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HomeMy WebLinkAboutPC Reso 14-16 Wallis Ranch rec to CC CEQA Addendum RESOLUTION NO. 14-16
A RESOLUTION OF THE PLANNING COMMISSION
OF THE CITY OF DUBLIN
RECOMMENDING THAT THE CITY COUNCIL ADOPT A CEQA ADDENDUM FOR THE
WALLIS RANCH PROJECT
PLPA 2013-00035
WHEREAS, the Applicant, Trumark Homes LLC, has submitted a Planning Application to
develop up to 806 dwellings on 88.5 acres of an approximately 184-acre site. The remaining
area of the site would include parks, open space and other improvements. The project
proposes a Planned Development rezoning with amended Stage 1 and Stage 2 Development
Plan, Site Development Review, Master Vesting Tentative Map 7515, and eight Neighborhood
Vesting Tentative Maps 7711, 7712, 7713, 7714, 7715, 7716, 8169, and 8170. The applications
are collectively referred to herein as the "Project"; and
WHEREAS, the Project site contains one residence, several outbuildings, and a historic
school building that was moved onto the site. The site is located east of Camp Parks, west of
Tassajara Road and south of the Alameda/Contra Costa County boundary. The site is broad in
its northern area and narrows considerably towards the south. Tassajara Creek passes along
the easterly property boundary and is covered by a conservation easement known as the
Tassajara Creek Management Zone. In the northern area, several other smaller properties are
located between the site and Tassajara Road; the middle and southern parts of the property are
adjacent to the road; and
WHEREAS, the California Environmental Quality Act (CEQA), together with the State
guidelines and City environmental regulations, require that certain projects be reviewed for
environmental impacts and that environmental documents be prepared; and
WHEREAS, the Project and/or Project site has been addressed in three prior CEQA
reviews: The Eastern Dublin EIR, a 2005 Supplemental EIR prepared for the Dublin Ranch
West (Wallis Ranch) annexation, and a Mitigated Negative Declaration (MND) for the expansion
of the project onto adjacent property, all of which reviews are further described in the draft City
Council resolution attached as Exhibit A and incorporated herein by reference; and
WHEREAS, based on the prior CEQA reviews and a related Initial Study, the City
prepared a CEQA Addendum, concluding and documenting that potential environmental effects
of the Project are adequately addressed in the prior CEQA reviews, as further described in
attached Exhibit A; and
WHEREAS, on April 29, 2014, the Planning Commission held a properly noticed public
hearing on the Wallis Ranch project, at which time all interested parties had the opportunity to
be heard; and
WHEREAS, a staff report dated April 29, 2014 and incorporated herein by reference
described and analyzed the Wallis Ranch project and related Addendum for the Planning
Commission and recommended adoption of the CEQA Addendum and approval of the Project;
and
Page 1 of 2
WHEREAS, the Planning Commission considered the Addendum, as well as the prior
EIRs and MND and all above-referenced reports, recommendations, and testimony before
making a recommendation on the Project.
NOW, THEREFORE BE IT RESOLVED that the foregoing recitals are true and correct
and made a part of this resolution.
BE IT FURTHER RESOLVED that the Planning Commission of the City of Dublin
recommends that the City Council adopt the CEQA Addendum and related Initial Study,
attached as Exhibit A (and incorporated herein by reference), pursuant to CEQA Guidelines
Sections 15162 and 15164 for the Wallis Ranch project.
PASSED, APPROVED AND ADOPTED this 29th day of April, 2014 by the following vote:
AYES: Bhuthimethee, Do, Goel, Kohli
NOES:
ABSENT: O'Keefe
ABSTAIN:
Plan ing Commission hairperson
ATT 7
Assistan orb nity Development Director
2266440.1
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RESOLUTION NO. XX - 14
A RESOLUTION OF THE CITY COUNCIL
OF THE CITY OF DUBLIN
ADOPTING A CEQA ADDENDUM FOR THE WALLIS RANCH PROJECT AND A RELATED
STATEMENT OF OVERRIDING CONSIDERATIONS
PLPA 2013-00035
WHEREAS, the Applicant, Trumark Homes LLC, has submitted a Planning Application to
develop up to 806 dwellings on 88.5 acres of an approximately 184-acre site. The remaining
area of the site would include parks, open space and other improvements. The project
proposes a Planned Development rezoning with amended Stage 1 and Stage 2 Development
Plan, Site Development Review, Master Vesting Tentative Map 7515, and eight Neighborhood
Vesting Tentative Maps 7711, 7712, 7713, 7714, 7715, 7716, 8169, and 8170. The applications
are collectively referred to herein as the "Project"; and
WHEREAS, the Project site contains one residence, several outbuildings, and a historic
school building that was moved onto the site. The site is located east of Camp Parks, west of
Tassajara Road and south of the Alameda/Contra Costa County boundary. The site is broad in
its northern area and narrows considerably towards the south. Tassajara Creek passes along
the easterly property boundary and is covered by a conservation easement known as the
Tassajara Creek Management Zone. In the northern area, several other smaller properties are
located between the site and Tassajara Road; the middle and southern parts of the property are
adjacent to the road; and
WHEREAS, the 806 dwellings would include 92 units of Low Density Residential, 529
units of Medium Density Residential, and 185 units of Medium High Density Residential. The
residential neighborhoods would be located in the westerly, generally flatter areas west of
Tassajara Creek, where the property is broadest; and
WHEREAS, the non-residential uses include approximately 83.3 acres designated for
Open Space, 10.4 acres designated Neighborhood Park, and 1.3 acres designated Semi-Public
(for which no specific use is proposed). The non-residential areas are generally located along
Tassajara Creek, in the steeper areas along the southwestern border of the site, and in the
southerly, narrower areas of the site; and
WHEREAS, the California Environmental Quality Act (CEQA), together with the State
guidelines and City environmental regulations, require that certain projects be reviewed for
environmental impacts and that environmental documents be prepared; and
WHEREAS, the Project is in the General Plan Eastern Extended Planning Area and the
Eastern Dublin Specific Plan area, for which the City Council certified a Program Environmental
Impact Report by Resolution 51-93 ("Eastern Dublin EIR" or "EDEIR", SCH 91103064) on May
10, 1993, which resolution is incorporated herein by reference. The Eastern Dublin EIR
identified significant impacts from development of the Eastern Dublin area, some of which could
not be mitigated to less than significant. Upon approval of the Eastern Dublin General Plan
Amendment and Specific Plan, the City Council adopted mitigations, a mitigation monitoring
Page I of 4 EXHIBIT A TO
ATTACHMENT 3
program and a Statement of Overriding Considerations (Resolution 53-93, incorporated herein
by reference); and
WHEREAS, in 2005, a Supplemental EIR ("SEIR", SCH #2003022083) was prepared for
the Dublin Ranch West (Wallis Ranch) annexation to identify potentially significant impacts
beyond those identified in the 1993 EIR. The SEIR identified additional significant unavoidable
impacts for air quality and traffic. The City Council certified the SEIR (Resolution 42-05, dated
March 15, 2005 and incorporated herein by reference) and adopted a related Statement of
Overriding Considerations; and
WHEREAS, in 2007, an 11.6 acre parcel was added to the project to provide room for
offsite grading and an emergency vehicle access. The added parcel is north of the Project site,
in Contra Costa County and is owned by the Wallis Ranch owners. The City adopted a
Mitigated Negative Declaration (MND) for the expansion area through Resolution 18-07 on
February 20, 2007, which resolution is incorporated herein by reference. The current Project
proposes no change to the adjacent 11.6 acre parcel; and
WHEREAS, the Eastern Dublin EIR and 2005 SEIR identified significant unavoidable
impacts from development of the Eastern Dublin area and the Project site, some of which would
apply to the Project; therefore, approval of the Project must be supported by a Statement of
Overriding Considerations; and
WHEREAS, the City prepared an Initial Study to determine if additional review of the
proposed Project was required pursuant to CEQA Guidelines section 15162. Based on the
Initial Study, the City prepared an Addendum dated April 29, 2014 describing the Wallis Ranch
project and finding that the impacts of the proposed Project have been adequately addressed in
the prior EIRs and MND. The Addendum and its supporting Initial Study is attached as Exhibit
A; and
WHEREAS, on April 29, 2014, the Planning Commission held a properly noticed public
hearing on the Wallis Ranch project, at which time all interested parties had the opportunity to
be heard; and
WHEREAS, a staff report dated April 29, 2014 and incorporated herein by reference,
described and analyzed the Wallis Ranch project and related Addendum for the Planning
Commission and recommended adoption of the CEQA Addendum and approval of the Project;
and
WHEREAS, on April 29, 2014, the Planning Commission adopted Resolution 14-XX
recommending that the City Council adopt the CEQA Addendum for the Wallis Ranch project,
which resolution is incorporated herein by reference and available for review at City Hall during
normal business hours; and
WHEREAS, a staff report dated 2014 and incorporated herein by reference
described and analyzed the Wallis Ranch project and related Addendum for the City Council
and recommended adoption of the CEQA Addendum and approval of the Project; and
WHEREAS, on , 2014 the City Council held a properly noticed public hearing
on the Project at which time all interested parties had the opportunity to be heard; and
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WHEREAS, the City Council considered the Addendum, as well as the prior EIRs and
MND and all above-referenced reports, recommendations, and testimony before taking any
action on the Project.
NOW, THEREFORE BE IT RESOLVED that the foregoing recitals are true and correct
and made a part of this resolution.
BE IT FURTHER RESOLVED that the City Council makes the following findings to
support the determination that no further environmental review is required under CEQA for the
proposed Wallis Ranch project. These findings are based on information contained in the
CEQA Addendum, the prior CEQA documents, the City Council staff report, and all other
information contained in the record before the City Council. These findings constitute a
summary of the information contained in the entire record. The detailed facts to support the
findings are set forth in the CEQA Addendum and related Initial Study, the prior CEQA
documents, and elsewhere in the record. Other facts and information in the record that support
each finding that are not included below are incorporated herein by reference:
1. The proposed Project does not constitute substantial changes to the previous projects
affecting the Project site as addressed in the prior CEQA documents, that will require major
revisions to the prior documents due to new significant environmental effects or a substantial
increase in severity of previously identified significant effects. Based on the Initial Study, all
potentially significant effects of the proposed Project are the same or less than the impacts for
project which were previously addressed. The proposed Project will not result in substantially
more severe significant impacts than those identified in the prior CEQA documents. All
previously adopted mitigation measures from the Eastern Dublin EIR and the SEIR continue to
apply to the proposed Project and project site as applicable. In addition, all of the MND
mitigations continue to apply to the 11.6-acre expansion area.
2. The Addendum and its related Initial Study did not identify any new significant impacts
of the proposed Project that were not analyzed in the prior CEQA documents.
3. The City is not aware of any new information of substantial importance or substantial
changes in circumstances that would result in new or substantially more severe impacts or meet
any other standards in CEQA Section 21166 and related CEQA Guidelines Sections 15162/3.
BE IT FURTHER RESOLVED that the City Council of the City of Dublin finds the
following:
1. No further environmental review under CEQA is required for the proposed Project
because there is no substantial evidence in the record as a whole that any of the standards
under Sections 21166 or 15162/3 are met.
2. The City has properly prepared an Addendum and related Initial Study under
CEQA Guidelines section 15164 to explain its decision not to prepare a subsequent or
Supplemental EIR or conduct further environmental review for the proposed Project.
3. The City Council considered the information in the Addendum and prior CEQA
documents before approving the land use applications for the proposed Project.
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BE IT FURTHER RESOLVED that the City Council of the City of Dublin adopts the
CEQA Addendum and related Initial Study, attached as Exhibit A (and incorporated herein by
reference), pursuant to CEQA Guidelines Sections 15162 and 15164 for the Wallis Ranch
project.
BE IT FURTHER RESOLVED that the City Council of the City of Dublin adopts the
Statement of Overriding Considerations attached as Exhibit B and incorporated herein by
reference
PASSED, APPROVED AND ADOPTED this day of 2014 by the
following vote:
AYES:
NOES:
ABSENT:
ABSTAIN:
Mayor
ATTEST:
City Clerk
2264070.1
4 of 4
EXHIBIT A
CEQA ADDENDUM FOR THE WALLIS RANCH PROJECT
PLPA-2013-00035
April 22, 2014
On May 10, 1993, the Dublin City Council adopted Resolution No. 51-93, certifying an
Environmental Impact Report for the Eastern Dublin General Plan Amendment and
Specific Plan ("Eastern Dublin EIR, SCH #91103064). The certified EIR consisted of a
Draft EIR and Responses to Comments bound volumes, as well as an Addendum to the
Eastern Dublin EIR dated May 4, 1993, assessing a reduced development project
alternative. The City Council adopted Resolution No. 53-93 approving a General Plan
Amendment and Specific Plan for the reduced area alternative on May 10, 1993. On
August 22, 1994, the City Council adopted a second Addendum updating wastewater
disposal plans for Eastern Dublin. The Eastern Dublin EIR evaluated the potential
environmental effects of urbanizing Eastern Dublin over a 20 to 30 year period. Since
certification of the EIR, many implementing projects have been proposed, relying to
various degrees on the certified EIR.
A Supplement was prepared to the Eastern Dublin EIR in 2005 (State Clearinghouse #
2003022082) for an annexation of the property to the City of Dublin and Dublin San
Ramon Services District and prezoning of the site. The 2005 Supplemental EIR
provided updated analyses of agricultural resources, biology, air quality, land use,
population and housing, traffic and circulation, schools, parks and recreation and utilities
and services. In certifying the 2005 SEIR and approving the prezoning, the City
Council, through Resolution No. 42-05, adopted a Statement of Overriding
Considerations for the project and the cumulative air quality impacts.
In 2007, the City of Dublin approved a Mitigated Negative Declaration (MND) to analyze
improvements within approximately 11.6 acres of land located immediately north of the
Wallis Ranch property that was the subject of the 2005 SEIR. This property is under the
same ownership as Wallis Ranch, but located in the unincorporated portion of Contra
Costa County rather than within Dublin and Alameda County. The applicant proposed
placement of an Emergency Vehicle Assess (EVA), a herpetological barrier and a
bioswale within this area. The MND was adopted by Dublin City Council Resolution No.
18-07 on February 20, 2007.
This Addendum has been prepared pursuant to CEQA Guidelines Section 15164 for the
Project, as described below.
Project Description
The current application includes applications for a Planned Development Rezone with
amended Stage 1 and Stage 2 Development Plan, a Site Development Review (SDR)
permit, and a Vesting Tentative Subdivision Map to change the number of dwellings
units on this 184.1-acre site. The proposed Development Plan includes construction of
up to 809 dwellings at various densities and product types rather than up to 935
dwellings allowed under existing City approvals, primary and internal roadways, two
neighborhood parks, a private park, permanent open spaces, public and semi-public
uses and other related improvements.
Prior CEQA Analyses and Determinations
As summarized above and discussed in more detail in the attached Initial Study, the
Wallis Ranch property has been planned for urbanization since the Eastern Dublin
approvals in 1993, 2005 and 2007, and has been the subject of two previously certified
EIRs and a Mitigated Negative Declaration (MND). The Eastern Dublin EIR identified
numerous environmental impacts, and numerous mitigations were adopted upon
approval of the Eastern Dublin General Plan Amendment and Specific Plan. For
identified impacts that could not be mitigated to insignificance, the City Council adopted
a Statement of Overriding Considerations. Similarly, the 2005 SEIR identified
supplemental impacts and mitigation measures, as well as additional significant
unavoidable impacts for which statements of overriding considerations were adopted.
All previously adopted mitigation measures for development of Eastern Dublin identified
in the Eastern Dublin EIR and the 2005 SEIR that are applicable to the Project and
Project site continue to apply to the currently proposed Project as further discussed in
the attached Initial Study.
Current CEQA Analysis and Determination that an Addendum is appropriate for
this Project.
Updated Initial Study. The City of Dublin has determined that an Addendum is the
appropriate CEQA review for the Project, which proposes minor changes to the Planned
Development zoning. If approved, the proposed project would reduce the number of
dwellings allowed on the site from up to 935 to up to 809 dwellings.
The applicant is also seeking City approval of a Planned Development Rezone with
amended Stage 1 and Stage 2 Development Plan, Site Development Review permit, a
vesting subdivision map and potentially an amendment to an existing Development
Agreement.
The City prepared an updated Initial Study dated April 22, 2014, incorporated herein by
reference, to assess whether any further environmental review is required for this
Project. Through this Initial Study, the City has determined that no subsequent EIR or
Negative Declaration is required for the plan and zoning amendments or the refined
development details.
No Subsequent Review is required per CEQA Guidelines Section 15162. CEQA
Guidelines Section 15162 identifies the conditions requiring subsequent environmental
review. After a review of these conditions, the City has determined that no subsequent
EIR or negative declaration is required for this Project. This is based on the following
analysis:
Page 2
a) Are there substantial changes to the Project involving new or more severe significant
impacts? There are no substantial changes to the Project analyzed in the Eastern
Dublin EIR, as supplemented by the 2005 SEIR and 2007 MND. The Project is
similar to land uses for the project site analyzed in the 2005 SEIR. As demonstrated
in the Initial Study, the proposed land uses on the site is not a substantial change to
either the 2005 SEIR analysis or the 2007 MND analysis and will not result in
additional significant impacts, and no additional or different mitigation measures are
required.
b) Are there substantial changes in the conditions which the Project is undertaken
involving new or more severe significant impacts? There are no substantial changes
in the conditions assumed in the Eastern Dublin EIR, the 2005 SEIR or the 2007
MND. This is documented in the attached Initial Study prepared for this Project
dated April 22, 2014.
c) Is there new information of substantial importance, which was not known and could
not have been known at the time of the previous EIR that shows the Project will have
a significant effect not addressed in the previous EIR; or previous effects are more
severe; or, previously infeasible mitigation measures are now feasible but the
applicant declined to adopt them; or mitigation measures considerably different from
those in the previous EIR would substantially reduce significant effects but the
applicant declines to adopt them? As documented in the attached Initial Study,
there is no new information showing a new or more severe significant effect beyond
those identified in the prior CEQA documents. Similarly, the Initial Study documents
that no new or different mitigation measures are required for the Project. All
previously adopted mitigations continue to apply to the Project. The CEQA
documents adequately describe the impacts and mitigations associated with the
proposed development on portions of the Wallis Ranch property.
d) If no subsequent EIR-level review is required, should a subsequent negative
declaration be prepared? No subsequent negative declaration or mitigated negative
declaration is required because there are no impacts, significant or otherwise, of the
Project beyond those identified in the Eastern Dublin EIR and previous CEQA
documents for the site, as documented in the attached Initial Study.
Conclusion
This Addendum is adopted pursuant to CEQA Guidelines Section 15164 based on the
attached Initial Study dated April 12, 2014. The Addendum and Initial Study review the
proposed the Planned Development rezoning amendment, Site Development Review,
Vesting Tentative Subdivision Map and Development Agreement amendment as
discussed above. Through the adoption of this Addendum and related Initial Study, the
City determines that the above minor changes in land uses do not require a subsequent
EIR or negative declaration under CEQA Section 21166 or CEQA Guidelines Sections
15162 and 15163. The City further determines that the Eastern Dublin EIR, the 2005
SEIR and the 2007 MND adequately address the potential environmental impacts of the
Page 3
land use designation change for the Wallis Ranch site as documented in the attached
Initial Study.
As provided in Section 15164 of the Guidelines, the Addendum need not be circulated
for public review, but shall be considered with the prior environmental documents before
making a decision on this project.
The Initial Study, Eastern Dublin EIR, the 2005 SEIR, the 2007 MND and all resolutions
cited above are incorporated herein by reference and are available for public review
during normal business hours in the Community Development Department, Dublin City
Hall, 100 Civic Plaza, Dublin CA.
Page 4
EXHIBIT B
STATEMENT OF OVERRIDING CONSIDERATIONS
1. General. Pursuant to CEQA Guidelines section 15093, the City Council of
the City of Dublin adopted a Statement of Overriding Considerations for those
impacts identified in the Eastern Dublin EIR as significant and unavoidable.
(Resolution 53-93, May 10, 1993.) The City Council carefully considered each
impact in its decision to approve urbanization of Eastern Dublin through approval
of the Eastern Dublin General Plan Amendment and Specific Plan project. The
City Council is currently considering the Wallis Ranch project. The project
proposes a residential development on the west side of Tassajara Road,
generally south of the county line. The City prepared a Supplemental EIR in
2005 for the Dublin Ranch West project, which was similar to the current project
but with more dwellings. The 2005 Supplemental EIR identified supplemental
impacts that could be mitigated to less than significant. The Supplemental EIR
also identified supplemental Air Quality and Traffic impacts that could not be
mitigated to less than significant.
The City Council adopted a Statement of Overriding Considerations with the
original land use approvals for urbanization of Eastern Dublin and again with
approval of the 2005 and 2007 projects. Pursuant to a 2002 court decision, the
City Council must adopt new overriding considerations for the previously
identified unavoidable impacts that apply to the Wallis Ranch project.1 The City
Council believes that many of the unavoidable environmental effects identified in
the Eastern Dublin EIR and the 2005 Supplemental EIR will be substantially
lessened by mitigation measures adopted with the original Eastern Dublin
approvals and by the environmental protection measures adopted through the
2005 Dublin Ranch West approvals, to be implemented with the development of
the project. Even with mitigation, the City Council recognizes that the
implementation of the project carries with it unavoidable adverse environmental
effects as identified in the Eastern Dublin EIR and the 2005 Supplemental EIR.
The City Council specifically finds that to the extent that the identified adverse or
potentially adverse impacts for the project have not been mitigated to acceptable
levels, there are specific economic, social, environmental, land use, and other
considerations that support approval of the project.
2. Unavoidable Significant Adverse Impacts from the Eastern Dublin EIR.
The following unavoidable significant environmental impacts identified In the
Eastern Dublin EIR for future development of Eastern Dublin apply to the Wallis
Ranch project.
"...public officials must still go on the record and explain specifically why they are approving the
later project despite its significant unavoidable impacts." (emphasis original.) Communities for a
Better Environment v California Resources Agency 103 Cal.App. 4th 98, _(2002).
1
Land Use Impact 3.11F. Cumulative Loss of Agricultural and Open Space Lands;
Visual Impacts 3.8/13; and, Alteration of Rural/Open Space Character. Although
development has occurred south of the project area, the site is largely
undeveloped open space land. Future development of the Wallis Ranch site will
contribute to the cumulative loss of open space land.
Traffic and Circulation Impacts 3.318, 3.31E. 1-580 Freeway, Cumulative Freeway
Impacts: While city street and interchange impacts can be mitigated through
planned improvements, transportation demand management, the 1-580 Smart
Corridor program and other similar measures, mainline freeway impacts continue
to be identified as unavoidable, as anticipated in the Eastern Dublin EIR. Future
development on the Wallis Ranch site will generate less traffic than anticipated in
the Eastern Dublin EIR, but will still incrementally contribute to the unavoidable
freeway impacts.
Traffic and Circulation Impacts 3.311, 3.31M. Santa Rita Road/1-580 Ramps,
Cumulative Dublin Boulevard Impacts: The Wallis Ranch project will be required
to implement all applicable adopted traffic mitigation measures, including
contributions to the City's TIF program; however even with mitigation these
impacts continue to be identified as unavoidable, as anticipated in the Eastern
Dublin EIR.
Community Services and Facilities Impact 3.41S. Consumption of Non-
Renewable Natural Resources and Sewer, Water; and Storm Drainage Impact
3.51F, H, U. Increases in Energy Usage Through Increased Water Treatment,
Disposal and Operation of Water Distribution System: Future development of the
Wallis Ranch project will contribute to increased energy consumption.
Soils, Geology, and Seismicity Impact 3.61B. Earthquake Ground Shaking,
Primary Effects: Even with seismic design, future development of the Wallis
Ranch project could be subject to damage from large earthquakes, much like the
rest of the Eastern Dublin planning area.
Air Quality Impacts 3.111A, B, C, and E. Future development of the Wallis Ranch
project will contribute to cumulative dust deposition, construction equipment
emissions, mobile and stationary source emissions.
3. Unavoidable Significant Adverse Impacts from the Dublin Ranch West
Supplemental EIR. The following unavoidable significant supplemental
environmental impacts identified in the 2005 Supplemental EIR for the Dublin
Ranch West project apply to the Wallis Ranch project.
Supplemental Impacts AQ-2, AQ-3. Project emission increase that would
exceed the BAAQMD significance thresholds for ozone precursors on project and
cumulative levels. Even with implementation of the previously adopted mitigation
measures and the additional mitigation measures in the Supplemental EIR,
project and cumulative precursor emissions will exceed BAAQMD thresholds.
2
Supplemental Impact TRA-2. Impacts to study intersections under Buildout
conditions (Dublin Boulevard/Dougherty Road). Even with implementation of the
previously adopted mitigation measures, including contribution to intersection
improvements through the TIF program, the project will contribute to significant
and unavoidable impacts at this intersection under buildout conditions.
4. Overriding Considerations. The City Council previously balanced the
benefits of the Eastern Dublin 2005 and 2007 project approvals against the
significant and potentially significant adverse impacts identified in the Eastern
Dublin EIR and 2005 Supplemental EIR. The City Council now balances those
unavoidable impacts that apply to future development on the Wallis Ranch site
against its benefits, and hereby determines that such unavoidable impacts are
outweighed by the benefits of the Wallis Ranch project as further set forth below.
The project will further the urbanization of Eastern Dublin as planned through the
comprehensive framework established in the original Eastern Dublin approvals.
Prior approvals provided important protections to Tassajara Creek and through
reasonable and protective designations for sensitive creek areas; the Wallis
Ranch project will implement these protections through previously adopted
mitigation measures and current development standards. The project will
provide approximately 806 units of needed housing with diverse densities and
building types, as well as maintaining open space and the potential for semi-
public uses on the site. Development of the site will also provide construction
employment opportunities for Dublin residents.
2266460.1
3
Wallis Ranch/
Trumark Project
PLPA 2013-00035
INITIAL STUDY
Lead Agency:
City of Dublin
Prepared By:
Jerry Haag, Urban Planner
April 22,2014
Table of Contents
Introduction...................................................................................................................2
Applicant........................................................................................................................4
Project Location and Context ......................................................................................4
Prior Environmental Review Documents..................................................................4
ProjectDescription........................................................................................................7
Environmental Factors Potentially Affected.............................................................17
Determination................................................................................................................17
Evaluation of Environmental Impacts .......................................................................19
Attachmentto Initial Study .........................................................................................32
1. Aesthetics ...............................................................................................32
2. Agricultural and Forestry Resources .................................................35
3. Air Quality .............................................................................................37
4. Biological Resources .............................................................................40
5. Cultural Resources................................................................................46
6. Geology and Soils .................................................................................48
7. Greenhouse Gas Emissions..................................................................53
8. Hazards and Hazardous Materials ....................................................53
9. Hydrology and Water Quality............................................................55
10. Land Use and Planning........................................................................58
11. Mineral Resources.................................................................................59
12. Noise .......................................................................................................60
13. Population and Housing......................................................................62
14. Public Services.......................................................................................63
15. Recreation...............................................................................................65
16. Transportation/Traffic.........................................................................66
17. Utilities and Service Systems...............................................................70
18. Mandatory Findings of Significance ..................................................72
InitialStudy Preparers .................................................................................................73
Agencies and Organizations Consulted ....................................................................73
References ......................................................................................................................74
Attachment 1-Trip Generation Analysis....................................................................75
City of Dublin
Environmental Checklist/
Initial Study
Introduction
This Initial Study has been prepared in accord with the provisions of the California
Environmental Quality Act (CEQA) and assesses the potential environmental impacts
of implementing the proposed project described below.
The Initial Study consists of a completed environmental checklist and a brief
explanation of the environmental topics addressed in the checklist. Because the
proposed project is generally based on the land use designations, circulation patterns
etc. assigned to the project by the City of Dublin General Plan, the Initial Study relies on
a Program EIR certified by the City in 1993 for the Eastern Dublin General Plan
Amendment and Specific Plan (the "Eastern Dublin General Plan Amendment and
Specific Plan Environmental Impact Report, State Clearinghouse No. 91103064). That
EIR, also known in this Initial Study as the "Eastern Dublin EIR," evaluated the
following impacts: Land Use, Population, Employment and Housing, Traffic and
Circulation, Community Services and Facilities, Sewer, Water and Storm Drainage,
Soils, Geology and Seismicity, Biological Resources, Visual Resources, Cultural
Resources, Noise, Air Quality and Fiscal Considerations.
Even with mitigation, however, some of the identified significant impacts could not be
reduced to a less than significant level. Several of these impacts were cumulative level
impacts, such as loss of agriculture and open space, I-580 and other regional traffic
impacts, and air quality impacts. As required by CEQA, the Draft EIR identified project
alternatives, including No Project and No Development alternatives, a Reduced Land
Use Intensities alternative, and a Reduced Planning Area alternative, and analyzed
whether the alternatives would avoid any of the otherwise unavoidable impacts. As
further discussed below, the City Council adopted a modified version of the Reduced
Planning Area alternative after certifying the EIR as adequate and in compliance with
CEQA on May 10, 1993. (Resolution 51-93.) The City Council also certified an
Addendum dated May 4, 1993 which assessed the modifications to the Reduced
Planning Area alternative and concluded that this alternative "will have no
environmental impacts not addressed in the Draft Environmental Impact Report for the
Eastern Dublin General Plan Amendment and Specific Plan." (May 4, 1993 Addendum,
p. 1.) The Addendum further concluded that no subsequent or supplemental EIR was
required under CEQA Guidelines section 15162 or 15163 for approval of the modified
alternative.
A second Addendum was later prepared, dated August 22, 1994. The second
Addendum updated plans for providing sewer services to Eastern Dublin. The May 10,
1993 certified EIR, the May 4, 1993 Addendum and the August 22, 1994 Addendum are
collectively referred to hereafter as the Eastern Dublin EIR, or the "EDEIR" and are
incorporated herein by reference into this Initial Study. These documents are available
City of Dublin Page 2
Initial Study/Wallis Ranch/Trumark Project April 2014
for review at the Dublin Community Development Department during normal business
hours.
In 2005, a Supplemental EIR to the 1993 Eastern Dublin EIR was prepared for the
Dublin Ranch West project, also known as the Wallis Ranch, as well as other smaller
properties adjacent to the Dublin Ranch West site. This document will be referred to as
the "2005 SEIR." The Dublin Ranch West SEIR was certified by the City Council on
March 15, 2005, by City Council Resolution No. 42-05. This CEQA document analyzed
annexation of the property to the City of Dublin and Dublin San Ramon Services
District (DSRSD), amendments to the Dublin General Plan and Eastern Dublin Specific
Plan, a Planned Development prezoning and related Stage 1 Development Plan.
Following certification of the SEIR, the City of Dublin subsequently approved a PD
rezoning with related Stage 2 Development Plan for the Wallis site, a Site Development
Review (SDR) permit, a vesting tentative subdivision map and a Development
Agreement. This Supplemental EIR analyzed future development of up to 1,034
dwellings at a variety of densities (see SEIR Table 2).
The Dublin Ranch West has since been annexed into the City of Dublin and the Dublin
San Ramon Services District.
The 2005 SEIR analyzed agricultural resources, air quality, biological resources land
use, population, housing and employment, transportation and circulation and parks
and recreation.
In 2007, the City of Dublin approved a Mitigated Negative Declaration (MND) to
analyze improvements within approximately 11.6 acres of land located immediately of
the Wallis Ranch property that was the subject of the 2005 SEIR. This property is under
the same ownership as the Wallis Ranch, but is located in the unincorporated portion of
Contra Costa County rather than within Dublin and Alameda County. The applicant
proposed placement of an Emergency Vehicle Assess (EVA), a herpetological barrier
and a bioswale within this area. The MND was adopted by Dublin City Council
Resolution No. 18-07 on February 20, 2007. The proposed improvements were not
constructed and this 11.6-acre property is not part of the current development
application.
The subject of this Initial Study includes applications for a PD rezoning with amended
Stage 1 and Stage 2 Development Plan, A Site Development Review (SDR) permit, and a
Vesting Tentative Subdivision Map to change the number of dwellings units on this
184.1-acre site. The proposed Development Plan includes construction of up to 809
dwellings at various densities and product types, primary and internal roadways, two
neighborhood parks, a private park, permanent open spaces, public and semi-public
uses and other related improvements.
City of Dublin Page 3
Initial Study/Wallis Ranch/Trumark Project April 2014
Applicant:
Trumark Homes
4165 Blackhawk Plaza Circle, Suite 200
Danville CA 94506
Attn: Christopher Davenport
(925) 309 2503
Project Location and Context
The project area consists of 184.1 acres of land located in northern portion of Dublin
generally bounded by the Alameda/Contra Costa line to the north, Parks Reserve
Forces Training Area (Parks RFTA) to the west, Tassajara Road to the east and the
Tassajara Creek to the south.
The Assessors Parcel Number for the site is 986-0004-05.
Exhibit 1 depicts the regional setting of Dublin and Exhibit 2 shows the location of the
project site in context with nearby features, including nearby roadways and adjacent
creek.
The project site is fallow, with one inhabited residence (in the process of being vacated),
outbuildings and a historic school building adjacent to Tassajara Road. The easterly
portion of the site area includes Tassajara Creek, a major regional drainage facility.
Land uses surrounding the site include Parks RFTA to the west and along the southerly
boundary of the site. East of the project area is Tassajara Creek(which has been placed
in a conservation easement known as the Tassajara Creek Management Zone) and
Tassajara Road. A portion of the Silvera Ranch residential development is located
directly across Tassajara Road. Additionally, Quarry Lane School, a private K-12
education facility has been constructed east of the project. A residential project, Nielsen
Ranch, is also east of the project and has been approved for development of 36
residential lots but is as yet not constructed. A portion of Tassajara Creek forms the sites
southern boundary. An equestrian center, an East Bay Regional Park District staging
area and rural residential uses are also found south of the site.
Prior Environmental Review Documents
The project has been included in the following previous CEQA documents, as noted
below:
Eastern Dublin General Plan Amendment and Eastern Dublin Specific Plan EIR (State
Clearinghouse #91103064). A Program Environmental Impact Report for the Eastern
Dublin General Plan Amendment (Eastern Extended Planning Area) and the Eastern
Dublin Specific Plan (EDSP) was certified by the City Council in 1993 by Resolution
No. 51-93. This document and its related Addenda collectively are referred to as the
"Eastern Dublin EIR" or "EDEIR." It evaluated the following impacts:
City of Dublin Page 4
Initial Study/Wallis Ranch/Trumark Project April 2014
Land Use; Population, Employment and Housing; Traffic and Circulation;
Community Services and Facilities; Sewer, Water and Storm Drainage; Soils,
Geology and Seismicity; Biological Resources; Visual Resources; Cultural
Resources; Noise; Air Quality; and Fiscal Considerations.
The City adopted a Statement of Overriding Considerations (Resolution No. 53-93)
for the following impacts:
Cumulative loss of agriculture and open space land, cumulative traffic,
extension of certain community facilities (natural gas, electric and telephone
service), consumption of non-renewable natural resources, increases in energy
uses through increased water treatment and disposal and through operation
of the water distribution system, inducement of substantial growth and
concentration of population, earthquake ground shaking, loss or degradation
of botanically sensitive habitat, regional air quality, noise and alteration of
visual character.
The Eastern Dublin EIR was challenged in court and was found to be legally
adequate.
Two Addenda documents to the 1993 Eastern Dublin EIR have been approved by the
City, as described earlier.
Dublin Ranch West Supplemental EIR (SCH #200322082). In 2005, a Supplemental
EIR to the 1993 Eastern Dublin EIR was prepared for the Dublin Ranch West project,
also known as the Wallis Ranch, as well as other smaller properties adjacent to the
Dublin Ranch West site. The Dublin Ranch West SEIR was certified by the City
Council on March 15, 2005, by City Council Resolution No. 42-05. This CEQA
document analyzed annexation of the property to the City of Dublin and Dublin San
Ramon Services District (DSRSD), amendments to the Dublin General Plan and
Eastern Dublin Specific Plan, a Planned Development prezoning and Stage 1
Development Plan. Following certification of the SEIR, the City of Dublin
subsequently approved a PD rezoning with related Stage 2 Development Plan for
the site, a Site Development Review (SDR) permit, a vesting tentative subdivision
map and a Development Agreement.
The SEIR analyzed traffic and transportation and other impacts of constructing 1,034
dwellings on the site, although the City ultimately approved 935 dwellings.
This SEIR identified significant and unavoidable impacts with respect to project
exceedances of Bay Area Air Quality Management District air quality standards on a
project and cumulative level.
2007 MND. In 2007, the City of Dublin approved a Mitigated Negative Declaration
(MND) to analyze improvements within approximately 11.6 acres of land located
immediately of the Wallis Ranch property that was the subject of the 2005 SEIR. This
property is under the same ownership as the Wallis Ranch, but is located in the
unincorporated portion of Contra Costa County rather than within Dublin and
Alameda County. The analyzed the proposed placement of an Emergency Vehicle
City of Dublin Page 5
Initial Study/Wallis Ranchrfrumark Project April 2014
Assess (EVA), a herpetological barrier and a bioswale within this area. The MND
was adopted by Dublin City Council Resolution No. 18-07 on February 20, 2007.
Proposed land use approvals included an amended Stage 1 Development Plan for
Dublin Ranch West as well as a Vesting Master and Tentative Maps, Site
Development Review and Development Agreement.
The proposed improvements were not constructed and this 11.6-acre property is not
part of the current development application.
City of Dublin Page 6
Initial Study/Wallis Ranch/Trumark Project April 2014
Project Description
Overview. The proposed project includes amending existing land use entitlements
granted by the City of Dublin and developing up to 809 dwellings at various densities
and product types on the site as well as parks, open spaces, public/semi-public uses
and infrastructure improvements. If approved, there would be a reduction of
approximately 126 dwellings from existing City of Dublin approvals on the site. The
existing residence and associated outbuildings are proposed to be demolished. The
historic school building would be reconstructed on the site using historic building
material supplemented by other materials to replicate historic structures. The existing
Development Agreement between the City and the property owner requires the owner
to relocate the historic Antone School on the site. If the structure is damaged during
relocation, the owner is required to construct a similar structure as approved by the
City of Dublin Community Development Director.
The applicant has requested approvals of the following in order to implement the
project: a Stage 2 Development Plan, a Site Development Review (SDR) Permit and a
Vesting Tentative Map. The existing Development Agreement may be amended as part
of this project, or a new Development Agreement negotiated between the applicant and
City of Dublin.
Approved Development Plan. The approved development plan for the site is shown on
Exhibit 3. The development plan was based on Alternative 3 contained in the 2005
SEIR which moved the Neighborhood Park to border Tassajara Road. The Development
Plan approved by the City in 2005 and modified in 2007 allows the construction of up to
935 dwellings including a combination of Low Density Residential dwellings, Medium
Density Residential dwellings and Medium-High Density Residential dwellings.
Medium and Medium-High Density dwellings would be constructed in the
approximate center of the site, with the Low Density Residential dwellings located in
the northwest portion. A Neighborhood Park would be located in the southern portion
of the site with a 1.9-acre Semi Public use located in the southern portion of the site
adjacent to Tassajara Road.
The eastern portion of the site adjacent to Tassajara Creek is retained as permanent
Open Space through previous recordation of a permanent non-build easement.
Access into the site is provided by two existing roadways from Tasssjara Road with
associated bridges over Tassajara Creek into the site. The on-site main roadway is to be
extended in a northwesterly direction to provide access to individual neighborhoods on
the site. The second access is provided into the site from Tassajara Road with a bridge
crossing Tassajara Creek south of the main drive. Both bridges over Tassajara Creek
have been constructed in accordance with approved plans and all required local, state
and federal agency permits.
Proposed Development Plan. The proposed Development Plan would be similar to the
approved plan, with the proposed changes listed below, including build-out of fewer
City of Dublin Page 7
Initial Study/Wallis Ranch/Trumark Project April 2014
dwellings. The area of development and ground disturbance on the site would be the
same as established in the approved development plan.
• The total number of dwellings would be reduced from 935 to up to 809. See Table
1,below.
• In addition a public Neighborhood Park included in the approved plan, bisected
by the Tassajara Creek Conservation Area, a 3.0 gross acre private park would be
provided in the approximate center of the site.
• The main interior roadway would be located in a more westerly location than
shown in the approved plan
Proposed public Neighborhood Parks, Open Space areas and the Public/Semi-Public
area would remain the same as the approved plan and would contain approximately
the same acreage as approved.
Exhibit 4 shows the proposed development plan for this project. Table 1 compares
approved and proposed land uses on the project site.
Table 1. Approved v. Proposed Development Plans
Land Use Type Approved Development Proposed Develo ment
Gross Acres Dwellings Gross Acres Dwellings
Low Density Res. 15.4 58 15.4 92
Medium Density 57.1 629 57.1 531
Res.
Med.High Density 13.1 248 13.1 186
Res.
Water Quality 2.9 -- 2.9 --
Basin
Neighborhood 10.4 -- 10.4 --
Park
Open Space 83.3 --
Semi Public 1.9 -- 1.9 --
Total 184.1 935 184.1 1 809
Source: Project Applicant, 2013
Note:the 2005 SEIR analyzed development up to 1,034 dwellings on the site.
Circulation and access. Vehicular access to and from the site is currently provided from
Tassajara Road via two roadways. Both roads traverse Tassajara Creek via existing
bridges that would extend into the interior of the site and provide access to all of the
neighborhoods. Smaller private roadways would be constructed off of the main road for
access into each neighborhood and private in-tract streets would provide access to
individual dwellings. Road widths would vary from 74 feet for the main project access
road to 34.5 feet for roads within neighborhoods.
Sidewalks or walkways would be provided on one or both sides of all streets.
City of Dublin Page 8
Initial Study/Wallis Ranch/Trumark Project April 2014
A 6-ft. wide concrete sidewalk would be constructed along the project frontage on the
western side of Tassajara Road. The sidewalk would also serve as a portion of a regional
recreation trail. This would be consistent with the General Plan Circulation Element.
Additionally, an on-site and at-grade trail would be constructed extending from the
southwesterly edge of the site and adjacent to the western edge of Tassajara Creek
would link the East Bay Regional Park District trail to Contra Costa County to the
north.
Building architecture and design. Future dwellings that would be constructed on the
project site would include single-family detached dwellings (up to 622 dwellings),
townhouses (up to 126 dwellings) and three-plex attached dwellings (up to 61
dwellings).
Future dwellings would generally be of two-and three-story construction and would
reflect a rural/agrarian design theme. Exterior building materials would consist of
stucco, board and batten siding or lap siding. Roof material would consist of
composition shingle or concrete tile. A variety of window and door treatments would
be designed and each dwelling would have accent material to present an aesthetically
pleasing appearance.
A number of floor plans and sizes would be constructed. Dwelling unit sizes would
range from approximately 1,960 to 4,158 square feet each.
Each dwelling would include vehicle parking in the form of enclosed garages or open
parking that would meet City of Dublin parking requirements.
Landscaping. The applicant proposes a comprehensive landscape plan for the project.
Landscaping would including planting of street trees along all project roadways, public
and private parks and open space slope areas. An enhanced entryway would be
provided at the main project road along Tassajara Road. The entry area would consist of
project identification sign, monumentation and enriched landscaping.
Utility services. Domestic water, recycled water and sewer service would be provided
by Dublin San Ramon Services District (DSRSD). The project developer would be
required to install mainline extension of sewer along the frontage, to the entrance of the
project, as well as the in-tract water and sewer lines and laterals.
Surface water quality improvements would include a central water
quality/hydromodification pond in the south-central portion of the site. Bio-swales to
filter stormwater runoff would also be installed adjacent to most of the streets in the
project.
Grading. The applicant proposes to grade the site to allow construction of the
residential areas, roadways, parks and related improvements. Generally, the site would
be re-contoured from its present condition to provide a flatter development area in the
central portion of the site. The existing open space areas on the west side of the project
site would not be graded. A number of retaining walls are proposed on the site. It is
City of Dublin Page 9
Initial Study/Wallis Ranch/Trumark Project April 2014
anticipated that cut and fill will balance on the site, which means no dirt would be
imported into or exported from the site.
Erosion controls would be implemented during grading activities pursuant to City and
Regional Water Quality Board requirements, as enforced by the City of Dublin, to
protect surface water quality.
Inclusionary housing. The inclusionary housing requirement was met for Dublin
Ranch West (Wallis Ranch) by the Fairway Ranch (The Groves) development and
therefore, no further requirement is necessary. With the reduction of units with this
application from 935 to approximately 809, the original requirement of 117 units would
be reduced to 101 thereby potentially over-providing 16 inclusionary units.
Historic resource: The Antone School building is located on the site. This building has
been relocated to the project site from elsewhere on the larger Dublin Ranch site. The
current Development Agreement for the property requires the developer to relocate this
structure on the site and restore it. If the structure is damaged during relocation, the
Development Agreement requires the developer to construct a replacement structure
with the exterior design resembling the current building, as approved by the Dublin
Community Development Department.
Requested land use approvals. A number of land use approvals are required from the
City of Dublin to construct the project as proposed. These are described in more detail
below.
PD Rezoning with Amended Stage 1 & Stage 2 Development Plan. Previously
approved Stage 1 and Stage 2 Development Plans and associated land use
development standards would be replaced by the proposed Development Plan
shown on Exhibit 4.
Site Development Review (SD R). A Site Development Review permit has been
requested to approve exterior building architecture, landscaping, walls and fences
and related improvements.
Vesting Tentative Map. The Vesting Tentative Tract Map is shown on Exhibit 5.
Approval of the subdivision map would create a number of smaller building lots for
individual dwellings, multi-family housing, parks, open space, roads and utilities.
Development Agreement. A 15 year Development Agreement was approved or this
property in 2009, and remains in force until 2024. In accordance with the provisions
of the development Agreement, the property owner has the right to assign all or a
portion of the Agreement to any potential purchaser of all or a portion of the site to
the satisfaction of the City Manager. The current Development Agreement may be
amended or a new Agreement negotiated.
City of Dublin Page 10
Initial Study/Wallis Ranch/Trumark Project April 2014
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1. Project description: Constructing up to 809 dwellings at various densities
and product types on the site, as well as two public
and one private parks, open spaces, a public/semi-
public site and roads. The proposed project would
also include grading of the site to accommodate
proposed uses and extension of utilities to and within
the site.
2. Lead agency: City of Dublin
Community Development Department
100 Civic Plaza
Dublin CA 94568
3. Contact persons: Michael A. Porto
Consulting Planner
(925) 833 6610
4. Project location: Generally located on the west side of Tassajara Road
and, south of the City limit line and east of Parks
RFTA
5. Project sponsor: Christopher Davenport
Trumark Homes
6. General Plan designation: Low Density Residential
Medium Density Residential
Medium/High Density Residential
Open Space
Public/Semi-Public
7. Zoning: PD-Planned Development
8. Other public agency required approvals:
• Approval of PD-Planned Development zoning (City of Dublin);
• Approval of a Stage 2 Development Plan (City of Dublin);
• Approval of a Vesting Tentative Map (City of Dublin);
• Approval of a Site Development Review (SDR) Permit;
• Approval of Development Agreement (City of Dublin, possible);
• Notice of Intent (State Water Resources Control Board);
• Issuance of building and grading permits (City of Dublin); and
• Approval of water and sewer connections (DSRSD)
City of Dublin Page 16
Initial Study/Wallis Ranch/Trumark Project April 2014
Environmental Factors Potentially Affected
The environmental factors checked below would be potentially affected by this project,
involving at least one impact that is a "potentially significant impact" as indicated by the
checklist on the following pages.
_ Aesthetics _ Agricultural - Air Quality
Resources
Biological _ Cultural Resources - Geology/Soils
Resources
_ Hazards and - Hydrology/Water _ Land Use/
Hazardous Quality Planning
Materials
Mineral Resources -- Noise -- Population/
Housing
-- Public Services _ Recreation - Transportation
Circulation
-- Utilities/Service - Mandatory
Systems Findings of
Significance
Determination (to be completed by Lead Agency):
On the basis of this initial evaluation:
I find that the proposed project could not have a significant effect on the
environment and the previous Negative Declaration certified for this project by the
City of Dublin adequately addresses potential impacts.
_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 the mitigation
measures described on an attached sheet have been added to the project. A Negative
Declaration will be prepared.
X I find that although the proposed Project could have a significant effect on the
environment, there will not be any new or substantially more severe significant effect in
this case because all potentially significant effects: a) have been analyzed adequately in
earlier CEQA documents pursuant to applicable standards; and (b) have been avoided
or mitigated pursuant to those earlier CEQA documents, including revisions or
mitigation measures that are imposed on the proposed Project, except for those impacts
which were identified as significant and unavoidable and for which Statements of
Overriding Considerations were previously adopted by the City. An Addendum to the
Eastern Dublin Environmental Impact Report, the 2005 Dublin Ranch West
Supplemental Environmental Impact Report, and 2007 MND will be prepared.
_I find that the proposed project could have a significant effect on the environment,
there will not be a significant effect in this case because all potentially significant effects
City of Dublin Page 17
Initial Study/Wallis Ranchrfrumark Project April 2014
(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 P4f-(v are imposed on the proposed project.
Signature: r s'�-� Date: (10' !
Printed Name: 1.&tw A• PtN-Ev For:
City of Dublin Page 18
Initial Study/Wallis Ranch/Trumark Project April 2014
Evaluation of Environmental Impacts
1) A brief explanation is required for all answers except "no impact" answers that are
adequately supported by the information sources a lead agency cites in the
parenthesis following each question. A "no impact" answer is adequately
supported if the referenced information sources show that the impact simply does
not apply to projects like the one involved (e.g. the project falls outside a fault
rupture zone). A "no impact" answer should be explained where it is based on
project-specific factors as well as general factors (e.g. the project will not expose
sensitive receptors to pollutants, based on a project-specific screening analysis).
2) All answers must take account of the whole action involved, including off-site as
well as on-site, cumulative as well as project-level, indirect as well as direct, and
construction as well as operational impacts.
3) Once the lead agency has determined that a particular physical impact may occur,
then the checklist answers must indicate whether the impact is potentially
significant, less-than-significant with mitigation, or less-than-significant.
"Potentially Significant Impact" is appropriate if there is substantial evidence that
an effect may be significant. If there are one or more "Potentially Significant
Impact" entries when the determination is made, an EIR is required.
4) "Negative Declaration: Less-than-Significant With Mitigation Incorporated"
applies where the incorporation of mitigation measures has reduced an effect from
"Potentially Significant Impact" to a "Less-than-Significant Impact." The lead
agency must describe the mitigation measures and briefly explain how they reduce
the effect to a less-than-significant level (mitigation measures from Section 17,
"Earlier Analysis," as described in (5) below, may be cross-referenced).
5) Earlier analyses may be used where, pursuant to the tiering, program EIR, or other
CEQA process, an effect has been adequately analyzed in an earlier EIR or
negative declaration. Section 15063 (c) (3) (D). The checklist will include a response
"no new impact" in these circumstances. In this case, a brief discussion should
identify the following:
a) Earlier Analysis Used. Identify and state where they are available for
review.
b) Impacts Adequately Addressed: Identify which effects from the above
checklist were within the scope of and adequately analyzed in an earlier
document pursuant to applicable legal standards, and state whether such
effects were addressed by mitigation measures based on the earlier
analysis.
c) Mitigation Measures. For effects that are "Less-Than-Significant with
Mitigation Measures Incorporated," describe the mitigation measures
which were incorporated or refined from the earlier document and the
extent to which they address site-specific conditions for the project.
City of Dublin Page 19
Initial Study/Wallis Ranch/Trumark Project April 2014
6) Lead Agencies are encouraged to incorporate into the checklist references to
information sources for potential impacts (e.g. general plans, zoning ordinances,
etc.). Reference to a previously prepared or outside document should, where
appropriate, include a reference to the page or pages where the statement is
substantiated.
7) Supporting Information Sources: A source list should be attached and other
sources used or individuals contacted should be cited in the discussion.
8) This is a suggested form and lead agencies are free to use different formats;
however, lead agencies should normally address the questions from this checklist
that are relevant to a project's environmental effects in whatever format is selected.
9) The explanation of each agency should identify the significance criteria or
threshold, if any, used to evaluate each question and the mitigation measures
identified, if any, to reduce the impact to a less than significant level.
City of Dublin Page 20
Initial Study/Wallis Ranch/Trumark Project April 2014
Environmental Impacts (Note: Source of determination listed in parenthesis. See listing of
sources used to determine each potential impact at the end of the checklist)
Note: A full discussion of each item is found Potentially Less Than Less than No New
following the checklist. Significant Significant Significant Impact
Impact With Impact
Mitigation
1. Aesthetics. Would the project:
a) Have a substantial adverse effect on a scenic X
vista? (Source: 1,2,5)
b) Substantially damage scenic resources,including X
but not limited to trees,rock outcroppings,and
historic buildings within a state scenic highway?
(Source: 1,2,5)
c) Substantially degrade the existing visual character X
or quality of the site and its surroundings?
(Source: 5)
d) Create a new source of substantial light or glare X
which would adversely affect day or nighttime
views in the area? (Source: 1,2,5)
2.Agricultural Resources
Would the project:
a) Convert Prime Farmland, Unique Farmland or
Farmland of Statewide Importance,as shown on
the maps prepared pursuant to the Farmland X
Mapping and Monitoring Program of the
California Resources Agency,to a non-
agricultural use?(Source: 1,2)
b)Conflict with existing zoning for agriculture use, X
or a Williamson Act contract? (Source: 1,2)
c) Involve other changes in the existing environment
which,due to their location or nature,could
result in conversion of farmland to a non- X
agricultural use? (Source: 1,2,5)
3.Air Quality (Where available,the significance
criteria established by the applicable air quality
management district may be relied on to snake
the following determinations). Would the
project:
a)Conflict with or obstruct implementation of the X
applicable air quality plan? (Source: 1,4)
b)Violate any air quality standard or contribute
substantially to an existing or projected air X
quality violation? (Source: 2)
City of Dublin Page 21
Initial Study/Wallis RanchfTrumark Project April 2014
Potentially Less Than Less than No New
Significant Significant Significant Impact
Impact With Impact
Mitigation
c) Result in a cumulatively considerable net increase X
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? (2)
d) Expose sensitive receptors to substantial pollutant X
concentrations? (Source: 2,5)
e) Create objectionable odors affecting a substantial X
number of people? (Source: 6)
4.Biological Resources. Would the project
a) Have a substantial adverse effect,either directly
through habitat modifications,on any species X
identified as a candidate,sensitive,or special
status species in local or regional plans,policies
or regulations,or by the California Department
of Fish and Game or the U.S. Fish and Wildlife
Service?(Source: 1,2,6)
b) Have a substantial adverse effect on any riparian X
habitat or other sensitive natural community
identified in local or regional plans,policies or
regulations or by the California Department of
Fish and Game or the U.S. Fish and Wildlife
Service? (Source: 1,2.6)
c) Have a substantial adverse effect on federally X
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?
(Source: Source: 2,3,6)
d) Interfere substantially with the movement of any X
native resident or migratory fish or wildlife
species or with established native resident or
migratory wildlife corridors,or impede the use
of native wildlife nursery sites? (Source: 2,5)
e)Conflict with any local policies or ordinances X
protecting biological resources,such as tree
protection ordinances?(Source: 2,6)
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Potentially Less Than Less than No New
Significant Significant Significant Impact
Impact With Impact
Mitigation
f) Conflict with the provision of an adopted Habitat
Conservation Plan,Natural Community
Conservation Plan or other approved local, X
regional or state habitat conservation plan?
(Source: 6)
5.Cultural Resources. Would the project
a) Cause a substantial adverse impact in the
significance of a historical resource as defined in X
Sec. 15064.5? (Source: 1,2)
b) Cause a substantial adverse change in the
significance of an archeological resource X
pursuant to Sec. 15064.5 (Source: 1,2)
c) Directly or indirectly destroy a unique X
paleontological resource,site or unique geologic
feature?(Source: 1,2)
d) Disturb any human remains,including those X
interred outside of a formal cemetery? (2)
6.Geology and Soils. Would the project
a) Expose people or structures to potential
substantial adverse effects,including the risk of
loss,injury,or death involving:
i) Rupture of a known earthquake fault,as delineated
on the most recent Earthquake Fault Zoning Map X
issued by the State Geologist or based on other
substantial evidence of a known fault(Source: 2,
3,6)
ii) Strong seismic ground shaking (2,6) X
iii) Seismic-related ground failure,including X
liquefaction? (2,6)
iv) Landslides? (2,6) X
b) Result in substantial soil erosion or the loss of X
topsoil?(Source: 2,6)
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- X
or off-site landslide,lateral spreading,
subsidence,liquefaction or similar hazards
(Source: 2,6)
d) Be located on expansive soil,as defined in Table
18-1-B of the Uniform Building Code(1994),
creating substantial risks to life or property? X
(Source: 2,6)
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Potentially Less Than Less than No New
Significant Significant Significant Impact
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Mi ti Qation
e) Have soils incapable of adequately supporting the
use of septic tanks or alternative wastewater
disposal systems where sewers are not available X
for the disposal of wastewater?(Source: 1,2)
7.Hazards and Hazardous Materials. Would the
project:
a)Create a significant hazard to the public or the
environment through the routine transport,use or
disposal of hazardous materials X
(Source: 2,6)
b)Create a significant hazard to the public or the X
environment through reasonably foreseeable
upset and accident conditions involving the
release of hazardous materials into the
environment? (Source: 2,6)
c) Emit hazardous emissions or handle hazardous
materials or acutely hazardous materials, X
substances,or waste within one-quarter mile of
an existing or proposed school?(Source: 2,6)
d) Be located on a site which is included on a list of
hazardous materials sites compiled pursuant to
Government Code Sec.65962.5 and,as a result, X
would it create a significant hazard to the public
or the environment? (Source: 6)
e) For a project located within an airport land use X
plan or,where such a plan has not been adopted
within two miles of a public airport of public use
airport,would the project result in a safety
hazard for people residing or working in the
project area? (Source: 2,6)
f) For a project within the vicinity of private airstrip, X
would the project result in a safety hazard for
people residing or working in the project area?
(Source: 2,6)
g) Impair implementation of or physically interfere
with the adopted emergency response plan or
emergency evacuation plan? X
(Source: 2,6)
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Potentially Less Than Less than No New
Significant Significant Significant Impact
Impact With Impact
Mitigation
h) Expose people or structures to a significant risk of
loss,injury or death involving wildland fires, X
including where wildlands are adjacent to
urbanized areas or where residences are
intermixed with wildlands?(Source: 2,6)
8.Hydrology and Water Quality. Would the project:
a) Violate any water quality standards or waste
discharge requirements? (Source: 2,4 X
b)Substantially deplete groundwater supplies or
interfere substantially with groundwater recharge
such that there would be a net deficit in aquifer X
volume or a lowering of the local groundwater
table level (e.g.the production rate of existing
nearby wells would drop to a level which would
not support existing land uses or planned uses
for which permits have been granted?(1,2)
c) Substantially alter the existing drainage pattern of X.
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? (Source: 2,5,6)
d) Substantially alter the existing drainage pattern of X
the site or areas,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?(Source: 2,5)
e) Create or contribute runoff water which would X
exceed the capacity of existing or planned
stormwater drainage systems or provide
substantial additional sources of polluted runoff?
(Source: 4,5)
f)Otherwise substantially degrade water quality? X
(Source: 4,5)
g) Place housing within a 100-year flood hazard area
as mapped on a federal Flood Hazard Boundary
or Flood Insurance Rate Map or other flood X
delineation map?(Source: 4)
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Potentially Less Than Less than No New
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Mitigation
h) Place within a 100-year flood hazard area
structures which would impede or redirect flood X
flows?(Source: 4)
i) Expose people or structures to a significant risk of
loss,injury,and death involving flooding, X
including flooding as a result of the failure of a
levee or dam? (2)
j) Inundation by seiche,tsunami or mudflow? (5) X
9.Land Use and Planning. Would the project:
a) Physically divide an established community? X
(Source: 1,2,5)
b) Conflict with any applicable land use plan,policy,
or regulation of an agency with jurisdiction over
the project(including but not limited to the X
general plan,specific plan, or zoning ordinance)
adopted for the purpose of avoiding or
mitigating an environmental effect?(Source: 1,
1,2)
c) Conflict with any applicable habitat conservation
plan or natural community conservation plan? X
(2, 6)
10.Mineral Resources. Would the project
a) Result in the loss of availability of a known
mineral resource that would be of value to the X
region and the residents of the state?(Source: 1,
2)
b) Result in the loss of availability of a locally
important mineral resource recovery site
delineated on a local general Plan,specific plan X
or other land use plan? (Source:1,2)
11.Noise. Would the proposal result in:
a) Exposure of persons to or generation of noise X
levels in excess of standards established in the
local general plan or noise ordinance,or
applicable standards of other agencies?(2,3)
b) Exposure of persons or to generation of excessive
groundborne vibration or groundborne noise X
levels? (Source: 2,6)
c)A substantial permanent increase in ambient noise X
levels in the project vicinity above existing
levels without the project? (2,5)
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Mitigation
d)A substantial temporary or periodic increase in X
ambient noise levels in the project vicinity above
levels existing without the project?(2,5)
e) For a project located within an airport land use X
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 n the project area to excessive noise
levels?(2, 6)
f) For a project within the vicinity of a private X
airstrip,would the project expose people
residing or working in the project area to
excessive noise levels? (Source: 2,6)
12.Population and Housing. Would the project
a) Induce substantial population growth in an area, X
either directly or indirectly (for example,
through extension of roads or other
infrastructure)? (Source: 2, 5)
b) Displace substantial numbers of existing housing,
necessitating the construction of replacement X
housing elsewhere?(5)
c) Displace substantial numbers of people,
necessitating the construction of replacement of X
housing elsewhere? (Source: 5)
13.Public Services. Would the proposal:
a) Would the project result in substantial adverse
physical impacts associated with the provision of
new or physically altered governmental
facilities,need for new or physically altered
government facilities,the construction of which
could cause significant environmental impacts,
in order to maintain acceptable service rations,
response times or other performance objectives
for any of the public services? (Sources: 2,4)
Fire protection X
Police protection X
Schools X
Parks X
Other public facilities X
Solid Waste X
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Potentially Less Than Less than No New
Significant Significant Significant Impact
Impact With Impact
Mitigation
14.Recreation:
a) Would the project increase the use of existing X
neighborhood and regional parks or recreational
facilities such that substantial physical
deterioration of the facility would occur or be
accelerated (Source: 2,4)
b) Does the project include recreational facilities or X
require the construction or expansion of
recreational facilities which might have an
adverse physical effect on the environment?
(Source: 2,4.6)
15.Transportation and Traffic. Would the project:
a)Cause an increase in traffic which is substantial in X
relation to the existing traffic load and capacity
of the street system (i.e. result in a substantial
increase in either the number of vehicle trips,the
volume to capacity ratio on roads or congestion
at intersections)? (2,3)
b) Exceed,either individually or cumulatively,a X
level of service standard established by the
County Congestion Management Agency for
designated roads or highways?(2,3)
c) Result in a change in air traffic patterns,including
either an increase in traffic levels or a change in X
location that results in substantial safety risks?
(2,3)
d) Substantially increase hazards due to a design
feature(e.g. sharp curves or dangerous
intersections)or incompatible uses,such as farm X
equipment? (4)
e) Result in inadequate emergency access?(4) X
f) Result in inadequate parking capacity?(4) X
g)Conflict with adopted policies,plans or programs X
supporting alternative transportation (such as bus
turnouts and bicycle facilities)
(1,4)
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Potentially Less Than Less than No New
Significant Significant Significant Impact
Impact With Impact
Miti-ation
16.Utilities and Service Systems. Would the project
a) Exceed wastewater treatment requirements of the X
applicable Regional Water Quality Control
Board? (2, 4)
b) Require or result in the construction of new water X
or wastewater treatment facilities or expansion
of existing facilities,the construction of which
could cause significant environmental effects?
(2,4)
c) Require or result in the construction of new storm X
water drainage facilities or expansion of existing
facilities,the construction of which could cause
significant environmental effects? (4)
d) Have sufficient water supplies available to serve X
the project from existing water entitlements and
resources,or are new or expanded entitlements
needed?(4)
e) Result in a determination by the wastewater X
treatment provider which serves or may serve
the project that it has adequate capacity to serve
the project's projected demand in addition to the
providers existing commitments?(4)
f) Be served by a landfill with sufficient permitted X
capacity to accommodate the project's solid
waste disposal needs?(4)
g) Comply with federal,state and local statutes and X
regulations related to solid waste? (4)
17.Mandatory Findings of Significance.
a) Does the project have the potential to degrade X
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, substantially reduce
the number of 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?
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Potentially Less Than Less than No New
Significant Significant Significant Impact
Impact With Impact
Mitigation
b) Does the project have impacts that are X
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 X
beings,either directly or indirectly?
Sources used to determine potential environmental impacts
1. Eastern Dublin General Plan Amendment/Specific Plan EIR
2 2005 Dublin Ranch West SEIR
3 Trip Generation Analysis (TJKM)
4. Discussion with City staff or service provider
5. Site Visit
6. Other Source
XVII. Earlier Analyses
a) Earlier analyses used. Identify earlier analyses and state where they are available for
review.
Portions of the environmental setting, project impacts and mitigation measures for this
Initial Study refer to environmental information contained in the 1993 Eastern Dublin
General Plan Amendment and Specific Plan Environmental Impact Report (State
Clearinghouse No. 91103064), hereinafter referred to as the Eastern Dublin EIR. The
Eastern Dublin EIR is a Program EIR which was prepared for the Eastern Dublin
General Plan Amendment and Specific Plan of which this Project is a part. It was
certified by the Dublin City Council on May 10, 1993. Following certification of the EIR,
the Council adopted a Statement of Overriding Considerations for impacts including
but not limited to: cumulative traffic, extension of certain community facilities (natural
gas, electric and telephone service), regional air quality, noise and visual.
The Eastern Dublin EIR contains a large number of mitigation measures which apply to
this Project and which would be applied to any development within the project area.
Specific mitigation measures identified in the certified Eastern Dublin EIR for potential
impacts are referenced in the text of this Initial Study.
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Initial Study/Wallis Ranchrfrumark Project April 2014
This Initial Study relies on 2005 Dublin Ranch West Supplemental EIR (State
Clearinghouse #2003022082), certified by the Dublin City Council by Resolution No. 42-
05 on March 15, 2005.
This Initial Study also relies on a Mitigated Negative Declaration for an 11.6-acre site
located just north of the Wallis Ranch but included in the earlier City of Dublin
approval for the site (State Clearinghouse #2003022082), certified by the Dublin City
Council by Resolution No. XX-07 on February 20, 2007.
Pursuant to CEQA Guidelines Section 15162 and 15163, this Initial Study is intended to
identify the potential for any new or substantially increased significant impacts on or of
the project which were not evaluated in the Eastern Dublin EIR and the 2005 SEIR and
which would require additional environmental review.
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Initial Study/Wallis Ranch/Trumark Project April 2014
Attachment to Initial Study
Discussion of Checklist
1. Aesthetics
Environmental Setting
The project is set in an a portion of Eastern Dublin that is transitioning to urban uses
under the auspices of the City of Dublin General Plan Amendment and Eastern Dublin
EIR, adopted in 1993. The existing natural topography includes consists of steep slopes
in the western portion of the site adjacent to Parks RFTA transitioning to moderate to
gentle slopes in the approximate center of the site. The portion of the site lying adjacent
to Tassajara Creek is generally flat.
The portion of the project site adjacent to Tassajara Creek is heavily wooded. This area
is protected by an existing conservation easement and trees and other vegetation and
would not be disturbed as part of this project.
Tassajara Road from the I-580 freeway to the south, to the Alameda County-Contra
Costa County line just north of the Dublin Ranch West site is classified as a Scenic Route
in the Alameda County Scenic Route Element of the General Plan, which has also been
adopted by the City of Dublin by reference in the City of Dublin General Plan.
No existing parks, playgrounds, scenic vistas or other places for public gathering are
found on the project site.
As a largely rural area, minimal light sources exist on the project site.
Regulatory fi,ainework
Dublin General Plan. The project area is included in the Eastern Dublin Extended
Planning Area. Implementing Policy C.2 of the General Plan states that "proposed site
grading and means of access will not disfigure ridgelands." Further, Implementing
Policy C. 5 requires development projects to be consistent with all applicable General
Plan and Specific Plan policies."
Eastern Dublin Specific Plan. The City of Dublin adopted the Eastern Dublin Specific
Plan (EDSP) in 1993 to guide the future development of approximately 3,200 acres of
land in the eastern Dublin area. The Specific Plan includes a number of policies and
programs dealing with visual resources, including but not limited to protection of
ridgelines and ridgelands, scenic corridors, and hillside development.
Previous CEQA documents
Eastern Dublin EIR. The Eastern Dublin EIR contains a number of mitigation measures
to reduce anticipated visual resource impacts from the General Plan and EDSP project.
These include:
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Initial Study/Wallis Ranch/Trumark Project April 2014
• Mitigation Measure 3.8/1.0 reduced project impacts related to standardized tract
development (IM 3.8/B) to a less-than-significant level. This mitigation requires
future developers to establish visually distinct communities which preserves the
character of the natural landscape by protecting key visual elements and
maintaining views from major travel corridors.
• Mitigation Measure 3.8/2.0 reduced the impact of converting the rural and open
space character of the General Plan Amendment and Specific Plan area (IM
3.8/B) but not to a less-than-significant level. The mitigation measure requires
implementation of the land use plan that emphasizes retention of predominant
natural features. Even with adherence to this measure, IM 3.8/B would remain
significant and unavoidable on both a project and cumulative level.
• Mitigation Measure 3.8/3.0 would reduce the impact of obscuring distinctive
natural features of the General Plan Amendment and Specific Plan area (IM
3.8/C) but not to a less-than-significant level. The mitigation measure requires
implementation of the land use plan that emphasizes retention of predominant
natural features.
• Mitigation Measures 3.8/4.0-4.5 reduced the impact of altering the visual quality
of hillsides (IM 3.8/D) to a less-than-significant level. These mitigation measures
require implemtation of appropriate Eastern Dublin Specific Plan policies
including but not limited to use of sensitive grading design to minimize grading,
use of existing topographic features, limiting use of flat pads for construction,
using building designs that conform to natural land forms, recontouring hillside
to resemble existing topography and minimizing the height of cut and fill slopes.
• Mitigation Measures 3.8/5.0-5.2 reduced the impact of altering the visual quality
of ridges (IM 3.8/E) to a less-than-significant level. These mitigation measures
limit development on main ridges that border the Specific Plan area to the north
and east but are allowed on foreground hills, and would limit development in
locations where scenic views would be obscured or would extend above a
ridgetop.
• IM 3.8/F analyzed alteration of the visual character of the Eastern Dublin
flatlands. No mitigation measures were identified and the impact was identified
as significant and unavoidable.
• Mitigation Measure 3.8/6.0 reduced the impact of altering the visual quality of
watercourses (IM 3.8/G) to a less-than-significant level. This mitigation measure
protects Tassajara Creek and other stream courses from unnecessary alteration or
disturbance, and adjoining development should be sited to maintain visual
access to stream corridors.
• Mitigation Measures 3.8/7.0 and 7/1 reduced impacts on scenic vistas (IM 3.8/I)
to a less-than-significant level. These mitigation measures require protection of
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Initial Study/Wallis Ranch/Trumark Project April 2014
designated open space areas and directs the City to conduct a visual survey of
the EDSP area to identify and map viewsheds.
2005 SEIR. Aesthetics were addressed in the Initial Study for the SEIR. No
potentially significant aesthetic impacts or mitigation measures were identified in
this document.
The proposed project will be required to adhere to applicable mitigation measures
related to aesthetics set forth in the Eastern Dublin EIR.
Project Impacts
a,b) Have a substantial adverse impact on a scenic vista or substantially damage scenic
resources,within a state scenic highway? No New Impact. The Eastern Dublin EIR
identifies that implementation of the Eastern Dublin Specific Plan would result in
a potentially significant impact (Impact 3.8/I), in that development in the Eastern
Dublin planning area will alter the character of existing scenic vistas and may
obscure important sightlines. Adherence to Mitigation Measure 3.8/7.0
contained in the Eastern Dublin EIR reduced this impact to a less-than-significant
impact. This measure requires the City to preserve views of designated open
space areas and to complete a visual assessment and guidelines for the Eastern
Dublin area.
There are no scenic vistas visible from public vantage points along Tassajara
Road. The proposed project would include grading of the project site from its
existing natural condition so that access roads, building pads, water quality
improvements and related improvements. The Eastern Dublin EIR identified the
potential for alteration of visual resources along scenic routes, including
Tassajara Road (Impact 3.8/J). The same portion of the site would be disturbed
for development as has been previously analyzed in the 2005 SEIR and approved
by the City of Dublin. The heavily wooded areas of the Wallis site along
Tassajara Creek are protected by a conservation easement.
All of the mitigation measures contained in the Eastern Dublin EIR and the
visual policies contained in the EDSP will apply to this project. There are no
impacts beyond those in the prior review; no additional analysis is required.
c) Substantially degrade existing visual character or the quality of the site and its
surroundings? No New Impact. The proposed project includes the consideration
of a modified development plan for the Wallis Ranch project in Eastern Dublin.
Aesthetic impacts would include disturbance of existing vegetation, Landform
modification resulting from grading building pads and roads, and construction
of a mix of housing units where none now exist. The Eastern Dublin EIR
addressed the following potential impacts related to visual and aesthetics
impacts of adopting the Eastern Dublin Specific Plan:
Impact 3.8/B: Urban development of the project site will substantially alter
the existing rural and open space qualities that characterize Eastern Dublin
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The Eastern Dublin EIR identified one measure to mitigate this impact
(Mitigation Measure 3.8/2.0, "Implement the land use plan for the project site
which emphasizes retention of predominant natural features..."). Both the
approved and proposed development plans on the project site would adhere to
this mitigation measure by preserving Tassajara Creek that provides a significant
natural feature on and adjacent to the site. However the Eastern Dublin EIR
concluded that even with adherence to Mitigation Measure 3.8/2, alteration of
rural and open space in Eastern Dublin would remain a potentially significant
impact.
The proposed Stage 2 Development Plan, if approved, would disturb the same
amount of the site as the currently approved plan and has been analyzed in the
2005 SEIR. A large portion of the site, within and adjacent to Tassajara Creek,
would remain undeveloped. No new or more severe impacts have been
identified in this Initial Study and no further analysis is required.
d) Create light or glare? No New Impact. The project site contains minimal light
sources and construction of the proposed project would add additional light
sources in the form of streetlights along exterior and interior roadways as well as
building and security lighting, as noted in the Initial Study for the 2005 SEIR.
City of Dublin development requirements will be imposed as standard
conditions as part of the normal and customary review process to restrict
spillover of unwanted light off of the project site. The amount of light and glare
would be reduced compared to that assumed in the 2005 SEIR. No new or more
significant impacts would result with respect to light and glare than has been
previously analyzed in the previous CEQA documents and no additional
analysis is required.
2. Agricultural and Forestry Resources
Environmental Setting
The Eastern Dublin EIR contains a description of agricultural resources on and around
the project area at the time of EIR certification. Agricultural and grazing uses
historically predominated within the project area and throughout the Eastern Dublin
area. Urban development has commenced pursuant to the adopted EDSP on lands
immediately east of the project site and agricultural uses, including cattle grazing have
ceased on the project site. The Project site is currently fallow.
There are no current Williamson Act Land Conservation Agreements on the property.
The Alameda County Important Farmland Map (2000) designates the project area as
"Grazing Lands," with vegetation found on lands within this classification being
suitable for grazing of livestock.
No forests or major stands of trees exist on the site, although the Tassajara Creek
corridor, located east of the site is heavily wooded.
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Previous CEOA documents
Eastern Dublin EIR. The Eastern Dublin EIR identified several potential impacts related
to agricultural resources. Impact IM 3.1/C stated that discontinuation of agricultural
uses would be an insignificant impact due to on-going urbanization trends in Dublin
and the Tri-Valley area. Impact 3.1/D identified a loss of lands of Farmlands of Local
Importance with approval and implementation of the General Plan and Specific Plan.
This was also noted as an insignificant impact. Impact 3.1/F stated that buildout of
Specific Plan land uses would have a significant and unavoidable impact on cumulative
loss of agricultural and open space lands. Finally, Impact IM 3.1/E noted indirect
impacts related to non-renewal of Williamson Act contracts. This impact was also
identified as less-than-significant impact.
2005 SEIR. Agriculture resources were addressed in Chapter 4.1 of the SEIR. No
additional significant impacts to agricultural resources were identified in this
document.
Project Impacts
a,c) Convert prime farmland to a non-agricultural use or involve other changes which could
result in conversion of farmland to a non-agricultural use? No significant impacts
were identified with respect to agricultural resources in previous CEQA
documents listed above. The project proposes uses consistent with, but at a lesser
intensity and density than assumed in prior reviews. No new conditions have
been identified in this Initial Study with respect to conversion of prime farmland
to a non-agricultural use and no new or more severe impacts would result than
were analyzed in previous CEQA documents for this site. No additional analysis
is required.
Development of the project site would continue to contribute to cumulative loss
of agricultural land and open space, which was identified as a significant and
unavoidable impact in the Eastern Dublin EIR (Impact 3.1/F).
b) Conflict with existing zoning for agricultural use, or a Williamson Act contract? No
New Impact. The City of Dublin has previously zoned much of the project site
for residential uses. No agricultural zoning or Williamson Act contracts presently
exist on the site nor are any agricultural operations on-going. No new or more
severe impacts would result than have been previously analyzed in other CEQA
documents for the site. No additional analysis is required.
d) Result in the loss of forest land or conversion of forest land to a non forest use? No
Impact. No forest land exists on the development portion of the project site and
no impact would result with respect to this topic.
e) Involve other changes which, due to their location or nature, could result of forest land to
a non forest use? No Impact. See item "d," above.
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3. Air Quality
Environmental Setting
The project is within the Livermore-Amador Valley. The Livermore-Amador Valley
forms a small subregional air basin distinct from the larger San Francisco Bay Area Air
Basin. The Livermore-Amador Valley air basin is surrounded on all sides by high hills
or mountains. Significant breaks in the hills surrounding the air basin are Niles Canyon
and the San Ramon Valley, which extends northward into Contra Costa County.
The terrain of the Livermore-Amador Valley influences both the climate and air
pollution potential of the sub-regional air basin. As an inland, protected valley, the area
has generally lighter winds and a higher frequency of calm conditions when compared
to the greater Bay Area.
The occurrence of episodes of high atmospheric stability, known as inversion
conditions, severely limits the ability of the atmosphere to disperse pollutants vertically.
Inversions occur during all seasons in the Bay Area, but are particularly prevalent in the
summer months when they are present about 907o of the time in both morning and
afternoon.
According to the Bay Area Air Quality Management District, air pollution potential is
high in the Livermore Valley, especially for ozone in the summer and fall (BAAQMD,
2005 SEIR, p. 38). High temperatures increase the potential for ozone, and the valley not
only traps locally generated pollutants but also can be the receptor of ozone and ozone
precursors from upwind portions of the greater Bay Area. Transport of pollutants also
occurs between the Livermore Valley and the San Joaquin Valley to the east.
During the winter, the sheltering effect of terrain and its inland location results in
frequent surface-based inversions. Under these conditions, pollutants such as carbon
monoxide from automobiles and particulate matter generated by fireplaces and
agricultural burning can become concentrated.
Previous CEQA documents
Eastern Dublin EIR. The Eastern Dublin EIR contains a number of mitigation measures
to reduce anticipated air quality impacts from the General Plan and EDSP project. These
include:
• Mitigation Measures 3.11/1.0 reduced construction dust deposition impacts but
not to a level of less than significant (Impact 3.11/A). MM 3.11/1.0 requires
development projects to implement dust control measures. Even with these
measures, the impact would remain significant and unavoidable.
• Mitigation Measures 3.11/2.0-4.0 reduced project and cumulative impacts related
to vehicle emission from construction equipment (IM 3.11/B) but not to a less-
than-significant level. These mitigations require emission control from on-site
equipment, completion of a construction impact reduction plan and others. Even
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Initial Study/Wallis Ranch/Trumark Project April 2014
with adherence to these mitigations, this impact would remain significant and
unavoidable.
• Mitigation Measures 3.11/5.0-11.0 reduced mobile source emission from ROG
and NOx (IM 3.11/C) but not to a less-than-significant level. Mitigation
Measures require coordination of growth with transportation plans and other
measures. Many of which are at a policy (not a project) level. Even with
adherence to adopted mitigations, IM 3.11/C would remain significant and
unavoidable.
• Mitigation Measures 3.11/12.0-13.0 reduced project and cumulative impacts
related to stationary source emissions (IM 3.11/E) but not to a less-than-
significant level. The two adopted mitigations require reduction of stationary
source emissions to the extent feasible by use of energy conservation techniques
and recycling of solid waste material. Even with adherence to the two measures,
stationary source emissions would remain significant and unavoidable.
2005 SEIR. This document identified the following significant supplemental impacts
and supplemental air quality mitigation measures.
• Mitigation Measure SM-AQ-1 reduced impacts related to construction emission
from construction activities (Supplemental Impact AQ-1) to a less-than-
significant level. Specific items listed in this measure required contractors to
cover stockpiles of debris, sweep paved access roads and parking areas and
construction staging areas and install sandbags or equivalent to prevent silt
runoff from construction areas.
• Mitigation Measure SM-AQ-2 reduced Supplemental Impact AQ-2 but not to a
less-than-significant level. Supplemental Impact AQ-2 noted that the project
would result in a regional emission increase exceeding BAAQMD thresholds for
emission of ozone precursors. Mitigation Measure SM-AQ-2 required the project
proponent to coordinate with the regional public transit provider to extend
service the site along with transit improvements, the project developer to
provide bike paths and sidewalks, consider a local shuttle service to regional
transit hubs and consider installing a telecommute center. Even with adherence
to all of these features, this impact would remain significant and unavoidable.
• Supplemental Impact AQ-3 noted that project emissions of ozone would exceed
the BAAQMD threshold of significance for this pollutant. Adherence to
Supplemental Mitigation Measure SM-AQ-2 would partially but not fully reduce
this impact to a less-than-significant level and this impact would remain
significant and unavoidable.
The proposed project will be required to adhere to applicable mitigation measures
related to air quality.
Project Impacts
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a) Would the project conflict or obstruct implementation of an air quality plan? No New
Impact. The amount of development proposed on the site would be less than
previously considered and approved by the City of Dublin. Approved uses on the
project site includes up to 935 dwellings with a mix of attached and detached
dwellings. The proposed project would allow development of up to 809 dwellings
on the site, which would be up to 126 fewer dwellings. Therefore, approval and
implementation of the proposed project would represent a substantial dwelling
unit decrease on the site used as the basis of the regional Clean Air Plan. The
proposed project would not conflict with or obstruct the regional Clean Air Plan.
No new or more significant impacts would result than was previously analyzed in
other CEQA documents.
b,c) Would the project violate any air quality standards or result in cumulatively considerable
air pollutants? No New Impact. Air quality impacts of development of the Eastern
Dublin Planning area were analyzed in the 1993 Eastern Dublin EIR. The EIR
found that future development of the Eastern Dublin area, including the proposed
project, would contribute to the cumulative impacts related to dust deposition,
construction equipment emissions, mobile source emissions and stationary source
emissions and would exceed air quality standards. These impact (Impacts
(IM/3.11/A, B, C and E) were was found to be significant and unavoidable when
the Eastern Dublin Specific Plan was approved.
The 2005 Supplemental EIR also found that development if up to 935 dwellings on
the Dublin Ranch West site would result in a significant and unavoidable emission
of ozone
Since the proposed project would contain fewer dwellings anticipated in the
Eastern Dublin EIR and up to 126 fewer dwellings than analyzed in the 2005 SEIR,
there would be no new or more severe impact with respect to violation of air
quality standards than has been previously analyzed in the Eastern Dublin EIR.
No new analysis is required.
d,e) Expose sensitive receptors to significant pollutant concentrations or create objectionable
odors? No New Impact. Impact. Residential uses are considered sensitive receptors,
however, the site is not located adjacent to any freeways that would release
significant air emissions.
The Eastern Dublin EIR identified this impact as a potentially significant
cumulative impact which could not be mitigated to achieve the eight-fold
reduction in stationary source emissions needed to meet the insignificant threshold
and, pursuant to CEQA, the City of Dublin adopted a Statement of Overriding
Consideration for this impact in connection with the Eastern Dublin, 2005, and
2007 project approvals. No new impacts are identified in this Initial Study beyond
those identified in the Eastern Dublin EIR and the 2005 SEIR, and no additional
analysis is required.
Since the proposed project does not include manufacturing or similar uses, no
objectionable odors would be created.
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4. Biological Resources
Environmental Setting
The project area, consisting of the development area and the approximately 23-acre
western open space area, is dominated by non-native grassland with small areas of
developed lands, riparian woodland and other aquatic habitat. A substantial amount of
riparian woodland exists within the Tassajara Creek Management Zone, an adjacent
private open space area that consists mostly of non-native grassland habitat with some
riparian habitat. This area is not proposed for development.
Regulatory framework
California Fish and Wildlife Code Section 1600. Streams, lakes, and riparian vegetation as
habitat for fish and other wildlife species, are subject to jurisdiction by CDFW under
Sections 1600-1616 of the California Fish and Game Code. Any activity that will do one
or more of the following: 1) substantially obstruct or divert the natural flow of a river,
stream, or lake; 2) substantially change or use any material from the bed, channel, or
bank of a river, stream, or lake; or 3) deposit or dispose of debris, waste, or other
material containing crumbled, flaked, or ground pavement where it can pass into a
river, stream, or lake; generally require a 1602 Lake and Streambed Alteration
Agreement. The term "stream," which includes creeks and rivers, is defined in the
California Code of Regulations (CCR) as follows: "a body of water that flows at least
periodically or intermittently through a bed or channel having banks and supports fish
or other aquatic life. This includes watercourses having a surface or subsurface flow
that supports or has supported riparian vegetation" (14 CCR 1.72). In addition, the
term stream can include ephemeral streams, dry washes, watercourses with subsurface
flows, canals, aqueducts, irrigation ditches, and other means of water conveyance if
they support aquatic life, riparian vegetation, or stream-dependent terrestrial wildlife.
Riparian is defined as, "on, or pertaining to, the banks of a stream;" therefore, riparian
vegetation is defined as, "vegetation, which occurs in and/or adjacent to a stream and is
dependent on, and occurs because of, the stream itself." Removal of riparian vegetation
also requires a Section 1602 Lake and Streambed Alteration Agreement from CDFW.
Section 404 of the Clean Water Act. Section 404 of the Clean Water Act gives the U.S.
Environmental Protection Agency (EPA) and the Corps regulatory and permitting
authority regarding discharge of dredged or fill material into "navigable waters of the
United States." Section 502(7) of the Clean Water Act defines navigable waters as
"waters of the United States, including territorial seas." Section 328 of Chapter 33 in the
Code of Federal Regulations defines the term "waters of the United States" as it applies
to the jurisdictional limits of the authority of the Corps under the Clean Water Act. A
summary of this definition of"waters of the U.S." in 33 CFR 328.3 includes (1) waters
used for commerce; (2) interstate waters and wetlands; (3) "other waters" such as
intrastate lakes, rivers, streams, and wetlands; (4) impoundments of waters; (5)
tributaries to the above waters; (6) territorial seas; and (7) wetlands adjacent to waters.
Therefore, for purposes of determining Corps jurisdiction under the Clean Water Act,
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"navigable waters" as defined in the Clean Water Act are the same as "waters of the
U.S." defined in the Code of Federal Regulations above.
The limits of Corps jurisdiction under Section 404 as given in 33 CFR Section 328.4 are
as follows: (a) Territorial seas: three nautical miles in a seaward direction from the
baseline; (b) Tidal waters of the U.S.: high tide line or to the limit of adjacent non-tidal
waters; (c) Non-tidal waters of the U.S.: ordinary high water mark or to the limit of
adjacent wetlands; (d) Wetlands: to the limit of the wetland.
Some areas that meet the technical criteria for wetlands or waters may not be
jurisdictional under the Clean Water Act. Included in this category are some man-
induced wetlands, which are areas that have developed at least some characteristics of
naturally occurring wetlands due to either intentional or incidental human activities.
Examples of man-induced wetlands may include, but are not limited to, irrigated
wetlands, impoundments, or drainage ditches excavated in uplands, dredged material
disposal areas, and depressions within construction areas.
In addition, some isolated wetlands and waters may also be considered outside of
Corps jurisdiction as a result of the Supreme Court's decision in Solid Waste Agency of
Northern Cook County (SWANCC) v. United States Army Corps of Engineers (531 U.S. 159
(2001)). Isolated wetlands and waters are those areas that do not have a surface or
groundwater connection to, and are not adjacent to a "navigable waters of the U.S.",
and do not otherwise exhibit an interstate commerce connection.
Section 401 of the Clean Water Act. Section 401 of the Clean Water Act (33 U.S.C. 1341)
requires any applicant for a federal license or permit to conduct any activity that may
result in a discharge of a pollutant into waters of the United States to obtain a
certification from the state in which the discharge originates or would originate, or, if
appropriate, from the interstate water pollution control agency having jurisdiction over
the affected waters at the point where the discharge originates or would originate, that
the discharge will comply with the applicable effluent limitations and water quality
standards. A certification obtained for the construction of any facility must also pertain
to the subsequent operation of the facility. The responsibility for the protection of water
quality in California rests with the State Water Resources Control Board (SWRCB) and
its rune Regional Water Quality Control Boards (RWQCBs).
Federal and California Endangered Species Acts. The Federal Endangered Species Act
(FESA) of 1973 prohibits federal agencies from authorizing, permitting, or funding any
action that would jeopardize the continued existence of a plant or animal species listed
or a candidate for listing as Threatened or Endangered under the ESA. If a federal
agency is involved with a proposed action or project that may adversely affect a listed
plant or animal, that agency must enter into consultation with the USFWS under
Section 7 (a) (2) of the FESA. Individuals, corporations, and state or local agencies with
proposed actions or projects that do not require authorizing, permitting, or funding
from a federal agency but that may result in the "take" of listed species or candidate
species are required to apply to the USFWS for a Section 10(a) incidental take permit.
The State of California enacted similar laws to the FESA, the California Native Plant
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Protection Act (NPPA) in 1977 and the California Endangered Species Act (CESA) in
1984. The CESA expanded upon the original NPPA and enhanced legal protection for
plants, but the NPPA remains part of the California Fish and Game Code. To align with
the FESA, CESA created the categories of "threatened" and "endangered" species. The
State converted all animal species listed as "rare" under the FESA into the CESA as
threatened species, but did not do so for rare plants. Thus, these laws provide the legal
framework for protection of California-listed rare, threatened, and endangered plant
and animal species. CDFW implements NPPA and CESA, and its Wildlife and Habitat
Data Analysis Branch maintain the CNDDB, a computerized inventory of information
on the general location and status of California's rarest plants, animals, and natural
communities.
East Alameda County Conservation Strategy. The project site is located in the East
Alameda County Conservation Strategy ("Conservation Strategy") Study Area. The
Conservation Strategy is intended to provide an effective framework to protect,
enhance, and restore natural resources in eastern Alameda County, while improving
and streamlining the environmental permitting process for impacts resulting from
infrastructure and development projects. The City of Dublin is a partner in the
Conservation Strategy and uses the document to provide a baseline inventory of
biological resources and conservation priorities during project-level planning and
environmental permitting.
Eastern Dublin Comprehensive Stream Restoration Program. The Eastern Dublin
Comprehensive Stream Restoration Program was adopted by the City of Dublin in 1996
as an implementation program required by the Eastern Dublin General Plan
Amendment and Specific Plan. The purpose of this document is to provide more
detailed requirements relating to hydrologic and biological conditions for individual
development projects proposed adjacent to Tassajara Creek and its tributaries,
specifically to ensure that Tassajara Creek restoration policies and programs contained
in the Eastern Dublin General Plan and Specific Plan are fully implemented.
Previous CEQA documents
Eastern Dublin EIR. The Eastern Dublin EIR contains a number of mitigation measures
to reduce anticipated impacts to biological resources from the General Plan and EDSP
project. These include:
• Mitigation Measures 3.7/1.0-4.0 reduced impacts related to direct habitat loss
(IM 3.7/A) to a less-than-significant level. These mitigations require
minimization of direct habitat loss due to development, preparation of
vegetation management and enhancement plans and development of a grazing
management plan by the City of Dublin.
• Mitigation Measure 3.7/5.0 reduced impacts related to indirect loss of vegetation
removal (IM 3.7/B) to a less-than-significant level. Mitigation Measure 3.7/5.0
requires revegetation of graded or disturbed areas as quickly as possible.
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• Mitigation Measures 3.7/6.0-17.0 reduced impacts related to loss or degradation
of botanically sensitive habitats (IM 3.7/C) to a less-than-significant level. These
measures require a wide range of steps to be taken by future developers to
minimize impacts to sensitive habitat areas, including preserving natural stream
corridors, incorporating natural greenbelts and open space into development
projects, preparation of individual wetland delineations, preparation of
individual erosion and sedimentation plans and similar actions.
• Mitigation Measures 3.7/18.0-19.0 reduced impacts related to the San Joaquin kit
fox (IM 3.7/D) to a less-than-significant level. These measures require
compliance with the specified Kit Fox Protection Plan, consultation with
appropriate regulatory agencies regarding the possibility of kit fox on project
sites and restrictions on use of pesticides and herbicides.
• Mitigation Measures 3.7/20.0-22.0 reduced impacts related to the red-legged
frog, California tiger salamander, western pond turtle and tri-colored blackbird
(IM 3.7/F-I) to a less-than-significant level. These measures require
preconstruction surveys for the species and protection of impacted habitat areas.
• Mitigation Measures 3.7/23.0-24.0 reduced impacts related to destruction of
Golden Eagle nesting sites (IM 3.7/J) to a less-than-significant level. These
measures require preconstruction surveys for this species and protection of
impacted habitat areas.
• Mitigation Measure 3.7/25.0 reduced impacts related to loss of Golden Eagle
foraging habitat (IM 3.7/K) to a less-than-significant level. This measure requires
the identification of a Golden Eagle protection zone within the Eastern Dublin
planning area.
• Mitigation Measure 3.7/26.0 reduced impacts related to Golden Eagle and other
raptor electrocution (IM 3.7/L) to a less-than-significant level. This measure
requires undergrounding of electrical transmission facilities.
• Mitigation Measures 3.7/20.0 and 27.0 reduced impacts related to burrowing owl
and American badger (IM 3.7/M, N) to a less-than-significant level. This
measure mandates preconstruction surveys and a minimum buffer of 300 feet
around burrowing owl nesting sites and American badger breeding sites during
the breeding season.
• Mitigation Measure 3.7/28.0 reduced impacts related to special status
invertebrates (IM 3.7/S) to a less-than-significant level. This measure requires
follow-on special surveys for these species during appropriate times of the year.
The Eastern Dublin EIR also addresses potential impacts and mitigation measures
regarding bald eagle, peregrine falcons, red-legged frog, California tiger salamander,
western pond turtle the prairie falcon, northern harrier, black-shouldered kite, sharp-
shinned hawk, Cooper's hawk, short-eared owl and California horned lizard.
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2005 SEIR. Chapter 4.3 of this SEIR contained a comprehensive update regarding
potential species and identified the following significant biological impacts.
• Supplemental Impact BIO-1 noted an impact to California Tiger Salamander
(CTS) species. Supplemental Mitigation Measures SM-BIO-1 through BIO-7
reduced this impact to a less-than-significant level by requiring preparation of a
CTS Management Plan, installation of a barrier fence, conducting CTS larval
studies, acquiring compensatory CTS estivation habitat area, completion of an
Open Space Management Plan, appointment of a biological resource monitor
during construction and providing biological resource education to construction
staff.
• Supplemental Impact BIO-2 found a significant impact with respect to California
red-legged frogs (CRLF). This impact was reduced to a less-than-significant level
through adherence to Supplemental Mitigation Measures SM-BIO-8 though BIO-
10. These supplemental measures required CRLF avoidance measures during
prior to and during construction, provision of compensatory upland and
dispersal habitat land and limitations on grading activities during the rainy
season.
• Supplemental Impact BIO-3 noted an impact regarding breeding birds.
Adherence to Supplemental Mitigation Measures SM-BIO-5 through 7 and 11
and 12 reduced this impact to a less-than-significant level by limiting tree
removal to appropriate times of the year, establishing buffers around trees with
nests and conducting pre-construction surveys for protected birds prior to
construction.
• Supplemental Impact BIO-4 noted an impact with regard to bat species.
Adherence to Supplemental Mitigation Measures SM-BIO-5 through 7 and 13
reduced this impact to a less-than-significant level by requiring preconstruction
surveys for bat species. If occupied bat nests are found, a qualified biologist shall
implement an exclusion plan to prevent further occupancy.
• Supplemental Impact BIO-5 found an impact with respect to Burrowing Owls.
Adherence to Supplemental Mitigation Measures SM-BIO-5 through 7 and 14
reduced this impact to a less-than-significant level by requiring preconstruction
surveys for owl species, limiting construction periods and creating alternative
burrows away from construction areas. The mitigation requires the project
developer to develop a management plan for enhancement of burrows,
monitoring of burrows, funding assurance and similar measures.
• Supplemental Impact BIO-6 found an impact with loss of special-status plants.
Adherence to Supplemental Mitigation Measures SM-BIO-5 through 7 and 15
reduced this impact to a less-than-significant level by requiring compensatory
habitat for loss of Congdon's tarplant lost to construction and be requiring the
project developer to prepare a detailed mitigation and monitoring plan for this
species.
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• Supplemental Impact BIO-7 noted an impact regarding loss of riparian habitat.
Adherence to Supplemental Mitigation Measures SM-BIO-5 and 6, 16 and 17
reduced this impact to a less-than-significant level by mandating replacement
riparian habitat at a 3:1 ratio and completing a Riparian Habitat Management
Plan to compensate loss of this habitat type. A Tree Removal and Preservation
Plan is also required to protect trees from construction activity and to require
replacement trees for those lost to construction.
• Supplemental Impact BIO-8 found a temporary impact with loss of aquatic
habitat. Adherence to Supplemental Mitigation Measures SM-BIO-6 and 18
reduced this impact to a less-than-significant level by requiring all aquatic
habitat to be replaced to pre-project conditions. A Restoration Plan for Tassajara
Creek was also required that would minimize impacts to aquatic resources
during construction.
The proposed project will be required to adhere to applicable biological resource
mitigation measures contained in the above documents prepared for the site.
Project Impacts
a) Have a substantial adverse impact on a candidate, sensitive, or special-status species? No
New Impact. The Eastern Dublin EIR and 2005 SEIR document the presence of
special-status plant and wildlife species within the general project area and on
the project site. Numerous mitigation measures are included in the Eastern
Dublin EIR and 2005 SEIR to reduce impacts to candidate, sensitive and special-
status species to a less-than significant level. These are listed above and must be
completed prior to start of development. Therefore, no new or more severe
impacts with respect to candidate, sensitive or special-status species would occur
than have been analyzed in the three previous CEQA documents. No additional
analysis is required.
The proposed project would continue to contribute to cumulative loss or
degradation of botanically sensitive habitat, which was identified as a significant
and unavoidable impact (IM 3.7/C) in the Eastern Dublin EIR.
b, c) Have a substantial adverse impact on riparian habitat or federally protected wetlands?
No New Impact. No wetlands and waters of the United States have been
identified on the upland portion of the project site in the 2005 SEIR. This is the
proposed development area. Although wetlands and riparian habitat exist within
and adjacent to Tassajara Creek, this area is protected by a permanent
conservation easement and no development would occur in this location. No
new or more severe impacts would occur than have been previously analyzed
with respect to this topic. No additional is required.
d) Interfere with movement of native fish or wildlife species? No New Impact. Mitigation
measures contained in previous CEQA documents prepared to analyze the
currently approved development project on the site contain mitigation measures
that reduced this impact to a less-than-significant level, including placement of
biological barriers to prevent migration of some species on the site. The proposed
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project would disturb the same amount of the site in the same area as the
currently approved site. The regional native fish and wildlife corridor in the
project area is Tassajara Creek, which forms the eastern boundary of the site.
Tassajara Creek and immediately adjacent land has been included in a
permanent conservation easement to ensure full migration opportunities for
native fish and wildlife. No new or more severe impacts would occur than have
been previously analyzed with respect to potential interference with fish or
wildlife movement. No additional analysis is required.
e, f) Conflict with local policies or ordinances protecting biological resources or any adopted
Habitat Conservation Plans or Natural Community Conservation Plans? No New
Impact. Approval and construction of the proposed project could affect native
oak trees and other trees species on the site. The City of Dublin affords Heritage
Tree status to any oak,bay, cypress, maple, redwood, buckeye, or sycamore tree
with a main trunk of at least twenty-four inches in diameter when measured at
fifty-two inches above the natural grade; trees required for preservation under an
approved development plan, zoning permit, use permit, site development
review, or subdivision map; and trees planted as replacements for unlawfully
removed trees. Permits are required for the removal of any Heritage Tree.
Mitigation Measure SM-BIO-17 contained in the 2005 SEIR requires the project
applicant to prepare a Tree Removal and Preservation. The measure requires the
Plan to be approved by the City prior to issuance of a grading plan.
The project site lies within the Eastern Alameda County Conservation Strategy
(EACCS) planning area. The City of Dublin utilizes the Conservation Strategy as
guidance for environmental permitting for public projects, and private
development projects are encouraged to use the EACCS as a resource as well.
The Conservation Strategy embodies a regional approach to permitting and
mitigation for wildlife habitat impacts associated with land development,
infrastructure, and other activities. The Conservation Strategy is neither a
Habitat Conservation Plan nor a Natural Community Conservation Plan,but is a
document intended to provide guidance during the project planning and
permitting process to ensure that impacts are offset in a biologically effective
manner. There would therefore be no new or significantly more severe impacts
with respect to this topic than previously analyzed in the Eastern Dublin EIR and
2005 SEIR. No additional analysis is required.
5. Cultural Resources
Environmental Setting
The site is generally vacant and contains an existing inhabited residence (in the process
of being vacated), associated outbuildings and one historic school building, the Antone
School. The school building was moved onto the site several years ago. The current
Development Agreement for the property requires the developer to relocate this
structure on the site and restore it. In the event the structure is damaged during
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relocation making it impracticable to restore, the developer shall construct a
replacement building as approved by the Dublin Community Development Director.
The Eastern Dublin EIR did not identify any significant historic structures on the project
site.
The Initial Study for the 2005 SEIR found impacts to cultural resources to be less-than-
significant.
Previous CEOA documents
Eastern Dublin EIR. The Eastern Dublin EIR contains a number of mitigation measures
to reduce anticipated impacts to cultural resources from the General Plan and EDSP
project. These include:
• Mitigation Measures 3.9/1.0-4.0 reduced impacts related to disruption or
destruction of identified prehistoric resources (IM 3.9/A) to a less-than-
significant level. These mitigations mandate a program of mechanical and/or
hand subsurface testing for the presence or absence of midden deposits,
recordation of identified midden sites, collection and/or testing of resources and
development of a site-specific protection program for prehistoric sites.
• Mitigation Measures 3.9/5.0-6.0 reduced impacts related to the disruption or
destruction of unrecorded prehistoric resources (IM 3.9B) to a less-than-
significant level. These measures required that grading or construction activity
be stopped if historic resources were discovered, until the significance of the find
could be ascertained.
• Mitigation Measures 3.9/7.0-12.0 reduced impacts related to disruption or
destruction of identified historic resources to a less-than-significant level (Impact
3.9/Q. These measures would include preparing site-specific archival research
for individual resources, encourage adaptive reuse of historic resources,
recordation of historic sites on local state and federal registers, as appropriate
and development of preservation programs for significant resources.
2005 SEIR. The Initial Study of the 2005 SEIR did not identify any potentially significant
impacts or mitigation measures with respect to cultural resources.
The proposed project will be required to comply with the EDSP EIR cultural resource
mitigation measures.
Project Impacts
a) Cause substantial adverse change to significant historic resources? No New Impact.
Although one historic structure exists on the project site, the Antone School
building, the applicant proposes to rehabilitate this structure re-using materials
from the existing structure to replace the existing fagade and incorporate the
structure into the project. No new or more severe supplemental impacts have
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therefore been identified for the proposed project than were disclosed in
previous CEQA documents.
b, c) Cause a substantial adverse impact or destruction to archeological or paleontological
resources? No New Impact. The Eastern Dublin EIR identifies a remote but
potentially significant possibility that construction activities, including site
grading, trenching and excavation, may uncover significant archeological and/or
paleontological resources on development sites. The Eastern Dublin EIR
categorized these resources.as pre-historic cultural resources. None of these pre-
historic sites were identified by the EIR within near the project site. The Eastern
Dublin EIR assumed that all pre-historic sites would be disturbed or altered in
some manner. This potential impact was identified and addressed in the Eastern
Dublin EIR (Impact 3.9/A) and mitigation measures 3.9/1.0 through 3.9/4.0
(page 3.9-6—3.9-7) that require subsurface testing for archeological resources;
recordation and mapping of such resources; and development of a protection
program for resources which qualify as "significant" under Section 15064.5 of the
CEQA Guidelines. Mitigation Measures 3.9/5.0 and 3.9/6.0, described above,
also were adopted to address the potential disruption of any previously
unidentified pre-historic resources and would apply to the project as may be
appropriate.
The Eastern Dublin Specific Plan also contains policies (Policies 6-24 and 6-25)
requiring research of archaeological resources prior to construction and
determination of the significance and extent of any resources uncovered during
grading and construction.
Therefore, no new or more significant impacts with respect to cultural resources
have been identified that have been previously analyzed in other CEQA
documents for the project area and no additional analysis is required.
d) Disturb any human remains, including those interred outside of a formal cemetery? No
New Impact. Existing cultural resource mitigation measures contained in the
Eastern Dublin EIR reduced impacts to human remains to a less-than-significant
level. No new or more severe impacts with respect to cultural impacts are
anticipated beyond those previously analyzed.
6. Geology and Soils
Environmental Setting
This section is based on a recent site-specific geotechnical report ("Geotechnical
Feasibility Review, Wallis Ranch Residential Development, Alameda County,
California" prepared by Cornerstone Earth Group dated June 12, 2013). This report is
hereby incorporated by reference into this Initial Study and is available for review at the
Dublin Community Development Department during normal business hours.
Geology and soils. The Cornerstone report identified alluvial soils on the lower, eastern
portion of the site near Tassajara Creek and upper Tassajara Formation bedrock on the
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upper hillside portion of the site. Alluvial soils are composed of stiff to very still clays
with high potential for shrink and swell.
Landslide potential. Portions of the site have moderate to steep slopes. Although some of
the hillsides would be re-graded to allow for development, there is a potential for
landslide on the site. This topic has been addressed in the Cornerstone report and
recommendations are included in the report to ensure landsliding potential will not be
significant.
Seismic hazard. The Cornerstone report notes that the site is not within an Earthquake
Fault Zone (formerly Alquist-Priolo Special Studies Zone). Major active faults in the
region that influence earthquake susceptibility include the San Andreas, Hayward,
Calaveras, and Greenville Faults. The site is subject to strong ground shaking in the
event of seismic activity, consistent with all of the Bay area.
Tsunami and seiche hazards. The risk of damage to future improvements on the site from
a tsunami or seiche is low due to the inland location of the site.
Previous CEQA documents
Eastern Dublin EIR. The Eastern Dublin EIR contains a number of mitigation measures
to reduce anticipated impacts related to Soils, Geology and Seismicity from the General
Plan and EDSP project. These include:
• Mitigation Measure 3.6/1.0 reduced impacts related to primary effects of
earthquake ground shaking (IM 3.6/B)but not to a less-than-significant level.
This mitigation measure requires that future structure and infrastructure
facilities be designed to applicable local and state building codes.
• Mitigation Measures 3.6/2.0-7.0 reduced impacts related to the secondary effects
of earthquake ground shaking (IM 3.9/C) to a less-than-significant level.
Mitigation measures mandate building setbacks from landslides, stabilization of
unstable land forms, removal and reconstruction of unstable soils, use of
engineered retaining structures, use of appropriately designed and engineered
fill, and design of structures to account of potential soil failure.
• Mitigation Measures 3.6/9.0-10.0 reduced impacts related to substantial
alteration to landforms to a less-than significant level (IM 3.6/D). Mitigations
require grading plans with minimal cuts and fills and careful siting of homes and
improvements to avoid excessive grading.
• Mitigation Measures 3.6/14.0-16.0 reduced impacts related to expansive soils (IM
3.6/H) to a less-than-significant level. Mitigation measures require formulation
of site-specific designs to overcome expansive soils, reducing the amount of
moisture in the soil and by appropriate foundation and pavement design.
• Mitigation Measures 3.6/17.0-19.0 reduced impacts related to natural slope
stability (IM 3.6/I) to a less-than-significant level. Mitigation measures mandate
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formulation of use of site-specific designs based on follow-on geotechnical
reviews of individual developments, limiting the location of improvements on
downslopes of unstable soils, removal/reconstruction of potentially unstable
slope areas and installation of surface and subsurface slope drainage
improvements.
• Mitigation Measures 3.6/20.0-26.0 reduced impacts related to cut and fill slope
stability (IM 3.6/J) to a less-than-significant level. These measures include
developing grading plans for hillside areas that minimize grading and associate
cuts and fills, ensuring that grading plans comply with appropriate building
codes, utilizing keys and benches as part of grading to ensure slope stability and
minimizing use of unreinforced fill slopes, appropriate compaction of fill areas
and on-going maintenance of slope drainage areas.
• Mitigation Measure 3.6/27.0 reduced the impact related to short-term
construction-related erosion and sedimentation (IM 3.6/K) to a less-than-
significant level. This measure includes limiting timing of construction to avoid
the rainy season and implementing a number of other specific erosion control
measures.
• Mitigation Measure 3.6/28.0 reduced the impact related to long-term erosion and
sedimentation (IM 3.6/L) to a less-than-significant level. This measure includes
installation of erosion control facilities into individual development projects,
including sediment catch basins, creek bank stabilization, revegetation of graded
areas and similar measures.
2005 SEIR. The Initial Study for the 2005 SEIR updated the Eastern Dublin EIR analysis
based on a geologic study specific to the Wallis site. No supplemental impacts or
mitigation measures related to geology or soils were identified in this document.
The proposed project will be required to comply with applicable EDSP EIR soil,
geologic and seismic mitigation measures.
Project Impacts
a) Expose people or structures to potential substantial adverse impacts, including loss,
injury or death related to ground rupture, seismic ground shaking,ground failure, or
landslides? No New Impact. The Eastern Dublin EIR identified that the primary
and secondary effects of ground-shaking (Impacts 3.6/B and 3.6/C) could be
potentially significant impacts. With implementation of Mitigation Measure
3.6/1.0 the primary effects of ground-shaking are reduced but not to a less-than-
significant level by using modern seismic design for resistance to lateral forces in
construction, which would reduce the potential for structure failure, major
structural damage and loss of life. Consistent with the mitigations for Impact
3.6/C, the Cornerstone geotechnical report identifies construction techniques,
such as special footings and use of materials, to ensure that adverse impacts from
ground shaking, landslides, ground failure and other geologic hazards, to be
included in the project design as required by the City of Dublin, to minimize
geological hazard impacts as anticipated in the Eastern Dublin EIR and 2005
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Initial Study/Wallis Ranch/Trumark Project April 2014
SEIR. No new or more severe impacts would result with respect to this topic than
was previously analyzed in earlier CEQA documents. No further analysis is
required.
b) Is the site subject to substantial erosion and/or the loss of topsoil? No New Impact.
Construction of the proposed project improvements on the site would modify the
existing ground surface and alter patterns of surface runoff and infiltration and
could result in a short-term increase in erosion and sedimentation caused by
grading activities (Impact 3.6/K). Long-term impacts could result from
modification of the ground-surface and removal of existing vegetation (Eastern
Dublin EIR Impact 3.6/Q. With implementation of Mitigation Measures 3.6/27.0
and 28.0 contained in the Eastern Dublin EIR and re-stated above, both of these
impacts would be less-than-significant. The project will implement the erosion
controls from the EDEIR as well as the RWQCB measures referenced in the Initial
Study for the 2005 SEIR. Through the Cornerstone report, the project complies
with adopted measures that site-specific erosion and other controls be identified
and implemented.
The Eastern Dublin Specific Plan also contains a policy (Policy 6-43), which
requires that new development be designed to provide effective control of soil
erosion as a result of construction activities. This policy will be applied to the
proposed project.
With adherence to previous mitigation measures, there would be no new or more
severe impacts than have been previously analyzed in other CEQA documents
for this site and no further analysis is required.
c,d) Is the site located on soil that is unstable or expansive or result in potential lateral
spreading, liquefaction, landslide or collapse? No New Impact. Consistent with
Eastern Dublin EIR Mitigation Measure 3.6/7.0 and standard City development
procedures, the project applicant has retained a geologist to prepare a soils and
geotechnical report, as identified above. The report contains methods to
minimize impacts from shrink-swell, lateral spreading and landslide potential
for future improvements on the site. With adherence to Eastern Dublin EIR
mitigation measures, Eastern Dublin Specific Plan policies and the findings of the
Cornerstone geotechnical report, no new or more severe impacts have been
identified related to lateral spreading, liquefaction and other soil hazards than
have been analyzed in previous CEQA documents. No further analysis is
required.
e) Have soils incapable of supporting on-site septic tanks if sewers are not available? No
New Impact. Proposed residences on the site would be connected to sanitary
sewers provided by DSRSD, so there would be no new or more severe impacts
with regard to septic systems.
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7. Greenhouse Gas Emissions
Environmental Setting
Since certification of the Eastern Dublin EIR in 1993 and subsequent CEQA documents,
the issue of contribution of greenhouse gasses to climate change has become a more
prominent issue of concern as evidenced by passage of AB 32 in 2006. On March 18,
2010, amendments to the State CEQA Guidelines took effect which set forth
requirements for the analysis of greenhouse gasses. The topic of the project's
contribution to greenhouse gas emissions and climate change was not analyzed in the
Eastern Dublin EIR or the 2005 SEIR. Since the Eastern Dublin EIR and 2005 SEIR have
been certified, the determination of whether greenhouse gasses and climate change
needs to be analyzed for this proposed project is governed by the law on supplemental
or subsequent EIRs (Public Resources Code section 21166 and Guidelines, Sections
15162 and 15163). Greenhouse gas and climate change is not required to be analyzed
under those standards unless it constitutes "new information of substantial importance,
which was not known and could not have been known at the time the previous EIR was
certified as complete (CEQA Guidelines Sec. 15162 (a) (3).) Greenhouse gas and climate
change impacts is not new information that was not known or could not have been
known at the time the Eastern Dublin EIR and the 2005 SEIR were certified. The issue of
climate change and greenhouse gasses was widely known prior to the certification of
these EIRs. The United Nations Framework Convention on Climate Change was
established in 1992. The regulation of greenhouse gas emissions to reduce climate
change impacts was extensively debated and analyzed throughout the early 1990s. The
studies and analyses of this issue resulted in the adoption of the Kyoto Protocol in 1997.
In the early and mid 2000s, GHGs and climate change were extensively discussed and
analyzed in California. In 2000, SB 1771 established the California Climate Action
Registry for the recordation of greenhouse gas emissions to provide information about
potential environmental impacts. In 2005, the Governor issued Executive Order # S-03-
05 establishing greenhouse gas emission reduction targets in California. AB 32 was
adopted in 2006. Therefore, the impact of greenhouse gases on climate change was
known at the time of the certification of the Eastern Dublin EIR in May 1993 and the
certification of a SEIR in 2005. Under CEQA standards, it is not new information that
requires analysis in a supplemental EIR or negative declaration. No supplemental
envirorunental analysis of the project's impacts on this issue is required under CEQA.
Project Impacts
a,b Generate greenhouse gas emissions, either directly or indirectly, that may have a significant
impact on the environment or conflict with an applicable plan,policy or regulation adopted for the
purpose of reducing the emissions of greenhouse gases? As discussed above, no additional
environmental analysis is required under CEQA Section 21166.
8. Hazards and Hazardous Materials
This section of the Initial Study is based on a Phase I Environmental Site Assessment
prepared by Cornerstone Earth Group. in June 2013 (" Phase I Environmental Site
Assessment, 6582 Tassajara Road, Dublin"). This document is incorporated into this
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Initial Study/Wallis RanchfTrumark Project April 2014
Initial Study by reference and is available for review at the Dublin Community
Development Department during normal business hours.
Environmental Setting
The Phase I analysis prepared by Cornerstone Earth Group did not identify any
recognized environmental conditions on the project site. As is normal and customary
for conversion of a former agricultural area to urban uses, the Cornerstone Phase I
report does recommend preparation of a Site Management Plan that would establish
protocols in the event hazards are encountered during construction.
The project site is located considerably north of Livermore Municipal Airport and is not
within the Airport Influence Area of this facility.
The site is located within and adjacent to a wildland area that is subject to wildland fire
hazard.
Previous CEQA documents
Impacts to hazards and hazardous materials was not addressed in the Eastern Dublin
EIR. The Initial Study for the 2005 SEIR examined the potential for hazardous materials
and wildfire impacts and found them to be less-than-significant.
Project Impacts
a) Create a significant hazard to the public or the environment through the routine transport,
use or disposal of hazardous materials? No New Impact. There would be no impact
with regard to transport, use or disposal of hazardous materials, since the
proposed project involves construction of a residential development on the site.
Proposed land uses on the site would not use, store or transport of significant
quantities of hazardous materials. No new or more severe impacts would therefore
occur on the site than have been previously analyzed and no additional analysis is
required.
b) Create a significant hazard to the public or the environment through reasonably foreseeable
upset and accident conditions involving the release of hazardous materials into the
environment? No New Impact. Based on the discussion in subsection "a," above, no
new impacts are anticipated with respect to the release of hazardous materials
than were analyzed in the 2005 SEIR initial study document and no additional
analysis is required.
e) Emit hazardous materials or handle hazardous materials or acutely hazardous materials,
substances, or waste within one-quarter mile of an existing or proposed school? No
Impact. Although the Quarry Lane private school is located just to the east of the
project site, approval and implementation of the proposed project would have no
impact with regard to this topic, since no hazardous materials or acutely
hazardous materials would be released from the project, since the project would be
a residential development.
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d) Is the site listed as a hazardous materials site? No New Impact. No properties
comprising the project area are listed on the State of California Department of
Toxic Substances Control as an identified hazardous site as of February 6, 2014.
There is therefore no new or more severe impacts impact with respect to this topic
than have been previously analyzed. Approval and implementation of the
proposed project would have no impact with regard to this topic, since no schools
exist or are planned near the project area. No new impact with respect to emission
or handing of hazardous materials within one-quarter of an existing or planned
school will result from the project.
e,f) Is the site located within an airport land use plan of a public airport or private airstrip? No
New Impact. The project site lies significantly north of the Airport Influence Area
(AIA) of Livermore Municipal Airport and is not included in the AIA. No new or
more severe impacts are anticipated with respect to this topic than previously
analyzed and no additional analysis is required.
g) Intel ference with an emergency evacuation plan? No New Impact. The proposed
project would include the construction of a residential project on private land. No
emergency evacuation plan would be affected since no roadways would be
blocked. No new or more severe impacts would result than have been previously
analyzed, in the EDEIR or the Initial Study for the 2005 SEIR, and no additional
analysis is required.
h) Expose people and structures to a significant risk of loss, injury or death involving
wildland fires or where residences are intermixed with wildlands? No New Impact. The
project site is located in a largely rural and undeveloped area of Eastern Dublin.
Properties to the north lie in Contra Costa County and are undeveloped. Land to
the west is undeveloped and is within Parks RFTA. The project is required to
adhere to mitigation measures contained in Eastern Dublin EIR (as discussed in
the Initial Study for the 2005 SEIR) and City's Wildfire Management Plan (updated
in 2002). No new or more severe impacts will result beyond those previously
identified and no additional analysis is required.
9. Hydrology and Water Quality
Environmental Setting
Local surface water. The project site is located within the Tassajara Creek watershed
which drains to the San Francisco Bay via the Arroyo Del Valle and Arroyo de la
Laguna. The main course of Tassajara Creek flows in a north-south direction just east of
the site.
The project area is located within the jurisdiction of Zone 7 of the Alameda County
Flood Control and Water Conservation District (Zone 7). Zone 7 provides maintenance
of regional drainage facilities within this portion of Alameda County.
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Surface water quality.Water quality in California is regulated by the U.S. Environmental
Protection Agency's National Pollution Discharge Elimination System (NPDES), which
controls the discharge of pollutants to water bodies from point and non-point sources.
In the San Francisco Bay area, this program is administered by the San Francisco Bay
Regional Water Quality Control Board (RWQCB). Federal regulations issued in
November 1990 expanded the authority of the RWQCB to include permitting of
stormwater discharges from municipal storm sewer systems, industrial processes, and
construction sites that disturb areas larger than one acre of land area. The City of Dublin
is a co-permittee of the Alameda County Clean Water Program, which is a coordinated
effort by local governments in Alameda County to improve water quality in San
Francisco Bay.
Flooding. The project site lies outside of a 100-year flood hazard area (Flood Insurance
Rate Map, Community Panel No. 060705-0002B).
Previous CEOA documents
Eastern Dublin EIR. The Eastern Dublin EIR contains a number of mitigation measures
to reduce anticipated impacts related to hydrology and storm drainage from the
General Plan and EDSP project. These include:
• Mitigation Measures 3.5/44.0-48 reduced impacts related potential flooding (IM
3.5/Y) to a less-than-significant level. These mitigation measures require new
storm drainage facilities as part of new development, requires developers to
prepare storm drain plans for individual development projects and requires new
flood control facilities to alleviate downstream flooding potential.
• Mitigation Measures 3.5/51.0 and 52.0 reduced impacts related to non-point
source pollution (IM 3.5/AA) to a less-than-significant level. These mitigation
measures mandate that specific water quality investigations be submitted as part
of development projects and that the City should develop community-based
programs to educate residents and businesses to reduce non-point source
pollution.
2005 SEIR. Hydrology and water quality was addressed in the Initial Study for the 2005
SEIR. No potentially significant impacts or mitigation measures related to hydrology
and water quality were included in this document.
The proposed project shall adhere to all of the applicable above previous mitigation
measures.
Project Impacts
a) Violate any water quality standards or waste discharge requirements? No New Impact.
Approval and construction of the proposed development project would add
impervious surfaces to the essentially undeveloped site that would increase the
amount of stormwater runoff and potentially degrade water quality. Mitigation
Measure 3.5/51.0 contained in the EDSP EIR requires each project developer to
prepare and submit a water quality investigation. The City of Dublin also requires
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Initial Study/Wallis Ranch/Trumark Project April 2014
new development proposals to adhere to the most recent surface water quality
standards adopted by the Regional Water Quality Control Board. The Wallis
Ranch developer is proposing to install a large water quality/hydromodification
basin on the east-central portion of the site to filter water runoff prior to outfall
into Tassajara Creek. Other, smaller, bioswales would be installed through the site.
The proposed water quality facilities will ensure that water quality and waste
discharge standards are met. No new or more significant impacts with respect to
water quality violations or wastewater discharges would result than have been
previously analyzed. No additional analysis is required.
b) Substantially deplete groundwater recharge areas or lowering of water table? No New
Impact. No new or more significant impacts are anticipated with regard to
depletion of groundwater resources than have been analyzed in previous CEQA
documents. A portion of the site would remain as open space that would allow
recharge of the underground aquifer. Also, stormwater runoff from the site would
be directed to proposed stormwater basin located on the east-central portion of the
site that would allow recharge into the underground aquifer.
Also, the proposed water source for this project would rely on surface water
supplies from DSRSD and not local groundwater supplies. As noted in the EDEIR
and Initial Study for the 2005 SEIR, the project site is not identified as a
groundwater recharge area in the Eastern Dublin Specific Plan. The project is
required to comply with EDEIR mitigation measures 3.5/49 and 50 to protect
water quality and support Zone 7's groundwater recharge program. No new or
more severe impacts would occur with respect to this topic than has been
previously analyzed in other CEQA documents. No additional analysis is
required.
c) Substantially alter drainage patterns, including streambed courses such that substantial
siltation or erosion would occur? No New Impact. New impervious surfaces would
be added to the project site to accommodate new dwellings, roadways, driveways
and similar surfaces. Existing drainage patterns may be modified based on
proposed development, similar to the existing approved Development Plan.
However adherence to Mitigation Measure 46.0 requirement for a site-specific
storm drainage master plan, as contained in the Eastern Dublin EIR, would ensure
that impacts related to changed drainage patterns are less-than-significant. No new
or more severe impacts would result with respect to changed drainage patterns
than have been previously analyzed. No additional analysis is required.
d) Substantially alter drainage patterns or result in flooding, either on or off the project site?
No New Impact. No impacts or significant changes to drainage patterns are
anticipated as part of the project. Based on the Flood Insurance Rate Map, cited
above, the proposed development area lies outside of a FEMA 100-year flood
hazard area. No new or more significant impacts are anticipated than have been
previously analyzed. No additional analysis is required.
e) Create stormwater runoff that would exceed the capacity of drainage systems or add
substantial amounts of polluted runoff? No New Impact. Adherence to Eastern Dublin
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Initial Study/Wallis Ranch/Trumark Project April 2014
EIR Mitigation Measures 3.5/44.0-48.0 will reduce drainage and pollution impacts
to a less-than-significant level. These mitigation measures require new storm
drainage facilities as part of new development and requires developers to prepare
storm drain plans for individual development projects such as the Wallis Ranch
project. In compliance with these mitigations, the project applicant proposes the
construction of a large water quality and hydromodificaton basin in the southern
portion of the site as well as a number of vegetated swales throughout the site to
filter stormwater. No new or more significant impacts have been identified in this
Initial Study regarding flooding or increases in stormwater runoff than have been
previously analyzed. No additional analysis is required.
f) Substantially degrade water quality? This issue has been addressed above in items
"a" and "e."
g) Place housing within a 100-year flood hazard area as mapped by a Flood Insurance Rate
Map? No New Impact. As noted in the Environmental Setting section, above, the
site lies outside of a 100-year flood hazard zone. No new or more significant
impacts are anticipated than have been previously analyzed.
h, i) Place within a 100-year flood hazard boundary structures that impeded or redirect flood
flow, including dam failures? No New Impact. Refer to item "g," above regarding
flood hazard. The project site lies outside of a dam failure inundation area, as
mapped by the Association of Bay Area Governments
(http://www.abag.ca.gov/cgi-bin/pickdamx.pl).
j) Result in inundation by seiche, tsunami or mudflows? No New Impact. The project site
is located well inland from San Francisco Bay or other major bodies of water to be
impacted by a tsunami or seiche. Consistent with prior mitigations for slope
stability, the Cornerstone geotechnical report addresses landslide and mudflow
potential and includes design and construction methods to minimize impacts from
this hazard. No new or more significant impacts would result than have been
previously analyzed. No additional analysis is required.
10. Land Use and Planning
Environmental Setting
The project site contains a dwelling and unoccupied historic school building.
Surrounding uses include a combination of developed and undeveloped properties
within the Eastern Dublin Planning area. Properties to the east have been or are in the
process of developing for residential uses. The property west of the site is a part of
Parks RFTA and is used for military training purposes. Properties to the north are
within the unincorporated portion of Contra Costa County and contain rural residential
uses. Properties south of the Wallis Ranch are owned by a combination of the East Bay
Regional Park District and Parks RFTA.
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Project Impacts
a) Physically divide an established community? No New Impact. The project site is
located in the northwestern portion of the Eastern Dublin planning area. Uses to
the north and west of the Wallis Ranch are vacant and are likely not to experience
significant development in the future due to the nature of the ownership (Parks
RFTA) or being located in a rural residential portion of Contra Costa County to the
north. No new or more significant impacts have been identified in this Initial
Study than have been previously analyzed. No additional analysis is required.
b) Conflict with any applicable land use plan, policy or regulation? No New Impact. No
amendments have been requested to the General Plan and Eastern Dublin Specific
Plan to change development areas on the site and the number of dwellings would
be somewhat less with the proposed project than has been previously approved
(935 approved v. up to 809 proposed). No changes are proposed to any regulation
regulating environmental protection. No new or more significant impacts are
anticipated with regard to land use regulations than have been previously
analyzed in other CEQA documents prepared for this site. No additional analysis
is required.
c) Conflict with a habitat conservation plan or natural community conservation plan? No
New Impact. The project site lies within the Eastern Alameda County
Conservation Strategy (EACCS) planning area. The City of Dublin utilizes the
Conservation Strategy as guidance for environmental permitting for public
projects, and private development projects are encouraged to use the EACCS as a
resource as well. The Conservation Strategy embodies a regional approach to
permitting and mitigation for wildlife habitat impacts associated with land
development, infrastructure, and other activities. The Conservation Strategy is
neither a Habitat Conservation Plan nor a Natural Community Conservation Plan,
but is a document intended to provide guidance during the project planning and
permitting process to ensure that impacts are offset in a biologically effective
manner. There would therefore be no new or significantly more severe impacts
than previously analyzed in the Eastern Dublin EIR and the 2005 SEIR. No
additional analysis is required.
11. Mineral Resources
Environmental Setting
The project site contains no known mineral resources. This is based on the Eastern
Dublin EIR.
Project Impacts
a, b) Result in the loss of availability of regionally or locally significant mineral resources? No
New Impact. Neither the Eastern Dublin EIR nor the 2005 SEIR indicate that
significant deposits of minerals exist on the project site, so no new or more severe
impacts would occur than have been previously analyzed. No additional analysis
is required.
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12. Noise
Environmental Setting
The City defines "noise" as a sound or series of sounds that are intrusive, irritating,
objectionable and/or disruptive to daily life. Noise is primarily a concern with regard to
noise sensitive land uses such as residences, schools, churches and hospitals. Although
noise is controlled around commercial, industrial and recreation uses, community noise
levels rarely exceed maximum recommended levels for these uses.
Re ug latory Setting
The Noise Element of the General Plan identifies the following primary sources of noise
in Dublin: traffic noise from freeways and major roadways within the community and
noise generated by the BART line adjacent to the I-580 freeway. On the project site,
primary noise sources include vehicle noise from Tassajara Road and distant noise from
operations at Parks RFTA.
The Noise Element identifies the following maximum noise exposure levels by land use
type.
Table 2. City of Dublin Land Use/Noise Compatibility Standards (decibels)
Land Use Normally Conditionally Normally Clearly
Acceptable Acceptable Unacceptable Unacceptable
Residential 60 or less 60-70 70-75 75+
Lodging Facilities 60 or less 61-80 71-80 Over 80
Schools,churches, 60 or less 61-70 71-80 Over 80
nursing homes
Neighborhood 60 or less 61-65 66-70 Over 70
arks
Office/Retail 70 or less 71-75 76-80 Over 80
Industrial 70 or less 71-75 Over 75 J --
Source: Dublin General Plan Noise Element,Table 9-1, 2012
The City of Dublin also enforces an interior noise standard of 45 decibels for residential
dwellings.
Previous CEQA documents
Eastern Dublin EIR. The Eastern Dublin EIR notes that major noise sources within
Eastern Dublin include traffic noise from arterial roadways, helicopter overflights from
Camp Parks RFTA, west of Tassajara Road, noise generated by development of land
uses under the Specific Plan and General Plan and construction noise. No specific
significant future noise sources are identified on the project site.
The Eastern Dublin EIR contains a number of mitigation measures to reduce anticipated
noise impacts from the General Plan and EDSP project. These include:
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Initial Study/Wallis Ranch/Trumark Project April 2014
• Mitigation Measures 3.10/1.0 reduced impacts related to exposure of proposed
housing to future roadway noise (IM 3.10/A) to a less-than-significant level.
This mitigation measure require that all future development projects within a
future CNEL 60 noise contour have an acoustic analysis prepared to ensure that
future dwelling units meet City noise exposure levels.
• Mitigation Measures 3.10/4.0 and 5.0 reduced impacts related to construction
noise (IM 10/E) to a less-than-significant level. These mitigation measures
require developers to submit construction noise management plans and to limit
hours of construction operations.
2005 SEIR. Noise impacts were addressed in the Initial Study for the 2005 SEIR. No
supplemental impacts or mitigations were identified.
The proposed project will be required to comply with applicable noise mitigation
measures identified above.
Project Impacts
a) Would the project expose persons or generation of noise levels in excess of standards
established by the General Plan or other applicable standard? No New Impact.
Development of proposed residential land uses on the project site would increase
noise on the project site and future residences would be subject to traffic noise
from vehicles using Tassajara Road to the east. Consistent with EDEIR mitigation
measure 3.10/1.0, a recommended condition of SDR and subdivision map
approval will be to have an acoustic specialist ensure that project components,
including residences, outdoor living areas and parks, are designed to meet City
noise standards. Likely techniques could include setbacks from the roadway,
enhanced landscaping, enhanced glazing for the residences, among other things.
The project is required to adhere to Eastern Dublin EIR noise mitigation measures,
noise standards in the Eastern Dublin Specific Plan and the City noise ordinance.
No new or more significant noise impacts have been identified than have
previously analyzed. No further analysis is required.
The project would contribute to cumulative noise conditions identified as Impact
3.10/B in the Eastern Dublin EIR, which is exposure of existing residences to
future roadway noise. This impact was found to be significant and unavoidable in
the Eastern Dublin EIR. Also, EDSP EIR Impact 3.10/D, exposure of proposed
residential development to noise from future military training activities at Parks
RFTA, was found to be significant and unavoidable.
b) Exposure of people to excessive groundborne vibration or groundborne noise levels? No
New Impact. Consistent with discussion in the Initial Study for the 2005 SEIR, the
proposed project would not include construction or operational elements that
would result in significant groundborne vibration levels to nearby residents
(source: Jim Templeton, project engineer, 2/10/14). No new impacts would result
with respect to vibration or groundborne vibration than was analyzed in previous
CEQA documents on the project site. No additional analysis is required.
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c) Substantial increases in permanent in ambient noise levels? No New Impact. Increased
levels of permanent noise on the project that would occur based on project
development would be reduced to a less-than significant level through adherence
to applicable mitigation measures contained in the Eastern Dublin EIR and the
Dublin Noise Ordinance. The fewer number of dwellings on the project site (809)
than the approved project (935) would also generate fewer vehicle trips to and
from the site and would also represent a fewer number of mechanical systems on
the site that generate local noise. No new or more significant impacts have been
identified in this Initial Study than have been previously analyzed.
d) Substantial temporary or periodic increase in ambient noise levels in the project vicinity
above levels without the project? No New Impact. Increased levels of short-term
construction noise generated on the project site were addressed in EDEIR Impact
3.10/E and applicable mitigation measures. The project is also subject to the
Dublin Noise Ordinance. These measures require project developers to limit hours
of construction activity and to prepare construction noise management plans. No
new or more significant impacts have been identified in this Initial Study than
have been previously analyzed. No additional analysis is required.
e, f) For a project located within an airport land use plan, would the project expose people to
excessive noise levels? No New Impact.Based on Exhibit 3-2 contained in the
Livermore Municipal Airport Land Use Compatibility Plan (2012), the Wallis
Ranch site lies well north of the noise compatibility zone for this airport. The
project site would therefore not be subjected to substantial aircraft noise from this
airport. As noted in the Eastern Dublin EIR and Initial Study for the 2005 SEIR, the
project site could be subject to overflight noise from Camp Parks. No new or more
significant impacts are anticipated in terms of this topic than was previously
analyzed in previous CEQA documents. No additional analysis is required.
13. Population and Housing
Environmental Setting
The project is generally vacant but contains one inhabited dwelling (in the
process of being vacated) that would be removed to allow construction of the
proposed project. An existing historic building also exists on the site as discussed
in the Cultural Resources section of this Initial Study.
Project Imi2acts
a) Induce substantial population growth in an area, either directly or indirectly? No New
Impact. Approval of the proposed project would not induce substantial additional
population growth in the Eastern Dublin area, since development on the affected
properties has been envisioned in the Eastern Dublin Specific Plan and Dublin
General Plan and was approved for development in site-specific approvals in 2005
and 2007.. Approval of the proposed project would result in fewer dwellings being
constructed than currently approved on the site (935 units currently approved v.
City of Dublin Page 61
Initial Study/Wallis Ranch[Trumark Project April 2014
809 proposed.) No new or more severe impacts than were previously analyzed are
therefore anticipated with respect to this topic. No additional analysis is required.
b,c) Would the project displace substantial numbers of existing housing units or people? No
New Impact. Only one housing unit and associated inhabitants would be
displaced should be project be approved and implemented, although existing
residents are currently relocating from the dwelling. No new or more severe
impacts than were previously analyzed are therefore anticipated with respect
housing displacement as several residences were occupied at the time of the 2005
SEIR. No additional analysis is required.
14. Public Services
Environmental Setting
The following provide essential services to the community:
• Fire Protection. Fire protection services are provided by the Alameda County
Fire Department. The Department provides fire suppression, emergency
medical response, fire prevention, education, building inspection services and
hazardous material control. The nearest station is Station 18 at 4800 Fallon
Road.
• Police Protection: Police and security protection is provided by the Alameda
County Sheriff under contact to the City of Dublin.
• Schools. The Dublin Unified School District provides K-12 educational
services for properties on the project site.
• Library Services: Alameda County Library service.
• Maintenance. Maintenance of streets, roads and other governmental facilities
are the responsibility of the City of Dublin.
Previous CE QA documents
Eastern Dublin EIR. Applicable mitigation measures contained in Eastern Dublin EIR
addressing fire and police protection include:
• Mitigation Measure 3.4/7.0: Establish appropriate funding mechanisms to
cover up-front costs of capital fire improvements.
• Mitigation Measure 3.4/9.0: Incorporate Fire Department recommendations
on project design relating to access, water pressure, fire safety and prevention
into the requirements of development approval.
City of Dublin Page 62
Initial Study/Wallis Ranch/Trumark Project April 2014
• Mitigation Measure 3.4/10.0: Ensure, as a requirement of project approval,
that an assessment district, homeowners association or other mechanism is in
place that will provide regular long-term maintenance of the urban/open
space interface.
• Mitigation Measure 3.4/12.0: The City shall work with the Fire Department
and qualified biologists to prepare a wildfire management plan for the project
area.
• Mitigation Measure 3.4/1.0: Provide additional personnel and facilities and
revise beats as necessary in order to establish and maintain City standards for
police protection service in Eastern Dublin.
• Mitigation Measure 3.4/3.0-5.0: Incorporate into the requirements of project
approval Police Department recommendations on project design that affect
traffic safety and crime prevention.
2005 SEIR. The Initial Study for the 2005 SEIR analyzed public service impacts and
found no new or more severe impacts beyond those identified in the EDEIR
The project will be required to comply with the above mitigation measures.
Protect Impacts
a) Fire protection? No New Impact. Approval and implementation of the proposed
project would increase the number of fire and emergency medical calls for service
that would need to be responded to by the Alameda County Fire Department, the
City of Dublin's contract fire department, as a result of a greater number of
dwellings on the project site compared to existing conditions. The proposed
project is required to adhere to previously adopted mitigation measures, including
payment of public facility impact fees to assist in funding new fire stations
(Eastern Dublin EIR Mitigation Measure 3.4/7.0) . Consistent with Eastern Dublin
EIR Mitigation Measure 3.4/9.0, proposed development on the project site will be
conditioned to meet Fire Department requirements including but not limited to
maintaining minimum water pressure and fire flow, providing adequate site
access, using fire retardant building materials and similar features. Proposed
development on the site will also be conditioned to be consistent with the City's
adopted Wildfire Management Plan (Eastern Dublin EIR Mitigation Measure
3.4/12.0).
Based on discussions with Alameda County Fire Department staff, there would be
no new or substantially more severe significant impacts with respect to fire service
beyond that analyzed in previous CEQA documents (source: Bonnie Terra,
Alameda County Fire Department, 2/7/14) and no new or expanded fire stations
would be needed to provide fire and emergency service for the proposed project.
No additional analysis is required.
b) Police protection? No New Impact. Similar to fire protection, there would be no new
impact with regard to police protection,based on mitigation measures included in
the Eastern Dublin EIR. These Mitigation Measures include paying City of Dublin
City of Dublin Page 63
Initial Study/Wallis Ranch/Trumark Project April 2014
public facility impact fees to assist in funding new police facilities (EDSP EIR
Mitigation Measure 3.4/1.0), incorporating Police Department safety and security
requirements into the proposed project, including but not limited to adequate
locking devices, security lighting and ensuring adequate surveillance for
structures and parking areas (EDSP EIR Mitigation Measures 3.4/3.0-5.0).
Based on discussions with Dublin Police Services Department staff, there would be
no new or substantially more severe impacts with respect to police service
associated with the proposed project beyond that analyzed in previous CEQA
documents (source: Captain Tom McCarthy,Dublin Police Services, 2/7/14). No
additional analysis is required.
c) Schools? No New Impact. No new impacts to school service are anticipated should
the proposed project be approved since payment of mandated statutory impact
fees at the time of issuance of building permits will provide mitigation of
educational impacts of the proposed project pursuant to CEQA. The currently
proposed project would result in fewer school-aged children to be accommodated
in DUSD school facilities than estimated in Chapter 4.8 of the 2005 SEIR. There
would be no new or substantially more severe significant impacts with respect to
this impact than has been previously analyzed in previous CEQA documents. No
additional analysis is required.
d) Other governmental service, including maintenance of public facilities? No New Impact.
Maintenance of public facilities would continue to be provided by the City of
Dublin with no new impacts in regard to this topic. New public facilities will be
required to be designed to meet City of Dublin standards. There would therefore
be no new or substantially more severe significant impacts with respect to this
impact than has been previously analyzed in previous CEQA documents. No
additional analysis is required.
15. Recreation
Environmental Setting
No neighborhood or community parks and/or recreation services or facilities exist on
the project site. However, a 7.66-acre neighborhood park site is proposed as a
development require of the project and is shown on current development plans.
The City of Dublin maintains a wide range of park facilities throughout the community.
Regional park facilities are provided by the East Bay Regional Park District, which
maintains a large number of regional parks, trails and similar recreation facilities in
Alameda and Contra Costa County.
The City of Dublin has planned a regional recreational trail along Tassajara Road in
front of the proposed project. The portion of the trail adjacent to the project site would
be constructed by the project developer.
City of Dublin Page 64
Initial Study/Wallis Ranch/Trumark Project April 2014
Previous CEQA documents
Eastern Dublin EIR. Applicable mitigation measures contained in Eastern Dublin EIR
addressing fire and police protection include:
• Mitigation Measure 3.4/29.0: Ensure, as a part of the approval process, that
each new development provide its fair share of planned open space,
parklands and trail corridors.
• Mitigation Measure 3.4/31.0: Calculate and assess in-lieu park fees based on
the City's parkland dedication ordinance. Credit towards parkland
dedication requirements will only be given for level or gently sloping areas
suitable for active recreation use.
• Mitigation Measure 3.4/36.0: Require developer to dedicate public access
easements along ridgetops and stream corridors to accommodate the
development of trails and staging areas.
2005 SEIR. This document included supplemental mitigation measure PARK-1 that
required the project developer to either provide an additional 1.04 net acre of
Neighborhood Park area or provide a minimum of 1.9 net acres of Neighborhood Park
area in close proximity to the project site.
The current project will be required to comply with applicable mitigation measures
identified above.
Project Impacts
a) Would the project increase the use of existing neighborhood or regional parks? No New
Impact. Approval and construction of the proposed project would increase the use
of nearby City or regional recreational facilities, since it would include increasing
the on-site permanent population on the site, but to a lesser extent than analyzed in
previous CEQA documents. The applicant proposes to dedicate a public park site
to the City of Dublin and provide one private park on the site consistent with the
2005 SEIR Mitigation Measure. There would therefore be no new or more severe
impacts with respect to recreation than were previously analyzed.
b) Does the project include recreational facilities or require the construction of recreational
facilities? See item "a," above.
16. Transportation/Traffic
Environmental Setting
Roadways and freeways. The project area is served by Tassajara Road, an arterial road that
provides access from southern Contra Costa County to the I-580 freeway and southerly
into Alameda County south of the I-580 freeway.
City of Dublin Page 65
Initial Study/Wallis Ranch/Trumark Project April 2014
Existing transit service. Transit service to the project site is provided by
The Livermore/Amador Valley Transit Authority (LAVTA) provides bus service in
Dublin and throughout the Tri-Valley. The Bay Area Rapid Transit District (BART)
provides regional rapid transit service with the nearest station located at the Dublin
Transit Center, located on the south side of Dublin Boulevard just west of Arnold Road.
Existing Bicycle and Pedestrian Facilities. There are no marked pedestrian facilities
adjacent to the proposed project site along Tassajara Road. However, there is a striped
and paved shoulder for bicycles on either side of Tassajara Road adjacent to the project
site. Within the study area, there are numerous bicycle and pedestrian facilities
providing access throughout the City of Dublin
Previous CEQA documents
Eastern Dublin EIR. The Eastern Dublin EIR contains a number of mitigation measures
to reduce anticipated traffic impacts from the General Plan and EDSP project. These
measures generally include construction of new roadways, widening of existing
roadways and improvements to local freeway facilities to accommodate anticipated
increases in the number of vehicles associated with the build out of the Eastern Dublin
area.
With the exceptions noted below, the EIR found that all traffic and transportation
impacts could be reduced to less-than-significant levels with adherence to mitigation
measures identified in the EIR. A number of impacts could not be reduced to a level of
insignificance even with mitigations. These include: impacts to the 1-580 freeway
between I-680 and Hacienda Drive (IM 3.3/B), impacts to the I-580 Freeway between
Tassajara Road and Airway Boulevard (IM 3.3/C), cumulative freeway impacts (IM
3.3/E) impacts to Santa Rita Road and T-580 Eastbound ramps (IM 3.3/1), and
cumulative impacts to Tassajara Road (IM 3.3/N).
2005 SEIR. This CEQA document identified the following significant supplemental
impacts and mitigation measures:
• Supplemental Mitigation Measure TRA-1 reduced the impact of additional traffic
along Tassajara Road segments near the project site to a less-than-significant
level by requiring the developer to widen Tassajara Road to four travel lanes
between North Dublin Ranch Drive to the northern project access road.
• Supplemental Mitigation Measure TRA-2 reduced the impact of potential traffic
safety impacts to a less-than-significant level by requiring installation of traffic
signals at the two project entrances, provide an east-bound right-turn lane,
provide northbound left-turn capacity from Tassajara Road onto project access
drives, provide a northbound left-turn lane from Tassajara Road onto the
southern access drive and provide a southbound right-turn pocket with a taper
on Tassajara Road at both access roadways..
The proposed project will be required to comply with all of the above transportation
and circulation mitigation measures.
City of Dublin Page 66
Initial Study/Wallis RanchlTrumark Project April 2014
Project Impacts
a,b) Conflict with applicable plans related to the effectiveness of the circulation system,
including all modes of travel, including intersections, streets, highways and other
components or conflict with an applicable congestion management program, including
level of service standards, travel demand measures and other applicable standards? The
Eastern Dublin EIR considered the development of the project site with residential
land uses and adopted mitigation measures to address the impacts thereof.
Additional analysis of increased traffic and circulation impacts occurred in as part
of the 2005 SEIR. As noted above, even though the City of Dublin ultimately
approved development of up to 935 dwellings on the Dublin Ranch West site, the
2005 SEIR analyzed up to 1,034 dwellings on the property. Table 3, below,
compares daily, AM peak and PM peak trips on the site from the 2005 SEIR and
the currently proposed development program. Documentation of this is found in
Attachment 1 of this Initial Study. This document is hereby incorporated by
reference into this Initial Study.
Table 3. Trip Generation Comparison
Land Use(ITE Code) Size Daily A.M.Peak Hour P.M.Peak Hour
(d.u.)
Rate Total Rate In Out Total Rate In Out Total
2005 SEIR Project' 1,034 - 8,713 - 152 527 679 - 580 309 889
Single-Family
Detached 624 9.07 5,660 0.72 112 335 447 0.87 344 202 546
Housing(210)
Proposed
Wallis Low-Rise
Ranch Residential 185 5.94* 1,099 0.61 28 85 113 0.78 84 60 144
Condominium/T
ownhouse(23 1)
Total 809 1 15.01 1 6,759 1.33 1 140 420 1 560 1.65 428 262 1 690
Difference -225 - -1954 - -12 -107 1 -119 -152 -47 1 -199
Notes:
d.u.=Dwelling Units
'From Supplemental EIR for Dublin Ranch West Development, 2005
2Proposed Wallis Ranch minus 2005 EIR Project
'Daily Rate is for Residential Condominium/Townhouse(230); ITE lacks daily rate for Low-Rise Residential
Condo/Townhouse(231)
For Single-Family Detached Housing (210): Daily Trips= Ln(T)=0.92Ln(X) +2.72;AM Trips=T=0.70(X) +9.74;
PM Trips= Ln (T)=0.90Ln(X) +0.51;where X=Number of Dwelling units and T=Average Vehicle Trip Ends.
For Low-Rise Residential Condominium[Townhouse(231): Daily Trips=Ln(T)=0.87Ln(X)+2.46;A.M.Trips=T=
0.88(X)—49.70;
P.M. Trips=No. of Dwelling Units x Average Rate(0.78), where X=Number of Dwelling units and T=Average
Vehicle Trip Ends.
Source of trip rates for Proposed Wallis Ranch: ITE Trip Generation, 91 h Edition, 2012
City of Dublin Page 67
Initial Study/Wallis Ranch/Trumark Project April 2014
Based on the above table, the proposed Wallis Ranch project would generate an
estimated 107 fewer A.M. peak hour trips, 199 fewer P.M. peak hour trips and
1,954 fewer daily trips than the amount of development analyzed in the 2005 SEIR.
However, if approved and constructed, the project would continue to contribute to
significant and unavoidable cumulative project impacts as part of the larger
Eastern Dublin project. The Eastern Dublin EIR identified such impacts on the
following roads and transportation facilities:
• I-580 freeway between 1-680 and Hacienda Drive;
• The Santa Rita Road/I-580 eastbound ramps;
• The Dublin Boulevard/Hacienda Drive and Dublin Boulevard/Tassajara
Road intersection
• Other impacts to Tassajara Road, as identified in the EIR.
No new or more severe impacts would result with respect to this topic than was
previously analyzed in other CEQA documents. No additional analysis is
required.
c) Change in air traffic patterns? No New Impact. The proposed project includes
residential uses and would have no impact on air traffic patterns. No new or more
severe impacts would result with respect to this topic than was previously
analyzed in other CEQA documents. No additional analysis is required.
d) Substantially increase hazards due to a design feature or incompatible use? No New
Impact. Approval of the proposed project would add new driveways, sidewalks
and other vehicular and pedestrian travel ways where none currently exist. The
current development proposal will be required to comply with current City
engineering design standards, appropriate supplemental mitigation measures
from the 2005 SEIR dealing with traffic safety and other safety standards to ensure
that no safety hazards would be created or exacerbated. No new or more severe
impacts with respect to design hazards would be created than previously
analyzed. No additional analysis is required.
e) Result in inadequate emergency access? No New Impact. Two access drives are
already constructed into the project site from Tassajara Road. No new or more
severe impacts would result with respect to this topic. No additional analysis is
required.
f) Conflict with adopted policies, plans or programs regarding public transit, pedestrian
facilities or otherwise decrease the performance or safety of such facilities? No New
Impact. No conflicts to plans, policies or programs that promote public transit,
pedestrian use or similar features were identified in previous CEQA reviews for
the subject property. No new or more impacts have been identified in this Initial
City of Dublin Page 68
Initial Study/Wallis Ranch/Trumark Project April 2014
Study that has been previously analyzed in other CEQA documents for the project
site. No additional analysis is required.
17. Utilities and Service Systems
Environmental Setting
The project area is served by the following service providers:
• Water supply and distribution: Dublin San Ramon Services District (DSRSD).
• Sewage collection and treatment; recycled water: DSRSD.
• Storm drainage: City of Dublin and Zone 7.
• Solid waste service: Amador Valley Industries
• Electrical and natural gas power: Pacific Gas and Electric Co.
• Communications: AT &T
Previous CEQA documents
Eastern Dtitblin EIR. In terms of water resources, the Eastern Dublin EIR identified
overdraft of groundwater resources (Impact 3.5/P) as a potentially significant impact
Adherence to Mitigation Measures 3.5/24.0 and 25.0 would reduce this impact to a level
of insignificant. These measures require the City of Dublin to coordinate with DSRSD to
develop recycled water resources and otherwise carefully use water resources and that
all new development in the Eastern Dublin project area to connect to the DSRSD water
system. Impact 3.5/Q identified an increase in water demand as a potentially significant
impact, but this impact could be mitigated to an insignificant level based on
implementation of Mitigation Measures 3.5/26.0-31.0. These mitigation measures
require implementation of water conservation measures in individual development
projects and construction of new system-wide water improvements which are funded
by development impact fees. Another related impact identified in the Eastern Dublin
EIR is the need for additional water treatment plant capacity (Impact 3.5/R). This
impact was identified as being reduced to a level of insignificance through the
implementation of Mitigation Measures 3.5/32.0-31.0, which requires improvement to
the Zone 7 water system, to be funded by individual development impact fees.
Impact 3.5/S (lack of a water distribution system) was identified as a potentially
significant impact in the Eastern Dublin EIR, but this impact has been reduced to an
insignificant level through adherence to Mitigation Measures3.5/4.34.0-38.0. These
mitigations require upgrades to the project area water system and provision of a "will
serve" letter prior to issuance of a grading permit. Impact 3.5/T identified a potentially
significant impact related to inducement of substantial growth and concentration of
population in the project area. The Eastern Dublin found that this was a significant and
unavoidable impact.
City of Dublin Page 69
Initial Study/Wallis Ranch/Trumark Project April 2014
Regarding sewer service, the Eastern Dublin EIR identified Impact 3.5/B (lack of a
wastewater collection system) as a potentially significant impact that could be mitigated
through adherence to Mitigation Measures 3.5/1.0-5.0. These measures require DSRSD
to prepare an area-wide wastewater collection system master plan, requires all new
development to be connected to DSRSD's public sewer system, discourages on-site
wastewater treatment, requires a "will-serve" letter from DSRSD and requires that all
sewer facilities be constructed to DSRSD engineering standards. Impact 3.5 noted an
impact with regard to extension of a sewer trunk line with capacity to serve new
development, but could be reduced to an insignificant level since the proposed Eastern
Dublin Specific Plan sewer system has been sized to accommodate increased sewer
demand from the proposed Specific Plan project. Impact 3.5/G found that lack of
wastewater disposal capacity as a significant impact. An upgraded wastewater disposal
facility has been constructed by the Livermore Amador Valley Water Management
Agency and is operational. Impact 3.5/E identified lack of wastewater treatment plant
capacity as a potentially significant impact, which could be reduced to an insignificant
level through adherence to Mitigation Measure.
2005 SEIR. Utilities and services were addressed in Chapter 4.7 of the 2005 SEIR. No
supplemental mitigation measures were included in this CEQA document.
The project developer shall be required to adhere to the applicable Eastern Dublin EIR
mitigation measures.
Project Impacts
a) Exceed wastewater treatment requirements of the RWQCB? No New Impact. The
current project would contain the same type of development as analyzed in the
2005 SEIR and, based on recent discussions with DSRSD staff (noted below)
regarding this project, the proposed project would not exceed wastewater
requirements of the Regional Water Quality Control Board (RWQCB). No new or
more significant impacts with respect to wastewater treatment requirements have
been identified in this Initial Study than have been analyzed in previous EIRs.
b) Require new water or wastewater treatment facilities or expansion of existing facilities?
No New Impact. Water, recycled water and wastewater extensions to existing
mains in Tassajara Road would need to be constructed to serve the amount of
development proposed in the Wallis Ranch development application. According to
a representative of DSRSD, District wastewater collection, treatment and disposal
facilities from the construction of the proposed project would not result in a new
or more significant impact than was analyzed in previous CEQA documents
(source: Stan Kolozdie, DSRSD, 2/18/14). No additional analysis is required.
The Wallis Ranch project would also contribute to cumulative impacts related to
consumption of non-renewable natural resources (Impact 3.4/S, increase in energy
use though increased wastewater treatment and disposal and though the operation
of the water system (Impact 3.5/F, H, and U), and inducement of substantial
growth and concentration of population (Impact 3.5/T). All of these impacts were
City of Dublin Page 70
Initial Study/Wallis RanchrFrumark Project April 2014
identified as significant and unavoidable in the Eastern Dublin EIR and were
overridden by the City Council.
c) Require new storm drainage facilities? No New Impact. The proposed development
project would require new and or upgraded drainage facilities to support
proposed development. Consistent with Eastern Dublin EIR Mitigation Measures,
the project developer will be required to install new or upgraded on and off-site (if
required) storm drain systems that comply with City of Dublin and Zone 7
standards. The current project would include on-site storm pipes and a large water
quality pond to ensure consistency with the City-approved stormwater
management plan prepared for this project. No new or more significant impacts
are anticipated with respect to storm drain facilities that have been analyzed in
previous CEQA documents. No additional analysis is required.
d) Are sufficient water supplies available? No New Impact. Based on the information
provided by DSRSD staff, the District has planned for future urban uses on this
site (source: Stan Kolozdie, DSRSD, 2/18/14). However, DSRSD staff also note
that due to the current water emergency resulting from the drought, DSRSD will
limit use of water for construction purposes. No new or more significant impacts
are anticipated with respect to water supplies than have been previously analyzed.
No additional analysis is required.
e) Adequate wastewater capacity to serve the proposed project? See response to "a," above.
e, f) Solid waste disposal? No New Impact. The project site is within the franchise area of
Amador Valley Industries that provides residential and commercial solid waste
pick-up and recycling services. According to representatives of the company, no
solid waste service is currently provided to the area, since it is undeveloped. The
topic of solid waste disposal was not identified as a potentially significant impact
in previous CEQA documents and no new or more significant impacts have been
identified in this Initial Study than have been previously analyzed. No additional
analysis is required.
g) Comply with federal, state and local statutes and regulations related to solid waste? No
New Impact. The existing service provider will ensure adherence to federal, state
and local solid waste regulations. No new or more severe impacts are anticipated
impacts than have been previously analyzed. No additional analysis is required.
18. Mandatory Findings of Significance
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 of 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? No. .
Potential impacts related to biological resources, including a reduction in habitat
area of fish or wildlife species, elimination of a plant or animal community, or
City of Dublin Page 71
Initial Study/Wallis Ranch/Trumark Project April 2014
elimination of an important example of major periods of California history or
prehistory was analyzed in the Eastern Dublin EIR and supplemented in the 2005
SEIR. The proposed project would represent less development intensity than
previously analyzed in earlier CEQA documents and would implement previously
adopted mitigation measures.
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). No.
Cumulative impacts of the proposed Sub Area 3 project have been fully analyzed
in the Eastern Dublin EIR and the 2005 SEIR.
c) Does the project have environmental effects which will cause substantial adverse effects on
human beings, either directly or indirectly? No. No such impacts have been
discovered in the course of preparing this Initial Study.
Initial Study Preparers
Jerry Haag, Urban Planner, project manager
Agencies and Organizations Consulted
The following agencies and organizations were contacted in the course of this Initial
Study:
City of Dublin
Luke Sims, AICP, Community Development Director
Jeff Baker, Assistant Community Development Director
Michael Porto, Project Manager
Andy Russell PE, City Engineer
Obaid Khan, City Transportation Engineer
Bonnie Terra, Alameda County Fire Department
Darrell Jones, Alameda County Fire Department
Chief Tom McCarthy, Dublin Police Services
Kathleen Faubion, AICP, Assistant City Attorney
California Department of Toxic Substances Control (DTSQ
Website
DSRSD
Stan Kolozdie
Applicant Representatives
Christopher Davenport, Trumark Homes
City of Dublin Page 72
Initial Study/Wallis Ranch[frumark Project April 2014
References
Dublin General Plan, City of Dublin, Updated through 7/2/11
Eastern Dublin General Plan, Wallace Roberts &Todd, 1993
Eastern Dublin Specific Plan and General Plan Environmental Impact Report,
Wallace Roberts & Todd, 1994
Eastern Dublin Comprehensive Stream Restoration Program, Sycamore
Associates, 1996
Eastern Dublin Scenic Corridor Policies and Standards, David Gates &
Associates, 1996
Livermore Municipal Airport, Airport Land Use Compatibility Plan, ESA
Associates, August 2012
Parks and Recreation Master Plan, City of Dublin, 2006 update
All resolutions and ordinances referenced in the Initial Study are incorporated
herein by reference and available for review at City Hall during normal business
hours.
City of Dublin Page 73
Initial Study/Wallis Ranch/Trumark Project April 2014
Attachment 1
Trip Generation Analysis
City of Dublin Page 74
Initial Study/Wallis RanchfTrumark Project April 2014
L"I,
4 Vision That Mw"Your CotnmuKq
Transportation
Consultants February 28, 2014
Mr.Jerry Haag
2029 University Avenue
Berkeley, CA 94704
Re: Wallis Ranch/Trumark Development in the City of Dublin
Dear Mr. Haag:
TJKM Transportation Consultants has prepared this letter report comparing trip generation for
the 184-acre Wallis Ranch development site for the currently proposed mix of 809 dwelling units
(d.u.)versus the project trip generation estimate for 1,034 d.u, presented in the certified 2005
Supplemental EIR for Dublin Ranch West Development(2005 SEIR). The project site is located west
of Tassajara Road and south of the Alameda/Contra Costa County line. The purpose of this trip
generation comparison is to assess whether the currently proposed 809-unit mix at the Wallis
Ranch site has the potential to generate additional traffic impacts not identified in the 2005 SEIR.
Results
As Table I indicates,the project analyzed in the 2005 SEIR for the Wallis Ranch site was estimated
to generate 8,713 weekday daily trips, 679 a.m. peak hour trips, and 889 p.m. peak hour trips.
Comparatively, using trip rates in Trip Generation, 91h Edition published by ITE (2012), the currently
proposed Wallis Ranch project is expected to generate 6,759 weekday daily trips, 560 trips during
the a.m. peak hour, and 690 trips during the p.m. peak hour, which represents fewer daily and
peak hour trips than the project the SEIR analyzed.
Table I:Trip Generation Comparison
Size Daily A.M.Peak Hour P.M.Peak Hour
Land Use(ITE Code) (d.u.)
Pleasanton 1 Rate Total Rate In Out Total Rate In Out Total
4305 Hacienda Drive II
Suite 550 2005 SEIR Project' 1,034 8,713 152 527 679 580 309 889
Pleasanton,CA
94588.8526
925.463.061 I Single-Family
925.463.3690 fax Detached 624 9.07 5,660 0.72 112 335 447 0.87 344 202 546
Fresno Housing(2 10)
516 W.Shaw Avenue
Site 200 Proposed Low-Rise
Fresno,CA Wallis Residential
93704.2515 Ranch Condominium/ 185 5.94* 1.099 H13 28 85 113 0.78 84 60 144
559.325.7530
559.22IA940 fax Townhouse
(231)
Sacramento I -
980 Ninth Street Total 809 15.01 6,759 140 420 560 1.65 428 262 690
16-Floor
Sacramento,CA Difference2 225 -1954 - -12 -107 -119 - 152 47 -199
95814-2736
916.449.9095 Notes:
d.u.=Dwelling Units
Santa Rosa 'From Supplemental EIR for Dublin Ranch West Development,2005
1400 N.Dutton Avenue 2Proposed Wallis Ranch minus 2005 EIR Project
Suite 21 *Daily Rate is for Residential Condominium/Townhouse(230);ITE lacks daily rate for Low-Rise Residendal Condo/Townhouse(23 1)
Santa Rosa,CA
95401-4643 For Single-Family Detached Housing(210):Daily Trips=Ln(T)=0.92Ln(X)+2.72;AM Trips=T=0.70(X)+9.74;
707.575.5800 PM Trips=Ln(T)=0.90Ln(X)+0.51;where X=Number of Dwelling units and T=Average Vehicle Trip Ends.
707.575.5888 fax For Low-Rise Residential Condominium/Townhouse(231):Daily Trips=Ln(T)=0.87Ln(X)+2.46;A.M.Trips=T=0.88(X)—49.70:
P.M.Trips=No.of Dwelling Units*Average Rate(0.78),where X=Number of Dwelling units and T=Average Vehicle Trip Ends.
tlkm@vt1km.com Source of trip rates for Proposed Wallis Ranch:ITE Trip Generation,91 Edition,2012
www.tikm.com
Mr.Jerry Haag
i jKM February 28, 2014
T r;nsr,c=t;,rc=n Page 2
Conclusion
Based on the decrease in trip generation for the currently proposed Wallis Ranch development
compared with the project analyzed in the 2005 SEIR, and the fact that the land use remains
residential and the expected directional distribution of project trips would not change, the project-
added traffic at intersections and roadway segments would be less than the 2005 SEIR analysis. As
a result, TJKM concludes that no supplemental traffic impacts would result with the revised
project.
Very truly yours,
Richard K. Haygood, P.E.
Director,Traffic& Multimodal Studies
cc: Shruti Shrivastava, TJKM