0000 0.7528 0.4138 0.0000 0.4138 0.0000 0.0000
Off-Road 1.0643 9.4295 7.7762 0.0120 0.6228 0.6228 0.5943 0.5943 0.0000 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Total 1.0643 9.4295 7.7762 0.0120 0.7528 0.6228 1.3755 0.4138 0.5943 1.0081 0.0000 1,169.350
2
1,169.350
2
0.2254 1,174.985
7
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 12 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
3.4 Grading - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0446 0.0336 0.3184 8.1000e-
004
0.0822 5.5000e-
004
0.0827 0.0218 5.1000e-
004
0.0223 80.4787 80.4787 2.4100e-
003
80.5390
Total 0.0446 0.0336 0.3184 8.1000e-
004
0.0822 5.5000e-
004
0.0827 0.0218 5.1000e-
004
0.0223 80.4787 80.4787 2.4100e-
003
80.5390
Mitigated Construction Off-Site
3.5 Building Construction - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.0848 11.0316 7.7512 0.0114 0.7087 0.7087 0.6520 0.6520 1,146.532
3
1,146.532
3
0.3569 1,155.455
5
Total 1.0848 11.0316 7.7512 0.0114 0.7087 0.7087 0.6520 0.6520 1,146.532
3
1,146.532
3
0.3569 1,155.455
5
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 13 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
3.5 Building Construction - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 4.4600e-
003
3.3600e-
003
0.0318 8.0000e-
005
8.2100e-
003
6.0000e-
005
8.2700e-
003
2.1800e-
003
5.0000e-
005
2.2300e-
003
8.0479 8.0479 2.4000e-
004
8.0539
Total 4.4600e-
003
3.3600e-
003
0.0318 8.0000e-
005
8.2100e-
003
6.0000e-
005
8.2700e-
003
2.1800e-
003
5.0000e-
005
2.2300e-
003
8.0479 8.0479 2.4000e-
004
8.0539
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.0848 11.0316 7.7512 0.0114 0.7087 0.7087 0.6520 0.6520 0.0000 1,146.532
3
1,146.532
3
0.3569 1,155.455
5
Total 1.0848 11.0316 7.7512 0.0114 0.7087 0.7087 0.6520 0.6520 0.0000 1,146.532
3
1,146.532
3
0.3569 1,155.455
5
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 14 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
3.5 Building Construction - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 4.4600e-
003
3.3600e-
003
0.0318 8.0000e-
005
8.2100e-
003
6.0000e-
005
8.2700e-
003
2.1800e-
003
5.0000e-
005
2.2300e-
003
8.0479 8.0479 2.4000e-
004
8.0539
Total 4.4600e-
003
3.3600e-
003
0.0318 8.0000e-
005
8.2100e-
003
6.0000e-
005
8.2700e-
003
2.1800e-
003
5.0000e-
005
2.2300e-
003
8.0479 8.0479 2.4000e-
004
8.0539
Mitigated Construction Off-Site
3.6 Paving - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.9202 8.7447 7.2240 0.0113 0.5109 0.5109 0.4735 0.4735 1,070.137
2
1,070.137
2
0.3017 1,077.679
8
Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 0.9202 8.7447 7.2240 0.0113 0.5109 0.5109 0.4735 0.4735 1,070.137
2
1,070.137
2
0.3017 1,077.679
8
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 15 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
3.6 Paving - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0802 0.0605 0.5731 1.4600e-
003
0.1479 1.0000e-
003
0.1489 0.0392 9.2000e-
004
0.0401 144.8616 144.8616 4.3400e-
003
144.9702
Total 0.0802 0.0605 0.5731 1.4600e-
003
0.1479 1.0000e-
003
0.1489 0.0392 9.2000e-
004
0.0401 144.8616 144.8616 4.3400e-
003
144.9702
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.9202 8.7447 7.2240 0.0113 0.5109 0.5109 0.4735 0.4735 0.0000 1,070.137
2
1,070.137
2
0.3017 1,077.679
8
Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 0.9202 8.7447 7.2240 0.0113 0.5109 0.5109 0.4735 0.4735 0.0000 1,070.137
2
1,070.137
2
0.3017 1,077.679
8
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 16 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
3.6 Paving - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0802 0.0605 0.5731 1.4600e-
003
0.1479 1.0000e-
003
0.1489 0.0392 9.2000e-
004
0.0401 144.8616 144.8616 4.3400e-
003
144.9702
Total 0.0802 0.0605 0.5731 1.4600e-
003
0.1479 1.0000e-
003
0.1489 0.0392 9.2000e-
004
0.0401 144.8616 144.8616 4.3400e-
003
144.9702
Mitigated Construction Off-Site
3.7 Architectural Coating - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 0.5068 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 0.2986 2.0058 1.8542 2.9700e-
003
0.1506 0.1506 0.1506 0.1506 281.4485 281.4485 0.0267 282.1171
Total 0.8055 2.0058 1.8542 2.9700e-
003
0.1506 0.1506 0.1506 0.1506 281.4485 281.4485 0.0267 282.1171
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 17 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
3.7 Architectural Coating - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 0.5068 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 0.2986 2.0058 1.8542 2.9700e-
003
0.1506 0.1506 0.1506 0.1506 0.0000 281.4485 281.4485 0.0267 282.1171
Total 0.8055 2.0058 1.8542 2.9700e-
003
0.1506 0.1506 0.1506 0.1506 0.0000 281.4485 281.4485 0.0267 282.1171
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 18 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
4.0 Operational Detail - Mobile
4.1 Mitigation Measures Mobile
3.7 Architectural Coating - 2018
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 19 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 0.0334 0.1613 0.3962 1.1200e-
003
0.0935 1.4600e-
003
0.0949 0.0250 1.3700e-
003
0.0264 112.9590 112.9590 4.8800e-
003
113.0809
Unmitigated 0.0334 0.1613 0.3962 1.1200e-
003
0.0935 1.4600e-
003
0.0949 0.0250 1.3700e-
003
0.0264 112.9590 112.9590 4.8800e-
003
113.0809
4.2 Trip Summary Information
4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
Single Family Housing 19.04 19.04 19.04 43,975 43,975
Total 19.04 19.04 19.04 43,975 43,975
Miles Trip %Trip Purpose %
Land Use H-W or C-W H-S or C-C H-O or C-NW H-W or C-W H-S or C-C H-O or C-NW Primary Diverted Pass-by
Single Family Housing 10.80 4.80 5.70 31.00 15.00 54.00 86 11 3
5.0 Energy Detail
4.4 Fleet Mix
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH
Single Family Housing 0.570523 0.041853 0.194077 0.115893 0.018544 0.005373 0.016909 0.024079 0.002502 0.002562 0.005975 0.000872 0.000837
Historical Energy Use: N
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 20 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
NaturalGas
Mitigated
2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
NaturalGas
Unmitigated
2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
Single Family
Housing
231.911 2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
Total 2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
Unmitigated
5.1 Mitigation Measures Energy
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 21 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
6.1 Mitigation Measures Area
6.0 Area Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 2.1686 0.0418 2.8464 5.0600e-
003
0.3800 0.3800 0.3800 0.3800 40.7567 12.6501 53.4067 0.0507 2.8800e-
003
55.5309
Unmitigated 2.1686 0.0418 2.8464 5.0600e-
003
0.3800 0.3800 0.3800 0.3800 40.7567 12.6501 53.4067 0.0507 2.8800e-
003
55.5309
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
Single Family
Housing
0.231911 2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
Total 2.5000e-
003
0.0214 9.0900e-
003
1.4000e-
004
1.7300e-
003
1.7300e-
003
1.7300e-
003
1.7300e-
003
27.2837 27.2837 5.2000e-
004
5.0000e-
004
27.4458
Mitigated
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 22 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
0.0139 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
0.0770 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 2.0726 0.0399 2.6806 5.0500e-
003
0.3791 0.3791 0.3791 0.3791 40.7567 12.3529 53.1096 0.0504 2.8800e-
003
55.2265
Landscaping 5.0800e-
003
1.9200e-
003
0.1658 1.0000e-
005
9.1000e-
004
9.1000e-
004
9.1000e-
004
9.1000e-
004
0.2971 0.2971 2.9000e-
004
0.3044
Total 2.1686 0.0418 2.8464 5.0600e-
003
0.3800 0.3800 0.3800 0.3800 40.7567 12.6500 53.4067 0.0507 2.8800e-
003
55.5309
Unmitigated
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 23 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
8.1 Mitigation Measures Waste
7.1 Mitigation Measures Water
7.0 Water Detail
8.0 Waste Detail
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
0.0139 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
0.0770 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 2.0726 0.0399 2.6806 5.0500e-
003
0.3791 0.3791 0.3791 0.3791 40.7567 12.3529 53.1096 0.0504 2.8800e-
003
55.2265
Landscaping 5.0800e-
003
1.9200e-
003
0.1658 1.0000e-
005
9.1000e-
004
9.1000e-
004
9.1000e-
004
9.1000e-
004
0.2971 0.2971 2.9000e-
004
0.3044
Total 2.1686 0.0418 2.8464 5.0600e-
003
0.3800 0.3800 0.3800 0.3800 40.7567 12.6500 53.4067 0.0507 2.8800e-
003
55.5309
Mitigated
9.0 Operational Offroad
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type
10.0 Stationary Equipment
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 24 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
11.0 Vegetation
Fire Pumps and Emergency Generators
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type
Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type
User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:00 AMPage 25 of 25
Alcalde Road Lot Split - Bay Area AQMD Air District, Winter
Bay Area AQMD Air District, Mitigation Report
Alcalde Road Lot Split
Construction Mitigation Summary
Phase ROG NOx CO SO2
Exhaust
PM10
Exhaust
PM2.5 Bio- CO2
NBio-
CO2 Total CO2 CH4 N2O CO2e
Percent Reduction
Architectural Coating 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Building Construction 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Demolition 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Grading 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Paving 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Site Preparation 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
OFFROAD Equipment Mitigation
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:01 AMPage 1 of 11
Equipment Type Fuel Type Tier Number Mitigated Total Number of Equipment DPF Oxidation Catalyst
Air Compressors Diesel No Change 0 1 No Change 0.00
Cement and Mortar Mixers Diesel No Change 0 4 No Change 0.00
Concrete/Industrial Saws Diesel No Change 0 2 No Change 0.00
Cranes Diesel No Change 0 1 No Change 0.00
Forklifts Diesel No Change 0 2 No Change 0.00
Graders Diesel No Change 0 1 No Change 0.00
Pavers Diesel No Change 0 1 No Change 0.00
Rollers Diesel No Change 0 1 No Change 0.00
Rubber Tired Dozers Diesel No Change 0 2 No Change 0.00
Tractors/Loaders/Backhoes Diesel No Change 0 8 No Change 0.00
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:01 AMPage 2 of 11
Equipment Type ROG NOx CO SO2 Exhaust PM10 Exhaust PM2.5 Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Unmitigated tons/yr Unmitigated mt/yr
Air Compressors 1.49300E-002 1.00290E-001 9.27100E-002 1.50000E-004 7.53000E-003 7.53000E-003 0.00000E+000 1.27663E+001 1.27663E+001 1.21000E-003 0.00000E+000 1.27966E+001
Cement and
Mortar Mixers
4.40000E-004 2.76000E-003 2.31000E-003 1.00000E-005 1.10000E-004 1.10000E-004 0.00000E+000 3.43710E-001 3.43710E-001 4.00000E-005 0.00000E+000 3.44600E-001
Concrete/Industria
l Saws
3.12000E-003 2.34900E-002 2.23400E-002 4.00000E-005 1.60000E-003 1.60000E-003 0.00000E+000 3.22594E+000 3.22594E+000 2.50000E-004 0.00000E+000 3.23218E+000
Cranes 1.42700E-002 1.70520E-001 6.30500E-002 1.40000E-004 7.38000E-003 6.79000E-003 0.00000E+000 1.31677E+001 1.31677E+001 4.10000E-003 0.00000E+000 1.32702E+001
Forklifts 1.33600E-002 1.18090E-001 9.08400E-002 1.10000E-004 9.42000E-003 8.67000E-003 0.00000E+000 1.04635E+001 1.04635E+001 3.26000E-003 0.00000E+000 1.05450E+001
Graders 2.60000E-004 3.56000E-003 9.60000E-004 0.00000E+000 1.20000E-004 1.10000E-004 0.00000E+000 3.03880E-001 3.03880E-001 9.00000E-005 0.00000E+000 3.06240E-001
Pavers 7.10000E-004 7.89000E-003 6.40000E-003 1.00000E-005 3.90000E-004 3.50000E-004 0.00000E+000 9.38920E-001 9.38920E-001 2.90000E-004 0.00000E+000 9.46220E-001
Rollers 5.60000E-004 5.45000E-003 4.23000E-003 1.00000E-005 3.80000E-004 3.50000E-004 0.00000E+000 5.23710E-001 5.23710E-001 1.60000E-004 0.00000E+000 5.27790E-001
Rubber Tired
Dozers
8.70000E-004 9.42000E-003 3.28000E-003 1.00000E-005 4.60000E-004 4.20000E-004 0.00000E+000 5.85250E-001 5.85250E-001 1.80000E-004 0.00000E+000 5.89810E-001
Tractors/Loaders/
Backhoes
2.97200E-002 2.93710E-001 2.60980E-001 3.50000E-004 2.08100E-002 1.91400E-002 0.00000E+000 3.16908E+001 3.16908E+001 9.87000E-003 0.00000E+000 3.19375E+001
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:01 AMPage 3 of 11
Equipment Type ROG NOx CO SO2 Exhaust PM10 Exhaust PM2.5 Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Mitigated tons/yr Mitigated mt/yr
Air Compressors 1.49300E-002 1.00290E-001 9.27100E-002 1.50000E-004 7.53000E-003 7.53000E-003 0.00000E+000 1.27663E+001 1.27663E+001 1.21000E-003 0.00000E+000 1.27966E+001
Cement and Mortar
Mixers
4.40000E-004 2.76000E-003 2.31000E-003 1.00000E-005 1.10000E-004 1.10000E-004 0.00000E+000 3.43710E-001 3.43710E-001 4.00000E-005 0.00000E+000 3.44600E-001
Concrete/Industrial
Saws
3.12000E-003 2.34900E-002 2.23400E-002 4.00000E-005 1.60000E-003 1.60000E-003 0.00000E+000 3.22593E+000 3.22593E+000 2.50000E-004 0.00000E+000 3.23218E+000
Cranes 1.42700E-002 1.70520E-001 6.30500E-002 1.40000E-004 7.38000E-003 6.79000E-003 0.00000E+000 1.31677E+001 1.31677E+001 4.10000E-003 0.00000E+000 1.32702E+001
Forklifts 1.33600E-002 1.18090E-001 9.08400E-002 1.10000E-004 9.42000E-003 8.67000E-003 0.00000E+000 1.04635E+001 1.04635E+001 3.26000E-003 0.00000E+000 1.05450E+001
Graders 2.60000E-004 3.56000E-003 9.60000E-004 0.00000E+000 1.20000E-004 1.10000E-004 0.00000E+000 3.03880E-001 3.03880E-001 9.00000E-005 0.00000E+000 3.06240E-001
Pavers 7.10000E-004 7.89000E-003 6.40000E-003 1.00000E-005 3.90000E-004 3.50000E-004 0.00000E+000 9.38920E-001 9.38920E-001 2.90000E-004 0.00000E+000 9.46220E-001
Rollers 5.60000E-004 5.45000E-003 4.23000E-003 1.00000E-005 3.80000E-004 3.50000E-004 0.00000E+000 5.23710E-001 5.23710E-001 1.60000E-004 0.00000E+000 5.27790E-001
Rubber Tired Dozers 8.70000E-004 9.42000E-003 3.28000E-003 1.00000E-005 4.60000E-004 4.20000E-004 0.00000E+000 5.85250E-001 5.85250E-001 1.80000E-004 0.00000E+000 5.89810E-001
Tractors/Loaders/Ba
ckhoes
2.97200E-002 2.93710E-001 2.60980E-001 3.50000E-004 2.08100E-002 1.91400E-002 0.00000E+000 3.16908E+001 3.16908E+001 9.87000E-003 0.00000E+000 3.19374E+001
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:01 AMPage 4 of 11
Fugitive Dust Mitigation
No Soil Stabilizer for unpaved
Roads
PM10 Reduction PM2.5 Reduction
No Replace Ground Cover of Area
Disturbed
PM10 Reduction PM2.5 Reduction
No Water Exposed Area PM10 Reduction PM2.5 Reduction Frequency (per
day)
No Unpaved Road Mitigation Moisture Content
%
Vehicle Speed
(mph)
0.00
No Clean Paved Road % PM Reduction 0.00
Equipment Type ROG NOx CO SO2 Exhaust PM10 Exhaust PM2.5 Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Percent Reduction
Air Compressors 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 7.83313E-007 7.83313E-007 0.00000E+000 0.00000E+000 1.56291E-006
Cement and Mortar
Mixers
0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000
Concrete/Industrial
Saws
0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 3.09987E-006 3.09987E-006 0.00000E+000 0.00000E+000 0.00000E+000
Cranes 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 1.51886E-006 1.51886E-006 0.00000E+000 0.00000E+000 7.53567E-007
Forklifts 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 9.55700E-007 9.55700E-007 0.00000E+000 0.00000E+000 1.89664E-006
Graders 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000
Pavers 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000
Rollers 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000
Rubber Tired Dozers 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000
Tractors/Loaders/Ba
ckhoes
0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 0.00000E+000 9.46646E-007 9.46646E-007 0.00000E+000 0.00000E+000 1.25245E-006
Yes/No Mitigation InputMitigation InputMitigation InputMitigation Measure
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:01 AMPage 5 of 11
Operational Percent Reduction Summary
Unmitigated Mitigated Percent Reduction
Phase Source PM10 PM2.5 PM10 PM2.5 PM10 PM2.5
Architectural Coating Fugitive Dust 0.00 0.00 0.00 0.00 0.00 0.00
Architectural Coating Roads 0.00 0.00 0.00 0.00 0.00 0.00
Building Construction Fugitive Dust 0.00 0.00 0.00 0.00 0.00 0.00
Building Construction Roads 0.00 0.00 0.00 0.00 0.00 0.00
Demolition Fugitive Dust 0.00 0.00 0.00 0.00 0.00 0.00
Demolition Roads 0.00 0.00 0.00 0.00 0.00 0.00
Grading Fugitive Dust 0.00 0.00 0.00 0.00 0.00 0.00
Grading Roads 0.00 0.00 0.00 0.00 0.00 0.00
Paving Fugitive Dust 0.00 0.00 0.00 0.00 0.00 0.00
Paving Roads 0.00 0.00 0.00 0.00 0.00 0.00
Site Preparation Fugitive Dust 0.00 0.00 0.00 0.00 0.00 0.00
Site Preparation Roads 0.00 0.00 0.00 0.00 0.00 0.00
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:01 AMPage 6 of 11
Category ROG NOx CO SO2
Exhaust
PM10
Exhaust
PM2.5 Bio- CO2
NBio-
CO2 Total CO2 CH4 N2O CO2e
Percent Reduction
Architectural Coating 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Consumer Products 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Electricity 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Hearth 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Landscaping 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Mobile 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Natural Gas 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Water Indoor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Water Outdoor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Operational Mobile Mitigation
Mitigation
Selected
No
No
No
No
No
No
Category
Land Use
Land Use
Land Use
Land Use
Land Use
Land Use
Land Use
% Reduction
0.00
0.00
0.00
0.25
0.00
0.00
-0.01
Input Value 1
0.13
Input Value 2 Input Value
3
Measure
Increase Diversity
Land Use SubTotal
Integrate Below Market Rate Housing
Increase Transit Accessibility
Improve Destination Accessibility
Improve Walkability Design
Increase Density
Project Setting:
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:01 AMPage 7 of 11
No
No
No Neighborhood Enhancements
Neighborhood Enhancements
Neighborhood Enhancements
0.00Implement NEV Network
Provide Traffic Calming Measures
Improve Pedestrian Network
No
No
No
No
No
No
Parking Policy Pricing
Transit Improvements
Transit Improvements
Transit Improvements
Transit Improvements
Parking Policy Pricing
Parking Policy Pricing
Parking Policy Pricing
Neighborhood Enhancements 0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00Limit Parking Supply
Land Use and Site Enhancement Subtotal
Transit Improvements Subtotal
Increase Transit Frequency
Expand Transit Network
Provide BRT System
Parking Policy Pricing Subtotal
On-street Market Pricing
Unbundle Parking Costs
Neighborhood Enhancements Subtotal
No
No
No
No
No
No
No
No
Commute
Commute
Commute
Commute
Commute
Commute
Commute
Commute
Commute
0.00
0.00
0.00
0.00
2.00
Transit Subsidy
Commute Subtotal
Provide Ride Sharing Program
Employee Vanpool/Shuttle
Market Commute Trip Reduction Option
Encourage Telecommuting and Alternative
Work Schedules
Workplace Parking Charge
Implement Employee Parking "Cash Out"
Implement Trip Reduction Program
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:01 AMPage 8 of 11
Area Mitigation
Measure Implemented
No
No
No
No
No
No
No
No
No
No
Mitigation Measure
No Hearth
% Electric Chainsaw
% Electric Leafblower
% Electric Lawnmower
Use Low VOC Paint (Non-residential Exterior)
Use Low VOC Paint (Non-residential Interior)
Use Low VOC Paint (Residential Exterior)
Use Low VOC Paint (Residential Interior)
Use Low VOC Cleaning Supplies
Only Natural Gas Hearth
Input Value
150.00
100.00
150.00
100.00
Energy Mitigation Measures
Measure Implemented
No
No
No
Mitigation Measure
Install High Efficiency Lighting
On-site Renewable
Exceed Title 24
Input Value 1 Input Value 2
No School Trip 0.00Implement School Bus Program
0.00Total VMT Reduction
No Use Low VOC Paint (Parking)150.00
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:01 AMPage 9 of 11
Appliance Type Land Use Subtype % Improvement
ClothWasher 30.00
DishWasher 15.00
Fan 50.00
Refrigerator 15.00
Water Mitigation Measures
Measure Implemented
No
No
No
Mitigation Measure
Use Reclaimed Water
Use Grey Water
Apply Water Conservation on Strategy
Input Value 1 Input Value 2
No
No
No
No
Install low-flow bathroom faucet
Install low-flow Toilet
Install low-flow Shower
Install low-flow Kitchen faucet
32.00
18.00
20.00
20.00
No
No
No
Turf Reduction
Water Efficient Landscape
Use Water Efficient Irrigation Systems 6.10
Solid Waste Mitigation
Mitigation Measures Input Value
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:01 AMPage 10 of 11
Institute Recycling and Composting Services
Percent Reduction in Waste Disposed
CalEEMod Version: CalEEMod.2016.3.2 Date: 1/10/2018 10:01 AMPage 11 of 11