HomeMy WebLinkAboutMINUTES - 09252012 - SD.4RECOMMENDATION(S):
CONSIDER accepting the report on implementation of the East Contra Costa County Habitat Conservation
Plan/Natural Community Conservation Plan (HCP/NCCP) and issuance by the U.S. Army Corps of Engineers of a
Regional General Permit related to the HCP/NCCP, as recommended by the Transportation Water and Infrastructure
Committee.
FISCAL IMPACT:
None.
BACKGROUND:
The Board of Supervisors requested that the Transportation, Water and Infrastructure (TWI) Committee monitor
implementation of the HCP/NCCP.
APPROVE OTHER
RECOMMENDATION OF CNTY ADMINISTRATOR RECOMMENDATION OF BOARD COMMITTEE
Action of Board On: 09/25/2012 APPROVED AS RECOMMENDED OTHER
Clerks Notes:
VOTE OF SUPERVISORS
AYE:John Gioia, District I Supervisor
Candace Andersen, District II
Supervisor
Mary N. Piepho, District III
Supervisor
Karen Mitchoff, District IV
Supervisor
Federal D. Glover, District V
Supervisor
Contact: John Kopchik,
925-674-7819
I hereby certify that this is a true and correct copy of an action taken and entered on the minutes of the Board
of Supervisors on the date shown.
ATTESTED: September 25, 2012
David Twa, County Administrator and Clerk of the Board of Supervisors
By: June McHuen, Deputy
cc:
SD. 4
To:Board of Supervisors
From:TWI Committee
Date:September 25, 2012
Contra
Costa
County
Subject:Report on the Implementation of the East Contra Costa County Habitat Conservation Plan/Natural Community
Conservation Plan
BACKGROUND: (CONT'D)
The Year in Review report (attached) was recently reviewed and discussed by the TWI Committee. The report
was prepared by the East Contra Costa County Habitat Conservancy, the joint exercise of powers authority
formed by the County and four participating cities to manage implementation of the HCP/NCCP. The Year in
Review report provides a concise summary of recent activities. The TWI Committee wanted the Board to be
aware of the progress and accomplishments of the HCP/NCCP.
Four years into a 30-year plan, the HCP/NCCP is off to a fast start. The East Contra Costa County Habitat
Conservancy continues to experience success at securing grants for land acquisition and, working closely with the
East Bay Regional Park District, stayed ahead of targets for acquisition and for specific conservation
requirements. A new wetland restoration project was planned and constructed near Kirker Pass Road.
Additionally, several significant regional infrastructure projects were permitted and are under construction
including the Vasco Road Safety Project, Oakley Generating Station and the new eBART station in Antioch.
Another key recent development related to the long term goal of coordinating wetland permitting with the
HCP/NCCP process. In May of 2012, the U.S. Army Corps of Engineers, Sacramento District (Corps), issued
Regional General Permit #1 (RGP), which will provide for coordinated and steam-lined permitting of wetland
impacts for projects covered by the HCP/NCCP (see RGP attached). Staff from the Corps, joined by staff from the
Department of Conservation and Development will provide a verbal update on the HCP/NCCP and the new RGP.
CONSEQUENCE OF NEGATIVE ACTION:
None.
CHILDREN'S IMPACT STATEMENT:
Not applicable.
ATTACHMENTS
The Year in Review
Corps Regioanl General Permit for ECCC HCP/NCCP
×××××××××××× Funding ×××××××××××× The Conservancy takes in revenue from three primary sources: grants, fees and contributions to recovery. Various federal, state and private funding sources generously awarded $10,631,582 in grant money to Conservancy activities during 2011. Most grant funding awarded will be received and spent in future years. Fees received from the thirteen projects permitted in 2011 totaled $531,322, while contributions to recovery received from five projects totaled $317,425. Partners Implementing the HCP/NCCP City of Brentwood City of Clayton City of Oakley City of Pittsburg Contra Costa County Contra Costa County Flood Control and Water Conservation District East Bay Regional Park District East Contra Costa County Habitat Conservancy California Department of Fish and Game U.S. Fish and Wildlife Service Public Advisory Committee Agricultural-Natural Resources Trust of Contra Costa County California Native Plant Society Contra Costa Council Contra Costa County Citizens Land Alliance Contra Costa County Farm Bureau Discovery Builders Inc. Friends of Marsh Creek Watershed Home Builders Association of Northern California Rural/suburban residents (3) Save Mount Diablo For more information on the Conservancy and HCP/NCCP, see the website www.cocohcp.org, the HCP/NCCP Overview Booklet and the 2011 Annual Report (both available on website) To reach the Conservancy, please contact Maureen Parkes: maureen.parkes@dcd.cccounty.us (925) 674-7831 The Habitat Conservation Plan/Natural Community Conservation Plan and the Conservancy The HCP/NCCP or “Plan” gives local cities and agencies control over endangered species permitting in their jurisdiction. - Under the Plan, project proponents pay a fee or provide their own conservation, conduct limited avoidance measures and receive species permits from their local land use agency. Fees and grants fund Preserve System acquisitions, management and restoration. - The Conservancy implements and ensures compliance with the Plan and oversees assembly and operation of the HCP/NCCP Preserve System. Conservancy Board Members: Joel Bryant City of Brentwood Hank Stratford City of Clayton Jim Frazier City of Oakley Salvatore Evola City of Pittsburg Federal Glover Contra Costa County 2011 was a busy year for the East Contra Costa County Habitat Conservancy. The Conservancy continued to experience success at securing grants for land acquisition, and stayed ahead of targets for acquisition and for specific conservation requirements. A new wetland restoration project was planned and constructed. Additionally, several significant regional infrastructure projects were permitted and are under construction, and progress was made towards coordinating wetland permitting with the HCP/NCCP process. EAST CONTRA COSTA COUNTY HABITAT CONSERVANCY 2011 Year in Review Key Plan Facts and Figures: Year the Plan went into effect: 2007 Term of regional permits: 30 years Inventory area: 174,018 acres Amount of urban development impact allowed for: 8,670 to 11,853 acres Amount of rural infrastructure impact allowed for: 1,126 acres Eventual size of Preserve System: 23,800 to 30,300 acres Number of species covered: 28 * Funding from partners not included ** Includes development, wetland, stream and administrative fees *** Payments by permit recipients that fund habitat improvements beyond required avoidance and mitigation measures Sources of Conservancy Funding*, 2008-201190%8%2%Grants expendedFees**Contributions to recovery*** 1 U.S. Fish and Wildlife Service 2 Wildlife Conservation Board 3 Department of Water Resources 4 California Department of Fish and Game 5 Funding from partners not included. EBRPD contributed more than $2.2 million of its own funds or its grant funds to joint land acquisitions in 2011. New Conservancy funding in 2011 Amount Grants awarded in 2011: USFWS1 administered by WCB2 (acquisition) $4,463,936 Prop. 84 through DWR3 (acquisition/restoration) $650,000 CDGF4 NCCP Local Assistance (3 grants) (inventory/monitoring/mgmt. plan) $165,000 Gordon and Betty Moore Foundation (acquisition) $1,300,000 WCB Prop. 84 (4 grants) (acquisition) $4,052,646 Fees received in 2011 $531,322 Contributions to recovery received in 2011 $317,425 Total new funding in 20115 $11,480,329 8-2
Simulated view of eBART transfer platform in SR4 median California red-legged frog Project Permitting Thirteen projects received permit coverage under the Plan in 2011 (two urban development projects and eleven rural infrastructure projects), totaling approximately 25 acres of permanent impacts and 52 acres of temporary impacts on various land cover types. In addition, there were 59 feet of permanent and 155 feet of temporary impacts to streams. One entity which received permit coverage in 2011 was Contra Costa Generating Station LLC, for the construction and operation of the Oakley Generating Station Project, which forms part of the redevelopment of the DuPont Oakley property. Construction of the natural gas-fired plant will generate over 730 local union jobs and after start up approximately 22 fulltime operational jobs. The San Francisco Bay Area Rapid Transit District extension of transit services to a new terminus station east of Hillcrest Avenue in the City of Antioch, known as the eBART Phase II Project, prepared its application in 2011 and received permit coverage in early 2012. This $462 million project will generate over 600 construction jobs and 40 to 80 permanent jobs. Wetland Coordination The HCP/NCCP was designed to enable permit streamlining to extend beyond endangered species and include regional permitting under state and federal laws for impacts on jurisdictional wetlands and waters. In 2011, significant progress was made towards the issuance of a Regional General Permit (RGP) by the U.S. Army Corps of Engineers that enables expedited authorization of activities covered under the HCP/NCCP. Public outreach on the Draft RGP generated eleven supportive comment letters and a lead Corps District was designated. The RGP was issued on May 4, 2012. The next steps for wetland coordination include establishing an In Lieu Fee program, which would sanction payment of HCP/NCCP fees as suitable mitigation under the RGP, and continuing to pursue certification from the State Water Resources Control Board to achieve additional permit streamlining. Land Acquisition The first four years of Plan implementation have resulted in significant progress toward acquisition goals, including four properties acquired in 2011. All acquisitions to date, totaling 6,741 acres, have been completed in partnership with East Bay Regional Park District (i.e. EBRPD will own and manage Preserve System lands). Highlights of the Preserve System include the following achievements: • More than 5,000 acres of annual grassland preserved • Oak woodland preservation requirement exceeded by 168% • 56% of the oak savanna preservation requirements achieved • 38% of pond and 12% of alkali wetland preservation requirements achieved • 19 stands of covered plants preserved • Intermittent and ephemeral stream preservation requirements achieved • Occupied or suitable habitat provided for at least 20 of the 28 covered species There is still a long way to go, but the Conservancy is currently ahead of the average pace necessary to assemble the 30,300-acre Preserve System estimated to be required by Year 30 (2037). Habitat Restoration and Creation The Plan requires stream, wetland and pond restoration and creation to compensate for impacts to these habitat types. The Conservancy has aggressively pursued wetland and pond restoration requirements; to date, five restoration projects have been constructed. During 2011, the Conservancy completed construction of one restoration project in the Upper Hess Creek watershed. This project resulted in the restoration or creation of creek channel, seasonal wetland, alkali wetland and pond. The restored aquatic habitats and surrounding upland areas will support California tiger salamander (Ambystoma californiense), California red-legged frog (Rana draytonii), native grasses and alkali vegetation, as well as improve the hydrologic connectivity in the upper watershed. Conservancy projects that were constructed in prior years are monitored and managed to help ensure they are functioning well for species. This more intensive monitoring and management will continue for a minimum of five years. Close monitoring of restoration sites has informed management actions including: re-seeding areas, adjusting grazing patterns, and aggressively combating invasive weeds. Constructing the generating station’s fire pump foundation Surveying a wetland on Vaquero Farms North HCP/NCCP Activities By the Numbers: 2011 and Cumulative (through 12/31/11) Projects permitted in 2011: 13 Projects permitted to date: 30 Fees and contributions to recovery received in 2011: $848,747 Fees and contributions to recovery received to date: $2,729,948 Grant funding awarded in 2011: $10,631,582 Grant funding awarded to date: $45,746,267 Number of properties acquired in 2011: 4 Acres conserved in 2011: 2,185 Number of properties acquired to date: 17 Acres conserved to date: 6,741 Number of restoration projects constructed to date: 5 HCP/NCCP Preserve System Map Area impacted vs. area conserved Impacts Conserved Terrestrial 86 acres 6,687 acres Aquatic 0.61 acres 54 acres Streams 197 linear feet 155,012 linear feet 8-3
Contra Costa County Board of Supervisors
September 25, 2012
Catherine Kutsuris and John Kopchik
CCC Department of Conservation and Development
HCP/NCCP website: www.cocohcp.org
Update on the East Contra Costa County
Habitat Conservation Plan / Natural
Community Conservation Plan (HCP/NCCP)
and U.S. Army Corps’ New Regional Permit
Defining HCP, NCCP and RGP
HCP (Habitat Conservation Plan): A federally-approved plan
to conserve and permit impacts to endangered species.
NCCP (Natural Community Conservation Plan): Similar to
HCP, but approved by the State.
The East Contra Costa County HCP/NCCP enables the
County, the Cities of Brentwood, Clayton, Oakley and
Pittsburg, EBRPD and Flood Control to control species
permitting for their jurisdiction.
RGP (Regional General Permit): A permit issued by the U.S.
Army Corps of Engineers to cover a specified category of
projects, in this case projects covered by the HCP/NCCP.
The problems with project-by-project permitting:
Regional HCPs try to address these
problems
Milestones in Development of the HCP/NCCP
October 10, 2006 Final HCP/NCCP & EIR/EIS released
August 6, 2007 Approval by all local, state & federal agencies
2000/2001 Local agencies initiate HCP/NCCP planning process
January 15, 2008 HCP/NCCP Implementing Ordinances take effect
September 2012 After 4+ years of implementing the HCP/NCCP:
--Streamlined permitting for key projects (Vasco Road Safety, eBART,
Oakley Generating Station, SR4 Bypass)
--9,177 acres acquired
--5 restoration projects constructed
--U.S. Army Corps of Engineers
approves Regional General Permit
in May of 2012
Current Status of Plan
9,177 acres acquired by EBRPD under HCP
Restoration Projects
•Five Projects Constructed in First
Four Years (approx 12 wet acres)
Irish Canyon Riparian Restoration, 2010
Restoration: ______________
850 feet / 0.5 acres of oak
and buckeye riparian
restoration
Save Mount Diablo volunteers at work
planting
February 2010
Volunteers at work watering
US Army Corps of Engineers
BUILDING STRONG®
Update on Regional General Permit 1:
Minimal Impact Activities, East Contra Costa
County
Kate Dadey, Ph.D, Chief
William Guthrie, Senior Project Manager
California Delta Branch, Regulatory Division
U.S. Army Corps of Engineers, Sacramento District
BUILDING STRONG®
Regulatory Mission
To protect the Nation’s aquatic resources,
while allowing reasonable development through
fair, flexible and balanced
permit decisions.
Goal: “No Net Loss of Wetlands”
BUILDING STRONG®
BUILDING STRONG®
Brief Overview of Permit Types
Standard (“Individual”)
General Permits
►Minimal individual and cumulative
environmental impacts
Types of GPs
►Nationwide Permits (NWP)
►Regional general permits (RGP)
►Programmatic General Permits (PGP)
BUILDING STRONG®
BUILDING STRONG®
Challenges with Project-by-Project Permits
►For applicants:
►Less predictable (timing, permit conditions)
►Working with HCP Implementing Entities and Corps separately
►For Corps / Resources:
►Reactive
►Less comprehensive understanding of relative functions of waters
within the region - case-by-case impact/mitigation assessment
►Efficiency strong but not as streamlined as can be possible with
an RGP
►Overall: More moving parts that are less coordinated
BUILDING STRONG®
Some Key Advantages Provided by RGP
►For applicants:
►More predictable
►Consistent mitigation requirements
►Same agencies reviewing but more coordinated
►For Corps / Resources:
►Consistent standards lends reviewing efficiency
►Systematic mitigation approach benefits resources
►Win-win for regulated public & resources
►Moving parts proactively coordinated!
BUILDING STRONG®
Highlights of RGP-1
Issued May 4, 2012: The first RGP of its kind in the
nation (and region!)
Overlays HCP Plan Area & covers “covered activities”
Thresholds: 1.5 acres waters; 300 linear ft. of certain
stream types
Sacramento District processes for whole plan area
Enhanced Sec. 7 coordination between Corps and
USFWS
Valid for 5 years (can be renewed through life of HCP)
Mitigation approach
BUILDING STRONG®
Mitigation Overview
Mitigation requirements coordinated with HCP –
ratios and fees one and the same
Appropriate formalized approach to comply with the
Corps’ mitigation rule is pending – In-lieu Fee Program
ILF development underway: Prospectus circulated in
Public Notice 2/16/11, 7 comments received, all
supportive; IRT invited Conservancy to prepare ILF
instrument
Interim Mitigation Strategy has been approved for 1 year
as of 1 May 2012
BUILDING STRONG®
RGP-1: Roll-out Status
Issued:
►Deer Creek Road Safety Improvement
Project (16 May 2012)
Pending:
►Chevron KLM Site 1357 Pipeline
Maintenance
►Upper Sand Creek Detention Basin
Expansion
►Pittsburg Trash Capture
Key Observations:
►Highly enhanced ESA coordination timeline
(Corps – USFWS)
►Mitigation coordinated; avoids “double fees”
BUILDING STRONG®
RGP-1 Implementation: Next Steps
Continue to process incoming applications…
Conduct outreach sessions (one is scheduled
for Oct. 10th) with practitioners and hone
processing elements with agency partners
Continue coordination with Water Boards to
achieve programmatic 401 WQC
Work with Conservancy to develop and
implement an In-Lieu Fee Program
BUILDING STRONG®
Thank You
Link to RGP: http://www.spk.usace.army.mil/Portals/12/documents/regulatory/gp/GP-
01-w-encls.pdf
General Permit 1
U.S. Army Corps of Engineers, Sacramento District
1325 J Street, Room 1350, Sacramento, California 95814
http://www.spk.usace.army.mil/Missions/Regulatory.aspx
Minimal Impact Activities
East Contra Costa County, California
EFFECTIVE DATE: May 4, 2012
EXPIRATION DATE: May 4, 2017
ISSUING OFFICE: U.S. Army Corps of Engineers, Sacramento District
ACTION ID: SPK-2001-00147
PURPOSE: The purpose of this RGP is to provide a simplified and expeditious means to authorize
activities in waters of the United States (U.S.), including wetlands, that are substantially similar in
nature and cause only minimal individual and cumulative impacts, within the area covered by the East
Contra Costa County Habitat Conservation Plan/Natural Community Conservation Plan (HCP/NCCP),
dated December, 2006. This RGP is part of an overall strategy envisioned in the HCP/NCCP to balance
the protection of important natural resources with long term economic development in the area covered
by the HCP/NCCP. The HCP/NCCP is intended to enhance protection of important natural resources,
including 28 listed and non-listed species and waters of the United States, by coordinating conservation
activities at a regional and watershed scale, enabling protection of large, contiguous resource-rich areas
and preservation of ecosystem processes and watershed functions. Appendix J of the HCP/NCCP
contains a partial inventory and assessment of the functions and services of waters of the U.S. located
within the HCP/NCCP Plan Area. The HCP/NCCP, associated documents and other program
information are available to the public at: http://www.cocohcp.org. Definitions associated with this
RGP are provided under the “Definitions” section at the end of the RGP.
LOCATION: The area covered by this RGP is east Contra Costa County, including the cities of
Clayton, Brentwood, Oakley, and Pittsburg, and specific areas of unincorporated Contra Costa County.
It is geographically coincident with the “Plan Area” of the HCP/NCCP (see Figures 1a and 1b).
AUTHORITY: The RGP authorizes activities within the Plan Area that involve discharges of dredged
or fill material into waters of the U.S. under Section 404 of the Clean Water Act (CWA).
ACTIVITIES AUTHORIZED BY THIS REGIONAL GENERAL PERMIT: This RGP authorizes
specific categories of activities with minimal individual and cumulative impacts on the aquatic
environment that meet the terms and conditions of this permit. Temporary structures, fills, and work
necessary to construct an activity authorized by this RGP (e.g., cofferdams, access roads) are allowed,
provided such work complies with the terms and conditions of this RGP inclusive of special conditions
that the Corps may add. This RGP applies only to HCP/NCCP Covered Activities, as set forth in Section
Page 2 General Permit 1
U.S. Army Corps of Engineers, Sacramento District
1325 J Street, Room 1350, Sacramento, CA 95814-2922
http://www.spk.usace.army.mil/Missions/Regulatory.aspx
2.3 of the HCP/NCCP (also see Definitions section). Any question as to whether a proposed activity is
considered a Covered Activity under the HCP/NCCP shall be subject to confirmation by the East Contra
Costa County Habitat Conservancy (Conservancy) (see Definitions section). The HCP/NCCP Covered
Activities are divided among the following Activity categories in this RGP for purposes of assigning
Activity-specific conditions (see section Activity Specific Conditions):
1. Residential, commercial, industrial, institutional, and other urban developments and
associated infrastructure inside the Urban Limit Line of Contra Costa County or inside the
City Limits of the Cities of Brentwood, Clayton, Oakley and Pittsburg, including but not
limited to roads, utilities, parks, storm water management facilities, and water supply and
delivery facilities. (activity-specific conditions: 1 through 4).
2. Recreation projects, including parks, picnic areas, staging areas, trails and park maintenance
facilities. Applies only to the activities set forth in Sections 2.3.2 and 2.3.4 of the
HCP/NCCP. (activity-specific conditions: 1 through 4).
3. Flood control detention basins, reservoirs1, channels, and related facilities. Applies only to
the specific planned facilities set forth in Section 2.3.2 of the HCP/NCCP. (activity-specific
conditions: 1 through 4).
4. Transportation projects, including road construction and widening, bicycle trails, rail
projects, bridges and safety-related projects. Applies only to the specific planned facilities
set forth in Section 2.3.2 of the HCP/NCCP. (general conditions apply only).
5. Wetland and stream restoration, creation, enhancement and management. Applies only to
activities set forth in Sections 2.3.2 and 2.3.4 of the HCP/NCCP. (activity-specific
conditions: 1, 2 and 4).
6. Utility projects, including electrical transmission projects, cellular communication projects
and pipelines. Applies only to the activities set forth in Sections 2.3.2 and 2.3.4 of the
HCP/NCCP. (activity-specific condition 4).
7. Maintenance, repair, rehabilitation or replacement of any previously authorized (under the
RGP or other Corps permit), currently serviceable, structure or fill. Applies only to the
maintenance activities set forth in Sections 2.3.1 and 2.3.3 of the HCP/NCCP. (general
conditions apply only).
If there is any question as to which Activity category a proposed activity would apply to, the Corps will
determine the applicable Activity category.
This RGP does not cover any activities in waters of the U.S. conducted in emergency situations.
1 The proposed Los Vaqueros Reservoir Expansion project is not covered by the HCP/NCCP as per Section 2.4 of the
HCP/NCCP.
Page 3 General Permit 1
U.S. Army Corps of Engineers, Sacramento District
1325 J Street, Room 1350, Sacramento, CA 95814-2922
http://www.spk.usace.army.mil/Missions/Regulatory.aspx
TERMS OF AUTHORIZATION:
1. Applying for RGP authorization: Prior to commencing a proposed activity, applicants seeking
authorization under this RGP shall notify the Corps in accordance with RGP general condition
number 18 (Notification). If the Corps determines that an activity is not an eligible activity under
the RGP, it will notify the applicant in writing within thirty (30) calendar days and provide
instructions on the procedures to seek authorization under a standard permit, letter of permission or
Nationwide permit. If the Corps determines that a proposed activity is eligible for coverage under
the RGP, it will notify the applicant within 45 calendar days of receipt of a complete application. If
the Corps does not provide a written response to the applicant within 45 calendar days following
receipt of a complete application, the applicant may presume the proposed activity is an eligible
activity that may be covered under the RGP, provided the activity complies with all other terms and
conditions of the RGP.
2. Impact Thresholds for waters of the U.S.: Impacts to waters of the U.S. shall be avoided and
minimized to the maximum extent practicable. The loss of waters of the U.S. (including wetlands)
resulting from individual project impacts may not exceed a total of 1.5 acres or more than 300 linear
feet of perennial, intermittent or 3rd or higher order ephemeral streams (as defined in Table 2 of the
RGP and further described in the HCP/NCCP), unless the linear limit is waived in writing by the
Corps. Additional restrictions are listed in the General and Activity-Specific Conditions.
3. Single and complete project: The project must be a single and complete project. For example, if
construction of a residential development involves phases, the sum of all impacted areas would be
the basis for deciding whether or not the project will be covered by this RGP.
4. After-the-fact projects: This RGP may not be used to authorize activities after they have impacted
Waters of the U.S.
5. Compliance with HCP/NCCP Conditions: Activities to be authorized under this RGP must be
HCP/NCCP Covered Activities and must fully comply with the HCP/NCCP. Compliance with the
HCP/NCCP requires applicants to implement the appropriate conservation measures outlined in
Chapter 6 of the HCP/NCCP.
6. Special conditions: The Corps may add special conditions to an authorization to ensure the activity
complies with the terms and conditions of the RGP, and/or that adverse impacts on the aquatic
environment or other aspects of the public interest are individually and cumulatively minimal.
7. Activity completion: Any activity authorized by the Corps under the RGP must be completed within
three (3) years of the date it is authorized. The “authorization date” is the date the Corps verifies in
writing that the activity meets the terms and conditions of the RGP. The Corps will, on a case-by-
case basis, review requests for time extensions if the permittee fails to complete the activity within
three years. A time extension would be considered a reverification and would be subject to review
and approval policies in effect at the time of review. Pursuant to term #9, below, activities
Page 4 General Permit 1
U.S. Army Corps of Engineers, Sacramento District
1325 J Street, Room 1350, Sacramento, CA 95814-2922
http://www.spk.usace.army.mil/Missions/Regulatory.aspx
authorized under the RGP that are under construction or under contract for construction in reliance
upon this authorization will remain authorized provided the activity is completed within 12 months
of the date of the RGP’s expiration, modification or revocation, unless the Corps exercises its
discretionary authority to modify, suspend, or revoke the authorization of a specific project.
8. Discretionary Authority: The Corps has the discretion to suspend, modify, or revoke authorizations
under this RGP. This discretionary authority may be used by the Corps to also further condition or
restrict the applicability of the RGP for cases in which it has concerns associated with the Clean
Water Act Section 404(b)(1) Guidelines, or regarding any public interest factor. Should the Corps
determine that a proposed activity may have more than minimal individual or cumulative adverse
impacts to aquatic resources or otherwise be contrary to the public interest, the Corps will modify
the authorization to reduce or eliminate those adverse effects, or notify the applicant that the
proposed activity is not authorized by the RGP and provide instructions on how to seek authorization
under an individual permit. The Corps may restore authorization under the RGP at any time it
determines that the reason for asserting discretionary authority has been resolved or satisfied by a
condition, project modification, or new information. The Corps may also use its discretionary
authority to modify, suspend, or revoke the RGP at any time.
9. Expiration of RGP: This RGP is valid for five (5) years from the date of issuance (or reissuance).
At least sixty (60) calendar days prior to the expiration date of this RGP, the Corps will issue a
public notice, with an opportunity for public comment, describing the reasons for reissuing the RGP,
reissuing the RGP with modifications, or not reissuing the RGP for another five years. The Corps
may extend the RGP for six months beyond the expiration date if it is unable to reissue the RGP due
to unresolved issues. If the Corps has not reissued or extended the RGP by the expiration date, the
RGP will no longer be valid. This RGP may also be modified, suspended or revoked by the Corps at
any time deemed necessary. In such instance, the Corps will issue a public notice concerning the
action.
GENERAL CONDITIONS:
The following conditions apply to all Activity categories:
1. Threatened and Endangered Species: No activity is authorized under the RGP that does not comply
with the mandatory terms and conditions of the USFWS’s “Programmatic Biological Opinion for a
Regional General Permit for the East Contra Costa Habitat Conservation Plan/Natural Community
Conservation Plan, Contra Costa County, California” (USFWS #81420-2011-F-0655, dated April 30,
2012) (copy attached). The Biological Opinion contains mandatory terms and conditions to implement
the reasonable and prudent measures that are associated with “incidental take” authorization under this
RGP. Authorization under this RGP is conditional upon your compliance with all of the mandatory
terms and conditions of the Biological Opinion. Failure to comply with the terms and conditions of the
Biological Opinion would constitute non-compliance with the RGP. The USFWS is the appropriate
authority to determine compliance with the terms and conditions of the Biological Opinion, and with the
ESA. The permittee must comply with all applicable conditions of this Biological Opinion, including
those ascribed to the Corps.
Page 5 General Permit 1
U.S. Army Corps of Engineers, Sacramento District
1325 J Street, Room 1350, Sacramento, CA 95814-2922
http://www.spk.usace.army.mil/Missions/Regulatory.aspx
2. Water Quality Certification: Section 401 Water Quality Certification is required for activities to be
authorized by this RGP. The Corps may require additional water quality management measures to
ensure that the authorized activity does not result in more than minimal impacts, individually or
cumulatively.
3. Historic Properties: No activity is authorized under the RGP if the activity may affect historic
properties listed, or eligible for listing, in the National Register of Historic Places, until the requirements
of Section 106 of the National Historic Preservation Act (NHPA), as amended, have been satisfied.
Applicants must notify the Corps if the activity may have the potential to cause effects to any historic
properties listed, determined to be eligible for listing on, or potentially eligible for listing on the National
Register of Historic Places, including previously unidentified historic properties. The Corps will consult
with the State Historic Preservation Officer (SHPO), as appropriate, following the policy and procedural
standards of 33 CFR Part 325 Appendix C2.
4. Unanticipated Cultural Resources Discoveries: If previously unidentified cultural materials are
unearthed during construction, all work shall be halted until a qualified archaeologist can examine the
deposit and determine its nature and significance. In the event of discovery of possible human remains,
state law requires that the County Coroner be contacted.
5. Fills within 100-Year Floodplains: The activity must comply with applicable FEMA-approved state or
local floodplain management requirements.
6. Bed and Bank Stabilization: Bank stabilization activities are limited to: a) using the minimum amount
of material needed for erosion protection; b) no more than 500 feet in length along the bank, unless this
criterion is waived in writing by the Corps; and c) no more than an average of 1 cubic yard of material
per running foot placed along the bank below the plane of the ordinary high water mark or high tide line,
unless this criterion is waived in writing by the Corps.
7. Best Management Practices: Best Management Practices (BMPs) must be employed during
construction and in project design to protect water quality and minimize impacts of stormwater runoff
on aquatic resources. BMPs should be appropriately located in or adjacent to waters of the U.S. (e.g., silt
curtains). The applicant shall employ the following BMPs, as appropriate and feasible, in designing and
constructing the project. The applicant shall describe which BMPs are practicable as part of the
notification procedure as per general condition #18, subpart (b):
a. Preservation of natural resource features on the project site (e.g., floodplains, wetlands,
streams, and other drainageways, grasslands, woodlands, and native soils);
b. Preservation of natural water infiltration and storage characteristics of the site;
2 Inclusive of Appendix C Interim Guidance dated April 25, 2005 and January 31, 2007, or such guidance that is applicable at
the time that a permit application is submitted. Current guidance may be found on the Sacramento District’s web site at:
http://www.spk.usace.army.mil/organizations/cespk-co/regulatory/.
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c. Minimization of new impervious surfaces in project design (impervious surfaces may be
minimized through practices such as reducing road widths and clustering developments
designed around open space);
d. Structural measures that provide water quality and quantity control,
e. Structural measures that provide only quantity control and conveyance,
f. Construction BMPs;
g. Low impact development (LID) BMPs.
Examples of structural BMPs include: vegetated natural buffers, grassed swales, infiltration trenches,
level spreaders and channel grade controls. Examples of construction BMPs include: matting and filter
fencing, or other barrier methods to intercept/capture sediment.
8. Proper Maintenance: Any authorized structure or fill shall be properly maintained, including
maintenance necessary to ensure public safety and the movement of aquatic organisms.
9. Aquatic Life Movements: No activity may substantially disrupt the necessary life cycle movement of
aquatic species indigenous to the water body, including those species that normally migrate through the
area, unless the activity’s primary purpose is to impound water. Culverts placed in streams must be
installed to maintain low-flow conditions. If feasible, they should be designed as open-bottom culverts.
10. Equipment: Heavy equipment working in wetlands must be placed on mats, or other measures, such
as low-ground pressure equipment, must be taken to minimize soil disturbance.
11. Tribal Rights: No activity or its operation may impair reserved Tribal rights, including, but not
limited to, reserved water rights and treaty fishing and hunting rights.
12. Water Supply Intakes: No discharge of dredged or fill material may occur in the proximity of a
public water supply intake, except where the discharge is for the repair or improvement of the intake
structure(s), and/or adjacent bank stabilization.
13. Suitable Material: No discharge of dredged or fill material may consist of unsuitable material and
material discharged must be free from toxic pollutants in toxic amounts (section 307 of the Clean Water
Act). Unsuitable material includes, but is not limited to, trash, debris, car bodies, and asphalt.
14. Management of Water Flows: To the maximum extent practicable, the pre-construction course,
condition, capacity, and location of open waters must be maintained. The activity must be constructed to
withstand expected high flows. The activity must not restrict or impede the passage of normal or high
flows, unless the primary purpose of the activity is to impound water or manage high flows. The activity
may alter the pre-construction course, condition, capacity, and location of open waters if it benefits the
aquatic environment (e.g., stream restoration project).
15. Migratory Bird Breeding Areas: Activities in waters of the U.S. that serve as breeding areas for
migratory birds shall be avoided to the maximum extent practicable.
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U.S. Army Corps of Engineers, Sacramento District
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16. Removal of Temporary Fills and Restoration of Affected Areas: Temporary fills shall be removed in
their entirety and the affected areas returned to pre-construction elevations. The affected areas shall be
revegetated with native vegetation upon completion of the project. A restoration plan, which includes a
1-foot contour topographic map, must be submitted with the notification to the Corps.
17. Compensatory Mitigation: Mitigation for impacts to waters of the U.S. must be accomplished by
conforming to the minimum mitigation ratios set by the HCP/NCCP, as summarized in Table 1.
Mitigation proposals are required to be consistent with the Corps’ mitigation rule (33 CFR Part 332).
a. Mitigation may be accomplished by one or more of the following mechanisms: 1) payment of the
aquatic resources mitigation fee to the Conservancy in accordance with the in-lieu fee (ILF)
program envisioned to be established by the Conservancy; 2) purchasing credits from a Corps-
approved mitigation bank that also provides mitigation acceptable under the HCP/NCCP, and/or;
3) through a “permittee-responsible” mitigation project.
b. Prior to proceeding with the activity authorized by this RGP, a final mitigation plan must be
approved by the Corps and the Conservancy, and/or mitigation fees must be paid. When
mitigation fees are applicable, evidence of fee payment must be provided to the Corps before
commencement of the activity authorized by this RGP can be initiated.
c. If the RGP verification includes permittee-responsible compensatory mitigation, the mitigation
plan must contain a reporting procedure consistent with the Corps’ mitigation rule (33 CFR Part
332.4[c][10]), Monitoring Requirements.
18. Notification: The applicant shall provide written notification (i.e., a complete application) for a
proposed activity to be authorized under the RGP prior to commencing the activity. The Corps’ receipt
of the complete application is the date when the Corps receives all required notification information
from the applicant (see below). Written notification shall include all of the following:
a. A letter signed by the applicant requesting authorization under the RGP, identifying the
Activity Category(s), a description of the proposed activity, the location of the activity (with
latitude and longitude), and the area (in acres, and/or linear feet as applicable) of waters of the
U.S., including wetlands, to be impacted;
b. For each general and applicable activity-specific condition of this RGP, a brief narrative
describing how the activity would comply with the condition, or that the condition does not
apply;
c. Vicinity and project site maps;
d. A delineation of waters of the U.S., including wetlands, for the project site and for areas
immediately adjacent to the project site. On-site wetlands must be delineated using the Corps
Wetlands Delineation Manual (1987) and Arid West Region Regional Supplement (2008), or
most recent manual(s) in effect at the time of the applicant’s proposal. Off-site wetlands may
be identified through the use of reference materials including local wetland inventories, soil
surveys and aerial photography. The delineation shall also include information on wetlands
and waters, as defined in the HCP/NCCP, that are/may not be waters of the U.S.
e. Preliminary plans (on 8 ½” x 11” or 14” reduced-sized drawings) showing all aspects of the
proposed activity and the location of avoided and impacted waters of the U.S. Plan-view and
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http://www.spk.usace.army.mil/Missions/Regulatory.aspx
cross-section plans shall be included. Both temporary (e.g., access, staging) and permanent
impacts to waters of the U.S. shall be shown. The plans shall include grading contours and
existing and proposed structures, such as buildings, roadways, stormwater management
facilities, utilities, construction access areas and water conveyance structures. The drawings
shall also show buffer areas, open space designations, locations of BMPs, deed restricted
areas, and restoration areas, if required; and
f. A written statement explaining how the activity has been designed to avoid and minimize
adverse effects, both temporary and permanent, to waters of the U.S. For compensatory
mitigation proposed in accordance with general condition #17, submit a preliminary plan to
offset unavoidable impacts to waters of the U.S.
g. A cultural resource survey report for the project site, including all staging, access and
construction areas. The report must be prepared in accordance with the Sacramento District’s
Guidelines for Compliance with Section 106 of the NHPA (dated February 25, 2011, or more
recent guidance (if applicable) at the time a permit application is submitted.
If the Corps determines that the activity complies with the terms and conditions of the RGP, including
confirmation that proposed impacts to aquatic resources are minimal, the Corps will notify the applicant
in writing and include any special conditions deemed necessary. If the Corps determines the impacts of
the proposed activity are more than minimal, the Corps will notify the applicant that the project does not
qualify for authorization under the RGP and instruct the applicant on the procedures to seek
authorization under an individual permit.
19. Reporting Responsibilities: The permittee must submit a letter report to the Corps within 30 days of
project completion. The report will contain the following:
a. The Corps’ file number;
b. Photographs showing pre- and post-construction project conditions;
c. A completed compliance certification.
20. Access: The permittee must allow representatives from the Corps to inspect the authorized activity
at any time deemed necessary to ensure that it is being or has been accomplished in accordance with the
terms and conditions of the permit.
21. Transfer of RGP Authorization: If the permittee sells the property associated with this permit, the
permittee must obtain the signature and mailing address of the new owner on the permit verification
letter, and forward a copy to this office to validate the transfer.
ACTIVITY SPECIFIC CONDITIONS:
The following conditions apply to Activity categories specified at the end of each condition.
1. Stream Setbacks. Consistent with the requirements of the HCP/NCCP, stream setbacks shall be
established. See the HCP/NCCP for detailed stream setback requirements, summarized in Table 2 of this
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RGP. Waters of the U.S. shall not be filled in order to meet the buffer requirements (Activity categories
1, 2, 3 and 5).
2. Permanent Protections. All preserved, created, restored or enhanced waters of the U.S. and adjacent
buffers on the project site shall be preserved and permanently protected through a deed restriction,
conservation easement, or other appropriate real estate or legal instrument, consistent with the
requirements of the HCP/NCCP as determined by the Corps. A recorded copy of the real estate
instrument must be provided to the Corps prior to proceeding with any activity otherwise authorized by
this RGP (Activity categories 1, 2, 3 and 5).
3. Fencing and Signage. Preserved areas on the project site must be fenced and signed as sensitive areas
to discourage human disturbance (Activity categories 1, 2 and 3).
4. Utility Lines. All utility lines shall be constructed in accordance with the following:
a. The construction area for linear utility line projects shall be limited to a width of 75 feet, unless
this limit is waived in writing by the Corps.
b. For utility line projects, directional drilling, clear span or other techniques that do not contact the
waterbody shall be used if the waterbody contains perennial flow.
c. If the project involves the use of directional drilling below waters, notification shall include a
contingency plan. The plan will include actions that will be taken to stabilize the work area and
avoidance/contingency measures in the event of a potential “frac-out.”
d. Material resulting from trench excavation may be temporarily sidecast (up to 60 days) into
waters of the U.S., provided that the material is not placed in such a manner that is dispersed by
currents or other forces. The Corps may extend the period of temporary side casting for no more
than a total of 180 days, where appropriate.
e. Utility lines must not adversely alter existing hydrology, including draining of wetlands. In
wetland areas, utility line trenches shall be lined with clay, or other impermeable materials or
structures (such as cut-off walls) to ensure that the trench through which the utility line is
installed does not drain waters of the U.S. In addition, to prevent a french drain effect, gravel
cannot be used as backfill material in the top 10 feet of the trench.
f. In wetland areas, the top 6”-12” of the trench shall be backfilled with topsoil excavated from the
trench in the same stratification in which it was removed.
g. Excess material shall be removed to upland areas immediately upon completion of utility line
construction in any segment of the project containing waters of the U.S. In no case shall the
excess material be left in place until the entire utility line is completed.
h. The construction area, including unprotected slopes and streambanks, shall be stabilized (e.g.,
blanketed and seeded) immediately upon completion of the utility line construction in any
segment of the project. In no case shall soil stabilization be delayed until the entire utility line is
completed.
i. Temporarily disturbed construction areas must be restored to pre-construction conditions,
including grading to original contours and revegetating (with native vegetation or other
appropriate vegetation approved by the Corps) immediately upon completion of the project. A
restoration plan, which includes a 1-foot contour topographic map, shall be submitted with
notification (Activity categories 1, 2, 3, 5 and 6).
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U.S. Army Corps of Engineers, Sacramento District
1325 J Street, Room 1350, Sacramento, CA 95814-2922
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LIMITATIONS AND RESTRICTIONS:
1. The Corps has authority to determine if an activity complies with the terms and conditions of the
RGP.
2. This RGP does not obviate the need to obtain other Federal, state, or local permits, approvals, or
authorizations required by law.
3. This RGP does not grant any property rights or exclusive privileges.
4. This RGP does not authorize any injury to the property or rights of others.
5. This RGP does not authorize interference with any existing or proposed Federal project.
DEFINITIONS:
Activity is any discharge of dredged or fill material into waters of the U.S. under Section 404 of CWA.
Activity categories are descriptions of HCP/NCCP Covered Activities listed in this RGP for purposes of
assigning activity-specific conditions.
Activity-specific conditions are RGP conditions that would apply to specified Activity categories
defined in this RGP.
Applicant is the individual, organization, or company requesting authorization under the RGP.
Authorization is written verification by the Corps that an activity qualifies for, and may proceed under,
the RGP provided all terms and conditions of the RGP are followed.
Compensatory mitigation is the restoration, establishment (creation), enhancement, and/or in certain
circumstances preservation of aquatic resources for the purposes of offsetting unavoidable adverse
impacts which remain after all appropriate and practicable avoidance and minimization has been
achieved. See also “in-lieu fee” definition.
Complete application is all required notification materials that must be submitted by the applicant to the
Corps, as listed in general condition #18. If all materials are not submitted, the application is considered
incomplete and will not be processed under the RGP.
Conservancy is the East Contra Costa County Habitat Conservancy, a joint exercise of powers agency
formed by the Cities of Brentwood, Clayton, Oakley and Pittsburg and Contra Costa County to perform
the role of Implementing Entity for the HCP/NCCP.
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U.S. Army Corps of Engineers, Sacramento District
1325 J Street, Room 1350, Sacramento, CA 95814-2922
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Emergency refers to the guidance provided in 33 CFR 325.2(e)(4): “…a situation which would result in
an unacceptable hazard to life, a significant loss of property, or an immediate, unforeseen, and
significant economic hardship if corrective action requiring a permit is not undertaken within a time
period less than the normal time needed to process the application under standard procedures. This RGP
does not cover any activities in waters of the U.S. conducted in emergency situations.
General conditions are RGP conditions that would apply to all activities authorized by this RGP.
HCP/NCCP is the East Contra Costa County Habitat Conservation Plan/Natural Community
Conservation Plan dated December, 2006. The United States Fish and Wildlife Service (“USFWS”),
under incidental take permit TE 160958-0, and the California Department of Fish and Game (“CDFG”),
under incidental take permit 2835-2007-01-03, have approved the HCP/NCCP and have authorized the
“HCP/NCCP Permittees” to take certain species of plants and wildlife listed under the ESA and/or
covered under the state of California’s Natural Community Conservation Planning Act (NCCPA) while
carrying out or approving certain development and other “covered activities.” Take is defined under
federal and state laws.
HCP/NCCP Covered Activity means an activity or project within one of the categories of activities set
forth in Section 2.3 of the HCP/NCCP that has been approved by an HCP/NCCP Permittee for coverage
under the HCP/NCCP.
HCP/NCCP Permittee is any of the following eight local agencies that have approved the HCP/NCCP
and have been authorized by USFWS and CDFG to take certain species, as take is defined respectively
under federal and state law. These are the Cities of Brentwood, Clayton, Oakley and Pittsburg, Contra
Costa County, the Contra Costa County Flood Control and Water Conservation District, the
Conservancy, and the East Bay Regional Park District.
Historic properties are as defined in 36 CFR Part 800.16(l). It means any prehistoric or historic district,
site, building, structure, or object included in, or eligible for inclusion in, the National Register of
Historic Places maintained by the Secretary of the Interior. This term includes artifacts, records, and
remains that are related to and located within such properties. The term includes properties of traditional
religious and cultural importance to an Indian tribe or Native Hawaiian organization and that meet the
National Register criteria.
Impact is the direct and indirect loss of waters of the U.S., including wetlands, which results from
implementation of a proposed activity. See also “loss of waters” definition.
In-lieu fee refers to an in-lieu fee (ILF) program as defined in 33 CFR Part 332.2. An ILF program
involves the restoration, establishment (creation), enhancement and/or preservation of aquatic resources
through funds paid to a governmental or non-profit natural resources management entity to satisfy
compensatory mitigation (see above definition) requirements for Department of the Army (DA) permits.
As required by 33 CFR Part 332.8(a), all ILF programs must be approved prior to being used to provide
compensatory mitigation for projects authorized by the Corps.
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1325 J Street, Room 1350, Sacramento, CA 95814-2922
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Loss of waters of the U.S. refers to waters that are permanently adversely affected by filling, flooding,
excavation, or drainage because of the regulated activity. Permanent adverse effects include permanent
discharges of dredge or fill material that change an aquatic area to dry land, increase the bottom
elevation of a waterbody, or change the use of an aquatic feature. The acreage of loss of waters of the
U.S. is a threshold measurement of the impact to jurisdictional waters for determining if the project may
qualify for the RGP; it is not a net threshold that is calculated after considering compensatory mitigation
that may be used to offset losses of aquatic functions and services.
Mitigation see “compensatory mitigation” definition.
Mitigation bank is a site where aquatic resources (e.g., wetlands, streams) are restored, established,
enhanced, and/or preserved for the purpose of providing compensatory mitigation for impacts authorized
by DA permits.
Notification is the submission of required information by the applicant to the Corps for a complete
application.
Permittee is an entity that has received authorization to conduct activities in waters of the U.S. under this
RGP.
Permittee-responsible mitigation refers to a type of compensatory mitigation as defined in 33 CFR Part
332.2, entailing aquatic resource restoration, establishment, enhancement, and/or preservation activity
undertaken by the permittee (or an authorized agent or contractor) to provide compensatory mitigation
for which the permittee retains full responsibility.
Plan Area is the area shown in Figure 1-1 of the HCP/NCCP and Figures 1a and 1b of this RGP. It is
the area analyzed by the HCP/NCCP and covered by the USFWS and CDFG incidental take permits
issued pursuant to the HCP/NCCP. In the HCP, the Plan Area is also referred to as the “Inventory
Area.” This RGP uses the term Plan Area.
Project site is the land, including waters of the U.S. and uplands, utilized for a single and complete
project. The project site includes the land cleared, graded, and/or filled to construct the single and
complete project, including any buildings, utilities, stormwater management facilities, roads, yards, and
other attendant features. Temporary construction areas (e.g., access and staging) are included. The
project site also includes any other land and attendant features that are used in conjunction with the
single and complete project, such as open space, roads and utilities.
Single and complete project is the “total project proposed or accomplished by one owner/developer or
partnership or other association of owners/developers” (33 CFR 330.2[i]).
Special conditions are conditions added by the Corps for projects on a case-by case basis to ensure an
activity has minimal impacts on aquatic resources and complies with the RGP. The Corps’ authority to
require special conditions is provided in 33 CFR Part 325.4(a).
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U.S. Army Corps of Engineers, Sacramento District
1325 J Street, Room 1350, Sacramento, CA 95814-2922
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Stream order refers to the numeric identification of the reaches within a stream network. This document
follows the stream ordering system of Strahler (1964)3. In this system, a first order stream is a stream
with an identifiable bed and bank, without any tributary streams. A second order stream is formed by
the confluence of two first order streams. A third order stream is formed by the confluence of two
second order streams, and so on. Addition of a lesser order stream does not change the stream order of
the trunk stream.
Suspension is the temporary cancellation of the authorization while a decision is made to modify, revoke
or reinstate the authorization.
Terms and conditions are the parameters, including thresholds, limitations and requirements, for
completing an activity under the RGP. These parameters are described in each Activity category and in
the general conditions and Activity-specific conditions. Special conditions may also be added by the
Corps on individual authorizations to ensure an activity has minimal individual and cumulative impacts.
Urban Limit Line is the boundary for urban growth that has been set for Contra Costa County in the
Contra Costa County General Plan, as amended from time to time.
Utility line is any pipeline used to transport a gaseous, liquid, liquefiable or slurry substance for any
purpose, and any cable, line or wire used to transmit electrical energy, telephone, radio signals,
television signals or data communication. This definition does not include pipes or ditches which serve
to drain a water of the United States, such as drainage tile; however, it does apply to pipes conveying
drainage from one area to another.
Waters of the U.S. are as defined in 33 CFR Part 328.3(a). For purposes of wetlands regulated under
Section 404 of the Clean Water Act under this RGP, the identification and delineation of wetlands must
be in accordance with the most recent guidance and wetland delineation manual and manual supplement
issued by the Corps.
Definitions found at 33 CFR Parts 320-323, 325-329, and 331-332 and 40 CFR Part 230 are also
applicable to this RGP and are incorporated by reference herein.
CONTACTS AND ADDITIONAL INFORMATION:
For additional information, about RGP 1, please contact the U.S. Army Corps of Engineers, Sacramento
District at the address below, phone number (916) 557-5250.
ATTACHMENTS:
Figure 1a: General Location of HCP/NCCP Plan Area and Area Covered by RGP
Figure 1b: HCP/NCCP Plan Area and Area Covered by RGP
Table 1: Required Ratios and Estimated Preservation, Restoration, and Creation Requirements for
Aquatic Land-Cover Types Under Initial and Maximum Urban Development Area
3 Strahler, A.N. 1964. Quantitative Geomorphology of drainage basins and channel networks; section 4-2, in Handbook of
Applied Hydrology, ed. Ven te Chow, McGraw-Hill, New York.
Page 14 General Permit 1
Table 2: Stream Setback Minimum Requirements for Streams
Programmatic Biological Opinion for a Regional General Permit for the East Contra Costa Habitat
Conservation PlanIN atural Community Conservation Plan, Contra Costa County, California.
(USFWS #81420-2011-F-0655, dated April 30, 2012)
This permit becomes effective when the Federal official, designated to act for the Secretary ofthe Army,
has signed below.
Chief, Regulatory Division
Sacramento District
Date
1 MaV ?fj/2----
U.S. Army Corps of Engineers, Sacramento District
1325 J Street, Room 1350, Sacramento, CA 95814-2922
http://www.spk.usace.army.mil/M issions/Reg u latory. aspx
San Joaquin
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Solano
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Alameda
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Contra Costa
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Stanislaus
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San Mateo
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Sacramento
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Napa
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Marin
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Sonoma
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Santa Clara
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San Francisco
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Yolo
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Figure 1a: General Location of HCP/NCCP Plan Area and Area Covered by RGP
Army Corps
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San FranciscoSan Francisco
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Non-urban Parks,
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Cities Participating
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Walnut
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Figure 1b: HCP/NCCP Plan Area and Area Covered by RGP
Army Corps
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Sacramento Sacramento
District District
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San FranciscoSan Francisco
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Text
City Not Participating
in HCP/NCCP and
Not Eligible for RGP
Area Covered
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Restoration Creation Riparian woodland/scrub2:1 30 35 60 70 205 2051:1–303520 205055 Wetlands and Ponds Perennial wetlands31:1 74 7574 753231 23231:1–747510 1084857 Seasonal wetlands3:1 43 56129 1683, 4172 1723, 4, 52:1 – 86 112 20 20 106 1324, 7 Alkali wetland3:1 28 3184 934168 16842:1–5662 5 5 61674 Ponds2:1 7 814 1680 80– 1:1 7 8 8 8 15 16 Slough/channel0.5:1 72 7236 36137 1371:1 or riparian–7272 0 0 72729 Aquatic (open water)1:1 12 12 12123 123– 0.5:1 (ponds)6 (ponds)6 (ponds)0 0 6 (ponds)6 (ponds)9Total Aquatic Land Cover Types (acres)–266 289 397 470 1,117 1,117331 370 63 63 394 433 Perennial streams (miles) 2:1 0.3 0.40.6 0.86181846, 71:1 1:1 if restoration not feasible0.3 0.4 0 0 0.3 0.47,10 Intermittent streams (miles)1:10.3 0.4 0.3 0.461841846, 71:1 1:1 if restoration not feasible0.3 0.4 0 0 0.3 0.47,10 Ephemeral streams (miles)1:1454 518418471:1 1:1 if restoration not feasible450 0457,10Initial Urban Development Area Scenario7 The approximate length of all streams of all types in the Acquisition Analysis Zone is 184 miles.6 Maximum allowable impacts for perennial and intermittent streams could not be separately estimated. Cumulative impacts for these two categories were estimated at 0.6 miles for the Initial Urban Development Area and 0.8 for the Maximum Urban Development Area. Forthe purposes of this table, it is assumed that the impacts are evenly split between the two categories.Initial Urban Development Area ScenarioMaximum Urban Development Area ScenarioInitial Urban Development Area Scenario8 Undetermined wetlands are either seasonal wetlands or perennial wetlands. Mitigation of seasonal wetlands will be accomplished through restoration at 2:1. Mitigation of perennial wetlands will be accomplished through in-kind creation at 1:1. This table assumes 75% of the undetermined wetlands are perennial wetlands and 25% are seasonal wetlands.9 Loss of slough/channel will be compensated by either restoring slough/channel at a 1:1 ratio or restoring riparian woodland/scrub at a 1:1 ratio (see text). These calculations assume all slough/channel impacts will be compensated through riparian woodland/scrub restoration because of the limited opportunities for slough/channel creation. Loss of open water will be compensated by creating ponds (see text).10 Streams will be restored at a 1:1 ratio where feasible. Where stream restoration is not feasible, out-of-kind creation of seasonal wetlands or permanent wetlands will be required to replace some of the functions of the lost stream at a 1:1 ratio. See Conservation Measure 2.10 for more details.5 The actual amount of seasonal wetlands available for preservation in the inventory area is unknown because of a lack of field surveys. The allowable impact to seasonal wetlands by covered activities will be capped at the amount required to preserve seasonal wetlands at the required 3:1 ratio. For example, if only 30 acres are preserved, allowable impacts will be capped at 10 acres. Initial Urban Development Area ScenarioEstimated Impact1 (acres)Estimated Preservation Requirement 1 (acres)Minimum Available in Acquisition Analysis Zones2 (acres)Estimated Restoration/ Creation Requirement1 (acres)Restoration or Creation Required to Contribute to Recovery (acres)Maximum Urban Development Area Scenario1 Actual impacts, preservation requirements and restoration/creation requirements will be based on field-delineated resources at impact sites and application of the required preservation ratios in this table.2 Many land cover types were underestimated in the mapping conducted for this HCP/NCCP, so these figures represent minimum acreages of what is available for preservation. See Chapter 3 for a discussion of the mapping limitations. Table 1. Required Ratios and Estimated Preservation, Restoration and Creation Requirements for Aquatic Land-Cover Types under Initial and Maximum Urban Development Area (Combines tables 5.5a, 5.5b, 5.16 and 5.17 of HCP)3 Undetermined wetlands could be seasonal wetlands or perennial wetlands (e.g., freshwater marsh). Seasonal wetlands will be mitigated at a preservation ratio of 3:1; perennial wetlands will be mitigated at a preservation ratio of 1:1. This table assumes 75% of undetermined wetlands are perennial wetlands and 25% are seasonal wetlands.4 Seasonal and alkali wetland acreage was quantified as the minimum polygon encompassing clusters of seasonal pools or drainages (i.e., wetland complexes). Impacts and land acquisition requirements will be tracked by jurisdictional wetland boundary, so estimates in this table overstate the expected impacts to and preservation of these land cover types. Impact restrictions and preservation ratios apply only to wetted acres.Initial Urban Development Area ScenarioMaximum Urban Development Area ScenarioMaximum Urban Development Area ScenarioInitial Urban Development Area ScenarioMaximum Urban Development Area ScenarioNotes:Preservation RequirementsRestoration & Creation RequirementsAquatic Land Cover TypeRequired Preservation RatioImpact & preservation notesAvailabilty notesRequired Restoration and Creation Ratios (in addition to preservation requirements)restoration / creation notesEstimated Total Restoration or Creation1 (acres)Maximum Urban Development Area Scenario
15 Table 2: Stream Setback Minimum Requirements for Streams4 Stream Reach Type and Location1 Buffer Objective/ Function (from Figure 5-11) Example Sites in Inventory Area Minimum Setback (from top of bank measured in aerial perspective2) Conditions and Limitations on Impacts To Streams3 Conditions and Limitations on Impacts Within Setbacks4 Comments Linear Limitations on Impacts to Streams Activities for Which Stream Impacts Will Be Authorized Limitations on Area of Impacts Within Setback5 Activities for Which Setback Impacts Will Be Authorized 1st and 2nd order6 ephemeral reaches in urban and agricultural areas N/A Multiple unnamed tributaries to intermittent and perennial reaches Avoidance and minimization measures for drainages must be documented but no setback is required No limitations Any activities No limitations Any activities These reaches are located in dense urban and intensive agricultural areas, and provide low habitat function for covered species. Avoidance and implementation of Conservation Measure 1.10 will minimize impacts to water quality and hydrologic functions. Concrete-lined channels Enhance water quality; retain restoration potential Reaches of Kirker Creek 20 ft No limitations Any activities No limitations Any activities These reaches are located in dense urban areas and provide low habitat function for covered species. A minimal buffer width will reduce sediment and nutrient inputs from surface flows, retain some potential for stream restoration, and provide for recreational opportunities. 1st and 2nd order6 ephemeral reaches in natural areas Erosion and nutrient control; Multiple unnamed tributaries to intermittent and perennial reaches 25 ft No limitations Any activities No limitations No limitations, but avoidance and minimization must be documented. Although ephemeral streams play a limited role in providing habitat to covered species, these systems represent the first point of entry for sediment and other contaminants into downstream reaches. Thus, unlike the stream types below, the primary objective of the setback for 4 Stream setbacks apply Within the Urban Limit Line or City Limits of Brentwood, Clayton, Oakley or Pittsburg.
16 Stream Reach Type and Location1 Buffer Objective/ Function (from Figure 5-11) Example Sites in Inventory Area Minimum Setback (from top of bank measured in aerial perspective2) Conditions and Limitations on Impacts To Streams3 Conditions and Limitations on Impacts Within Setbacks4 Comments Linear Limitations on Impacts to Streams Activities for Which Stream Impacts Will Be Authorized Limitations on Area of Impacts Within Setback5 Activities for Which Setback Impacts Will Be Authorized ephemeral streams is to filter out sediment and contaminants before they degrade downstream habitat. Perennial, intermittent, or 3rd or higher order6 ephemeral streams in urban areas except Marsh Creek mainstem Enhance water quality; retain restoration potential Lower Willow Creek, Lower Kirker Creek, Lower Sand and Deer Creeks 50 ft 300 feet Necessary bridges and outfalls Up to 15% of setback area Necessary bridges and outfalls, access and maintenance roads for flood control, c3 facilities, and trails These reaches are located mostly in dense urban areas and provide low habitat function for covered species. However, potential may exist for restoration of riparian vegetation and minimal floodplain areas. In addition, a minimal buffer width will reduce sediment and nutrient inputs from surface flows and provide for recreational opportunities. Perennial, intermittent, or 3rd or higher order6 ephemeral streams in agricultural or natural areas and Marsh Creek mainstem Enhance water quality; retain restoration potential See examples below7 75 ft 300 feet Necessary bridges and outfalls Up to 15% of setback area Necessary bridges and outfalls, access and maintenance roads for flood control, trails, and other necessary facilities approved by wetlands agencies These reaches retain the greatest habitat value and potential for restoration within the Urban Limit Line. The buffer will filter sediment and other contaminants, maintain habitat for covered species, allow for restoration of riparian vegetation and some small floodplain areas, as well as providing recreation opportunities. 1 Location parameters (e.g., “agricultural areas”, “natural areas”, etc.) describe the setting of the stream at the time of completing this HCP/NCCP and refer to the fee zones and urban landcover shown in Figure 9-1. 2 Where native woody riparian vegetation is present, minimum setbacks must extend to the outer dripline of the riparian vegetation or the specified number of feet measured from top of bank, whichever is greatest. Riparian vegetation is defined broadly to include oaks and other woody species that function as riparian
17 corridors. Setbacks must also meet minimum setback requirements of the applicable local land use agency. Contra Costa County has an ordinance regulating impacts near unimproved earthen channels. This Ordinance requires a “structure setback line” that varies between approximately 30 feet and 50 feet from top of bank depending on the height of top of bank above the channel invert (County Code Title 9, Division 914-14.012). 3 Mitigation is required for all impacts to streams, as described in Chapter 5 of the HCP/NCCP. Restoration requirements are summarized in Tables 5-16, 5-17, and 9-5. Preservation requirements are summarized in Tables 5-5a and 5-5b and may be accomplished through payment of the development fee described in Section 9.3.1 or through provision of land in lieu of fees. 4 Impacts within setbacks must be mitigated through: a) payment of the development fee described in Section 9.3.1 over the entire property including the setback and the stream channel; and b) through payment of the riparian impact fee (see Table 9-5 of HCP/NCCP) for every acre of impact within the setback or through direct performance of riparian restoration at a 0.5 to 1 ratio on-site or off-site. 5 Restrictions will be measured as a percentage of the setback area excluding the area the of the stream channel. 6 Stream order refers to the numeric identification of the links within a stream network. This document follows the stream ordering system of Strahler (1964). In this system, a first order stream is a stream with an identifiable bed and bank, without any tributary streams. A second order stream is formed by the confluence of two first order streams. A third order stream is formed by the confluence of two second order streams, and so on. Addition of a lesser order stream does not change the stream order of the trunk stream. 7Perennial streams in agricultural or natural areas within the Inventory Area consist of the following: a. Mount Diablo Creek, Russelman Creek, Peacock Creek upstream of the Oakhurst Country Club property, and tributaries to Mount Diablo Creek within Mount Diablo State Park; b. Kellogg Creek in the Foothills/Upper Valley and Delta geomorphic zones; c. Brushy Creek in the Delta and Lower Valley/Plain geomorphic zones; d. Indian, Rock, Sand Mound, Dutch, Piper, and Taylor Sloughs, and False River (does not include reaches in concrete channels); and e. Sand Creek and Oil Canyon Creek in the Montane geomorphic zone.
United States Department of the Interior
In Reply Refer To:
81420-2011-F-0655
Kathleen A. Dadey
Chief, California Delta Branch
Attn: Mary Pakenham-Walsh
Regulatory Division
U.S. Army Corps of Engineers
650 Capitol Mall, Suite 5-200
Sacramento, California 95814
FISH AND WILDLIFE SERVICE
Sacramento Fish and Wildlife Office
2800 Cottage Way, Room W-2605
Sacramento, Califomia95825-1846
APR 302012
U.S.
FISH & WILDLIFE
~SERVICE
~ . ~
~ .. ,. ,'i'l~
0>, 'J1l'"
Subject: Programmatic Biological Opinion for a Regional General Permit for the East Contra
Costa Habitat Conservation PlanlNatural Community Conservation Plan, Contra
Costa County, California (Corps file number SPK-2001-00147)
Dear Ms. Dadey:
This programmatic Biological Opinion has been prepared in response to the U.S. Army Corps of
Engineers' (Corps) June 14,2011, request for section 7 consultation with the U.S. Fish and
Wildlife Service (Service) for multiple activities that would be authorized under a Corps
Regional General Permit (RGP) within the permit area for the (Plan Area) for the East Contra
Costa Habitat Conservation PlanlNatural Community Conservation Plan (HCPINCCP). At issue
are the effects of this action on the threatened California red-legged frog (Rana draytonii),
threatened Central California Distinct Population Segment (DPS) of the California tiger
salamander (Ambystoma californiense) (Central California tiger salamander), threatened
Alameda whipsnake (Masticophis laterals euryxanthus), threatened giant garter snake
(Thamnophis gigas) endangered San Joaquin kit fox (Vulpes macrotis mutica), threatened vernal
pool fairy shrimp (Branchinecta lynch!) and its critical habitat, the endangered longhorn fairy
shrimp (Branchinecta longiantenna) and its critical habitat, and the endangered vernal pool
tadpole shrimp (Lepidurus packardi). This programmatic Biological Opinion is issued under the
authority of the Endangered Species Act, as amended (16 U.S.C. 1531 et seq.) (Act or ESA).
This document is based on: (1) the draft Department o/the Army Permit Regional General
Permit Number I -Minimal Impact Activities-East Contra Costa County, California dated June
14, 2011; (2) a public notice for the proposed issuance of a Regional General Permit (SPK-200 1-
00147) for activities covered under the HCPINCCP dated February 2011; (3) a public notice for
the proposed in-lieu fee program in conjunction with the HCPINCCP (SPK-2001-00147) dated
January 2011; (4) the final East Contra Costa Habitat Conservation Plan/Natural Community
Conservation Plan dated October 2006; (5) Exhibit B: Corrections and Updates to the
Ms. Kathleen A. Dadey
HCPINCCP dated December 2006; (6) the Intra-Service Biological Opinion on Issuance of a
Section 1O(a)(l)(B) Incidental Take Permit for the HCPINCCP (Intra-Service Opinion) dated
July 2007;(7) the draft Aquatic Resources Inventory, Classification, and Function for the
HCPINCCP dated October 2004; (8) the East Contra Costa Habitat Conservation Plan/Natural
Community Conservation Plan Annual Report 2010 dated March 2011; and (9) and other
information available to the Service.
Consultation History:
June 14,2011:
June 22, 2011:
March 1,2012:
The Service received the Corps letter requesting initiation of formal
consultation for the proposed action.
The Service attended an informational workshop for the public hosted
by the East Contra Costa HCPINCCP with the Corps and the
California Department ofFish and Game (CDFG) to discuss the
proposed action.
The Service received a revised RGP.
BIOLOGICAL OPINION
Description of the proposed action
2
The HCPINCCP addresses effects to both federally listed and unlisted species. However,
pursuant to section 7 of the Act, this Biological Opinion only addresses effects to federally listed
or proposed threatened and endangered species resulting from the proposed issuance of a RGP
that would authorize placement of dredged or fill materials into waters of the U.S. for activities
covered under the HCPINCCP within the Plan Area for the HCPINCCP. For a complete
description of all Covered Activities (Covered Activities) under the HCPINCCP, see Chapter 2 of
the HCPINCCP (Jones and Stokes 2006).
The proposed RGP is valid for five years from the date of issuance (or reissuance), but can be
extended or reissued (see Terms of Authorization: Expiration of RGP below); however, the
HCPINCCP and Intra-Service Opinion cover activities for a period of thirty years (expires on
July 25.2037). Because activities proposed under the RGP are a subset of the Covered
Activities analyzed in the HCPINCCP and Intra-Service Opinion, the Service will consider this
Biological Opinion valid for the life of the HCPINCCP's Incidental Take Permit (TEI60958-0)
(Service 2007), unless new information reveals effects of the proposed action may result in
adverse effects to federally listed species in a manner not identified to date, or if a new species is
listed that may be affected by the proposed action.
Ms. Kathleen A. Dadey 3
Project Overview
The proposed action is issuance of a RGP that would authorize placement of dredged or fill material
into waters of the U.S. within the Plan Area, pursuant to section 404 of the Clean Water Act
(CWA), for Covered Activities as defined in the HCPINCCP that would have minimal individual
and cumulative impacts on the aquatic environment. The RGP's procedures and associated
requirements would integrate with those contained in the HCPINCCP, resulting in consistent
implementation of the section 10 permit for the HCPINCCP and a coordinated permitting process
under section 404 of the CW A.
The proposed RGP would authorize specific categories of activities with minimal individual and
cumulative impacts on the aquatic environment that meet the terms and conditions of the RGP.
Temporary structures, fills, and work necessary to construct an activity authorized by the RGP
are allowed, provided such work complies with the terms and conditions of the RGP inclusive of
special conditions that the Corps may add. The RGP applies only to HCPINCCP Covered
Activities, as set forth in Section 2.3 of the HCPINCCP (Jones and Stokes 2006). Any question
as to whether a proposed activity is considered a Covered Activity under the HCPINCCP shall be
subject to confirmation by the East Contra Costa County Habitat Conservancy, a joint exercise of
powers agency formed by the Cities of Brentwood, Clayton, Oakley and Pittsburg and Contra
Costa County to perform the role ofImplementing Entity for the HCPINCCP (Conservancy).
The HCPINCCP Covered Activities are divided among the following Activity categories in the
RGP for purposes of assigning Activity-specific conditions (see Activity Specific Conditions
below):
I. Residential, commercial, industrial, institutional, and other urban developments and
associated infrastructure inside the Urban Limit Line of Contra Costa County or
inside the City Limits of the Cities of Brentwood, Clayton, Oakley and Pittsburg,
including but not limited to roads, utilities, parks, storm water management facilities,
and water supply and delivery facilities (activity-specific conditions: 1 through 4).
2. Recreation projects, including parks, picnic areas, staging areas, trails and park
maintenance facilities. Applies only to the activities set forth in Sections 2.3.2 and
2.3.4 of the HCPINCCP (activity-specific conditions: 1 through 4).
3. Flood control detention basins, reservoirs, channels, and related facilities. Applies
only to the specific planned facilities set forth in Section 2.3.2 of the HCPINCCP
(activity-specific conditions: 1 through 4).
4. Transportation projects, including road construction and widening, bicycle trails, rail
projects, bridges and safety-related projects. Applies only to the specific planned
facilities set forth in Section 2.3.2 of the HCPINCCP (general conditions apply only).
Ms. Kathleen A. Dadey
5. Wetland and stream restoration, creation, enhancement and management. Applies
only to activities set forth in Sections 2.3.2 and 2.3.4 of the HCP/NCCP (activity-
specific conditions: 1, 2, and 4).
6. Utility projects, including electrical transmission projects, cellular communication
projects and pipelines. Applies only to the activities set forth in Sections 2.3.2 and
2.3.4 of the HCP/NCCP (activity-specific condition 4).
7. Maintenance, repair, rehabilitation or replacement of any previously authorized
(under the RGP or other Corps permit), currently serviceable, structure or fill.
Applies only to the maintenance activities set forth in Sections 2.3.1 and 2.3.3 of the
HCP/NCCP (general conditions apply only).
4
If there is any question as to which Activity category a proposed activity would apply to, the
Corps will determine the applicable Activity category. The RGP does not cover any activities in
waters of the U.S. conducted in emergency situations.
Terms of Authorization:
1. Applying for RGP authorization: Prior to commencing a proposed activity, applicants
seeking authorization under the RGP shall notify the Corps in accordance with RGP general
condition number 19 (Notification) listed in the general conditions below. If the Corps
determines that an activity is not an eligible activity under the RGP, it will notify the
applicant in writing within 30 calendar days and provide instructions on the procedures to
seek authorization under a standard permit, letter of permission or Nationwide permit. If the
Corps determines that a proposed activity is eligible for coverage under the RGP, it will
notifY the applicant within 45 calendar days of receipt of a complete application. If the
Corps does not provide a written response to the applicant within 45 calendar days following
receipt of a complete application, the applicant may presume the proposed activity is an
eligible activity that may be covered under the RGP, provided the activity complies with all
other terms and conditions of the RGP.
2. Impact Thresholds for waters of the U.S.: Impacts to waters of the U.S. shall be avoided and
minimized to the maximum extent practicable. The loss of waters of the U.S. (including
wetlands) resulting from individual project impacts may not exceed a total of 1.5 acres or
more than 300 linear feet of perennial, intermittent or 3rd or higher order ephemeral streams
(as defined in Table 2 of the RGP and further described in the HCP/NCCP), unless the linear
limit is waived in writing by the Corps. Additional restrictions are listed in the General and
Activity-Specific Conditions.
3. Single and complete project: The project must be a single and complete project. For
example, if construction of a residential development involves phases, the sum of all
impacted areas would be the basis for deciding whether or not the project will be covered by
the RGP.
Ms. Kathleen A. Dadey
4. After-the-fact projects: The RGP may not be used to authorize activities after they have
impacted waters ofthe U.S.
5
5. Compliance with HCPINCCP Conditions: Activities to be authorized under the RGP must
be HCPINCCP Covered Activities and must fully comply with the HCPINCCP. Compliance
with the HCPINCCP requires applicants to implement the appropriate conservation measures
outlined in Chapter 6 of the HCPINCCP.
6. Special conditions: The Corps may add special conditions to an authorization to ensure the
activity complies with the terms and conditions of the RGP, and/or that adverse impacts on
the aquatic environment or other aspects of the public interest are individually and
cumulatively minimal.
7. Activity completion: Any activity authorized by the Corps under the RGP must be
completed within three (3) years of the date it is authorized. The "authorization date" is the
date the Corps verifies in writing that the activity meets the terms and conditions of the RGP.
The Corps will, on a case-by-case basis, review requests for time extensions if the permittee
fails to complete the activity within three years. A time extension would be considered a
reverification and would be subject to review and approval policies in effect at the time of
review. Pursuant to term #9, below, activities authorized under the RGP that are under
construction or under contract for construction in reliance upon this authorization will remain
authorized provided the activity is completed within 12 months of the date of the RGP's
expiration, modification or revocation, unless the Corps exercises its discretionary authority
to modify, suspend, or revoke the authorization of a specific project.
8. Discretionary Authority: The Corps has the discretion to suspend, modify, or revoke
authorizations under the RGP. This discretionary authority may be used by the Corps to also
further condition or restrict the applicability of the RGP for cases in which it has concerns
associated with the Clean Water Act Section 404(b)(I) Guidelines, or regarding any public
interest factor. Should the Corps determine that a proposed activity may have more than
minimal individual or cumulative adverse impacts to aquatic resources or otherwise be
contrary to the public interest, the Corps will modify the authorization to reduce or eliminate
those adverse effects, or notifY the applicant that the proposed activity is not authorized by
the RGP and provide instructions on how to seek authorization under an individual permit.
The Corps may restore authorization under the RGP at any time it determines that the reason
for asserting discretionary authority has been resolved or satisfied by a condition, project
modification, or new information. The Corps may also use its discretionary authority to
modifY, suspend, or revoke the RGP at any time.
9. Expiration ofRGP: The RGP is valid for five years from the date of issuance (or reissuance).
At least 60 calendar days prior to the expiration date of the RGP, the Corps will issue a
public notice, with an opportunity for public comment, describing the reasons for reissuing
the RGP, reissuing the RGP with modifications, or not reissuing the RGP for another five
years. The Corps may extend the RGP for six months beyond the expiration date if it is
Ms. Kathleen A. Dadey 6
unable to reissue the RGP due to unresolved issues. If the Corps has not reissued or extended
the RGP by the expiration date, the RGP will no longer be valid. The RGP may also be
modified, suspended, or revoked by the Corps at any time deemed necessary. In such
instance, the Corps will issue a public notice concerning the action.
General Conditions:
The following conditions apply to all Activity categories:
1. Threatened and Endangered Species: No activity is authorized under the RGP that does not
comply with the mandatory terms and conditions of the Service's Section 10(a)(1)(B)
Incidental Take Permit for the East Contra Costa HCPINCCP dated July 20, 2007 (Service
permit number: TE160958-0). This Biological Opinion contains mandatory terms and
conditions to implement the reasonable and prudent measures that are associated with
"incidental take" authorization under the RGP. Authorization under the RGP is conditional
upon compliance with all of the mandatory terms and conditions of this Biological Opinion.
Failure to comply with the terms and conditions of this Biological Opinion would constitute
non-compliance with the RGP. The Service is the appropriate authority to determine
compliance with the terms and conditions of the Biological Opinion, and with the ESA. The
permittee must comply with all applicable conditions of this Biological Opinion, including
those ascribed to the Corps.
2. Water Quality Certification: Section 401 Water Quality Certification is required for
activities to be authorized by the RGP. The Corps may require additional water quality
management measures to ensure that the authorized activity does not result in more than
minimal impacts, individually or cumulatively.
3. Historic Properties: No activity is authorized under the RGP if the activity may affect
historic properties listed, or eligible for listing, in the National Register of Historic Places,
until the requirements of Section 106 of the National Historic Preservation Act (NHPA), as
amended, have been satisfied. Applicants must notifY the Corps if the activity may have the
potential to cause effects to any historic properties listed, determined to be eligible for listing
on, or potentially eligible for listing on the National Register of Historic Places, including
previously unidentified historic properties. The Corps will consult with the State Historic
Preservation Officer (SHPO), as appropriate, following the policy and procedural standards
of33 CFR Part 325 Appendix ct.
4. Unanticipated Cultural Resources Discoveries: If previously unidentified cultural materials
are unearthed during construction, all work shall be halted until a qualified archaeologist can
examine the deposit and determine its nature and significance. In the event of discovery of
possible human remains, state law requires that the County Coroner be contacted.
1 Inclusive of Appendix C Interim Guidance dated April 25, 2005 and January 31, 2007, or such guidance that is applicable at the
time that a pennit application is submitted. Current guidance may be found on the Sacramento District's web site at:
http://www.spk.usace.army.mil/organizations/cespk-co/regulatory/.
Ms. Kathleen A. Dadey
5. Fills within 100-Year Floodplains: The activity must comply with applicable FEMA-
approved state or local floodplain management requirements.
7
6. Bed and Bank Stabilization: Bank stabilization activities are limited to: (a) using the
minimum amount of material needed for erosion protection; (b) no more than 500 feet in
length along the bank, unless this criterion is waived in writing by the Corps; and (c) no more
than an average of 1 cubic yard of material per running foot placed along the bank below the
plane of the ordinary high water mark or high tide line, unless this criterion is waived in
writing by the Corps.
7. Best Management Practices: Best Management Practices (BMPs) must be employed during
construction and in project design to protect water quality and minimize impacts of
stormwater runoff on aquatic resources. BMPs should be appropriately located in or adjacent
to waters of the U.S. (e.g., silt curtains). The applicant shall employ the following BMPs, as
appropriate and feasible, in designing and constructing the project. The applicant shall
describe which BMPs are practicable as part of the notification procedure as per general
condition #19, subpart (b) below:
a. Preservation of natural resource features on the project site (e.g., floodplains, wetlands,
streams, and other drainage ways, grasslands, woodlands, and native soils);
b. Preservation of natural water infiltration and storage characteristics of the site;
c. Minimization of new impervious surfaces in project design (impervious surfaces may be
minimized through practices such as reducing road widths and clustering developments
designed around open space);
d. Structural measures that provide water quality and quantity control;
e. Structural measures that provide only quantity control and conveyance;
f. Construction BMPs;
g. Low impact development (LID) BMPs.
Examples of structural BMPs include: vegetated natural buffers, grassed swales, infiltration
trenches, level spreaders and chaunel grade controls. Examples of construction BMPs
include: matting and filter fencing, or other barrier methods to intercept/capture sediment.
8. Proper Maintenance: Any authorized structure or fill shall be properly maintained, including
maintenance necessary to ensure public safety and the movement of aquatic organisms.
9. Aquatic Life Movements: No activity may substantially disrupt the necessary life cycle
movement of aquatic species indigenous to the water body, including those species that
normally migrate through the area, unless the activity'S primary purpose is to impound water.
Culverts placed in streams must be installed to maintain low-flow conditions. Iffeasible,
they should be designed as open-bottom culverts.
Ms. Kathleen A. Dadey
10. Equipment: Heavy equipment working in wetlaods must be placed on mats, or other
measures, such as low-ground pressure equipment, must be taken to minimize soil
disturbaoce.
11. Tribal Rights: No activity or its operation may impair reserved tribal rights, including, but
not limited to, reserved water rights aod treaty fishing and hunting rights.
8
12. Water Supply Intakes: No discharge of dredged or fill material may occur in the proximity of
a public water supply intake, except where the discharge is for the repair or improvement of
the intake stmcture(s), aod/or adjacent bank stabilization.
13. Suitable Material: No discharge of dredged or fill material may consist of unsuitable material
aod material discharged must be free from toxic pollutaots in toxic amounts (section 307 of
the CWA). Unsuitable material includes, but is not limited to, trash, debris, car bodies, aod
asphalt.
14. Maoagement of Water Flows: To the maximum extent practicable, the pre-constmction
course, condition, capacity, aod location of open waters must be maintained. The activity
must be constmcted to withstaod expected high flows. The activity must not restrict or
impede the passage of normal or high flows, unless the primary purpose of the activity is to
impound water or maoage high flows. The activity may alter the pre-constmction course,
condition, capacity, and location of open waters ifit benefits the aquatic environment (e.g.,
stream restoration project).
15. Migratory Bird Breeding Areas: Activities in waters of the U.S. that serve as breeding areas
for migratory birds shall be avoided to the maximum extent practicable.
16. Removal of Temporary Fills aod Restoration of Affected Areas: Temporary fills shall be
removed in their entirety aod the affected areas returned to pre-constmction elevations. The
affected areas shall be revegetated with native vegetation upon completion of the project. A
restoration plan, which includes a I-foot contour topographic map, must be submitted with
the notification to the Corps.
17. Compensatory Mitigation: Mitigation for impacts to waters of the U.S. must be accomplished
by conforming to the minimum mitigation ratios set by the HCP/NCCP. Mitigation
proposals are required to be consistent with the Corps' mitigation mle (33 CFR Part 332).
a. Mitigation may be accomplished by one or more of the following mechanisms: I)
payment of the aquatic resources mitigation fee to the Conservaocy in accordaoce with
the in-lieu fee (ILF) program envisioned to be established by the Conservaocy; 2)
purchasing credits from a Corps-approved mitigation bank that also provides mitigation
acceptable under the HCP/NCCP, aod/or; 3) through a "permittee-responsible" mitigation
project (33 CFR Part 332).
Ms. Kathleen A. Dadey
b. Prior to proceeding with the activity authorized by the RGP, a final mitigation plan must
be approved by the Corps and the Conservancy, and/or mitigation fees must be paid.
When mitigation fees are applicable, evidence of fee payment must be provided to the
Corps before commencement of the activity authorized by the RGP can be initiated.
c. If the RGP verification includes permittee-responsible compensatory mitigation, the
mitigation plan must contain a reporting procedure consistent with the Corps' mitigation
rule (33 CFR Part 332.4[c] [1 OJ), Monitoring Requirements.
9
18. Notification: The applicant shall provide written notification (i.e., a complete application) for
a proposed activity to be authorized under the RGP prior to commencing the activity. The
Corps' receipt of the complete application is the date when the Corps receives all required
notification information from the applicant (see below). Written notification shall include all
of the following:
a. A letter signed by the applicant requesting authorization under the RGP, identifying the
Activity Category(s), a description of the proposed activity, the location of the activity
(with latitude and longitude), and the area (in acres, and/or linear feet as applicable) of
waters of the U.S., including wetlands, to be impacted;
b. For each general and applicable activity-specific condition ofthe RGP, a brief narrative
describing how the activity would comply with the condition, or that the condition does
not apply;
c. Vicinity and project site maps;
d. A delineation of waters of the U.S., including wetlands, for the project site and for areas
immediately adjacent to the project site. On-site wetlands must be delineated using the
Corps Wetlands Delineation Manual (1987) and Arid West Region Regional Supplement
(2008), or most recent manual(s) in effect at the time of the applicant's proposal. Off-site
wetlands may be identified through the use of reference materials including local wetland
inventories, soil surveys, and aerial photography. The delineation shall also include
information on wetlands and waters, as defined in the HCPINCCP, that are/may not be
waters of the U.S.;
e. Preliminary plans (on 8 \1," x 11" or 14" reduced-sized drawings) showing all aspects of
the proposed activity and the location of avoided and impacted waters of the U.S. Plan-
view and cross-section plans shall be included. Both temporary (e.g., access, staging)
and permanent impacts to waters ofthe U.S. shall be shown. The plans shall include
grading contours and existing and proposed structures, such as buildings, roadways,
stormwater management facilities, utilities, construction access areas and water
conveyance structures. The drawings shall also show buffer areas, open space
designations, locations of BMPs, deed restricted areas, and restoration areas, if required;
f. A written statement explaining how the activity has been designed to avoid and minimize
adverse effects, both temporary and permanent, to waters of the U.S. For compensatory
mitigation proposed in accordance with general condition #18, submit a preliminary plan
to offset unavoidable impacts to waters of the U.S.;
Ms. Kathleen A. Dadey
g. A cultural resource survey report for the project site, including all staging, access and
construction areas. The report must be prepared in accordance with the Sacramento
District's Guidelines for Compliance with Section 106 of the NHP A (dated
February 25, 20 11), or more recent guidance (if applicable) at the time a permit
application is submitted.
10
If the Corps determines that the activity complies with the terms and conditions of the RGP,
including confirmation that proposed impacts to aquatic resources are minimal, the Corps
will notify the applicant in writing and include any special conditions deemed necessary. If
the Corps determines the impacts of the proposed activity are more than minimal, the Corps
will notifY the applicant that the project does not qualifY for authorization under the RGP and
instruct the applicant on the procedures to seek authorization under an individual permit.
19. Reporting Responsibilities: The permittee must submit a report to the Corps within 30 days
of project completion. The report will contain the following:
a. The Corps' file number;
b. Photographs showing pre-and post-construction project conditions;
c. A completed compliance certification.
20. Access: The permittee must allow representatives from the Corps to inspect the authorized
activity at any time deemed necessary to ensure that it is being or has been accomplished in
accordance with the terms and conditions of the permit.
21. Transfer ofRGP Authorization: If the permittee sells the property associated with this permit,
the permittee must obtain the signature and mailing address of the new owner on the permit
verification letter, and forward a copy to this office to validate the transfer.
Activity-Specific Conditions:
The following conditions apply to Activity categories specified at the end of each condition.
1. Stream Setbacks. Consistent with the requirements of the HCPINCCP, stream setbacks
shall be established (see the HCPINCCP for detailed stream setback requirements). Waters
of the U.S. shall not be filled in order to meet the buffer requirements (Activity categories I,
2,3, and 5).
2. Permanent Protections. All preserved, created, restored or enhanced waters of the U.S. and
adjacent buffers on the project site shall be preserved and permanently protected through a
deed restriction, conservation easement, or other appropriate real estate or legal instrument,
consistent with the requirements of the HCPINCCP as determined by the Corps. A recorded
copy of the real estate instrument must be provided to the Corps prior to proceeding with
any activity otherwise authorized by the RGP (Activity categories 1,2,3, and 5).
Ms. Kathleen A. Dadey
3. Fencing and Signage. Preserved areas on the project site must be fenced and signed as
sensitive areas to discourage human disturbance (Activity categories 1,2, and 3).
4. Utility Lines. All utility lines shall be constructed in accordance with the following;
11
a. The construction area for linear utility line projects shall be limited to a width 005 feet,
unless this limit is waived in writing by the Corps.
b. For utility line projects, directional drilling, clear span or other techniques that do not
contact the waterbody shall be used if the waterbody contains perennial flow.
c. If the project involves the use of directional drilling below waters, notification shall
include a contingency plan. The plan will include actions that will be taken to stabilize
the work area and avoidance/contingency measures in the event of a potential "frac-out."
d. Material resulting from trench excavation may be temporarily sidecast (up to 60 days)
into waters of the U.S., provided that the material is not placed in such a manner that it is
dispersed by currents or other forces. The Corps may extend the period of temporary side
casting for no more than a total of 180 days, where appropriate.
e. Utility lines must not adversely alter existing hydrology, including draining of wetlands.
In wetland areas, utility line trenches shall be lined with clay, or other impermeable
materials or structures (such as cut-off walls) to ensure that the trench through which the
utility line is installed does not drain waters ofthe U.S. In addition, to prevent a French
drain effect, gravel cannot be used as backfill material in the top 10 feet of the trench.
f. In wetland areas, the top 6"-12" of the trench shall be backfilled with topsoil excavated
from the trench in the same stratification in which it was removed.
g. Excess material shall be removed to upland areas immediately upon completion of utility
line construction in any segment of the project containing waters of the U.S. In no case
shall the excess material be left in place until the entire utility line is completed.
h. The construction area, including unprotected slopes and streambanks, shall be stabilized
(e.g., blanketed and seeded) immediately upon completion of the utility line construction
in any segment of the project. In no case shall soil stabilization be delayed until the
entire utility line is completed.
1. Temporarily disturbed construction areas must be restored to pre-construction conditions,
including grading to original contours and revegetating (with native vegetation or other
appropriate vegetation approved by the Corps) immediately upon completion of the
project. A restoration plan, which includes a I-foot contour topographic map, shall be
submitted with notification (Activity categories 1,2,3,5, and 6).
Limitations and Restrictions:
1. The Corps has authority to determine if an activity complies with the terms and conditions
of the RGP.
2. The RGP does not obviate the need to obtain other Federal, state, or local permits,
approvals, or authorizations required by law.
3. The RGP does not grant any property rights or exclusive privileges.
Ms. Kathleen A. Dadey 12
4. The RGP does not authorize any injury to the property or rights of others.
5. The RGP does not authorize interference with any existing or proposed Federal project.
Definitions:
This Biological Opinion incorporates by reference the Definitions contained within the RGP.
Action Area
The area covered by the RGP is geographically synonymous with the Plan Area for the
HCPINCCP in east Contra Costa County, including the cities of Clayton, Brentwood, Oakley,
and Pittsburg, and specific areas of unincorporated Contra Costa County. The HCPINCCP
action area is within eastern Contra Costa County, California. The action area covers 174,018
acres, or approximately one-third of Contra Costa County, and is entirely within the eastern
portion of the County. The action area is approximately bounded on the south by the Alameda-
Contra Costa County line; on the east by the westernmost Delta sloughs between Oakley and the
Alameda-Contra Costa County line; on the north by the San Joaquin River shoreline; and on the
southwest and west by the western edges of the watersheds of Kellogg and Marsh Creeks, the
Mount Diablo Meridian, and the Clayton sphere of influence.
The action area encompasses all or most of five incorporated cities: Brentwood, Clayton,
Oakley, Pittsburg, and Antioch; however, Antioch is not a Permittee to the HCPINCCP. Three-
quarters of the land in the action area, approximately 128,908 acres, are in unincorporated areas
of Contra Costa County. For a more detailed description of the action area refer to the Intra-
Service Opinion.
Analytical Framework for the Jeopardy Analysis
Jeopardy Determination
In accordance with policy and regulation, the jeopardy analysis in this Biological Opinion relies
on three components: (1) the Status of the Species, which evaluates the California red-legged
frog, Central California tiger salamander, Alameda whipsnake, giant garter snake, San Joaquin
kit fox, vernal pool fairy shrimp, longhorn fairy shrimp, and vernal pool tadpole shrimp, the
factors responsible for that condition, and their survival and recovery needs; (2) the
Environmental Baseline and evaluates the condition of these listed species in the action area, the
factors responsible for that condition, and the relationship ofthe action area to the survival and
recovery of these listed species; (3) the Effects of the Action, which determines the direct and
indirect effects of the proposed Federal action and the effects of any interrelated or
interdependent activities on these species; and (4) Cumulative Effects, which evaluates the
effects of future, non-Federal activities in the action area on them.
Ms. Kathleen A. Dadey 13
In accordance with policy and regulation, the jeopardy determination is made by evaluating the
effects of the proposed Federal action in the context of the California red-legged frog, Central
California tiger salamander, Alameda whipsnake, giant garter snake, San Joaquin kit fox, vernal
pool fairy shrimp, longhorn fairy shrimp, and vernal pool tadpole shrimp's current status, taking
into account any cumulative effects, to determine if implementation of the proposed action is
likely to cause an appreciable reduction in the likelihood of both the survival and recovery of
these listed species in the wild.
The jeopardy analysis in this Biological Opinion places an emphasis on consideration of the
range-wide survival and recovery needs of these listed species, and the role of the action area in
the survival and recovery of these listed species as the context for evaluating the significance of
the effects of the proposed Federal action, taken together with cumulative effects, for purposes of
making the jeopardy determination.
Adverse Modification Determination
This Biological Opinion does not rely on the regulatory definition of "destruction or adverse
modification" of critical habitat at 50 CFR 402.02. Instead, we have relied upon the statutory
provisions of the ESA to complete the following analysis with respect to critical habitat.
In accordance with policy and regulation, the adverse modification analysis in this Biological
Opinion relies on four components: (1) the Status of Critical Habitat, which evaluates the range
wide condition of designated critical habitat for vernal pool tadpole shrimp and longhorn fairy
shrimp in terms of primary constituent elements (PCEs), the factors responsible for that
condition, and the intended recovery function of the critical habitat at the provincial and range-
wide scale; (2) the Environmental Baseline, which evaluates the condition of the critical habitat
in the action area, the factors responsible for that condition, and the recovery role of the critical
habitat in the action area; (3) the Effects of the Action, which determines the direct and indirect
impacts of the proposed Federal action and the effects of any interrelated or interdependent
activities on the PCEs and how that will influence the recovery role of affected critical habitat
units; and (4) Cumulative Effects which evaluates the effects offuture, non-Federal activities in
the action area on the PCEs and how that will influence the recovery role of affected critical
habitat units.
For purposes of the adverse modification determination, the effects of the proposed Federal
action on vernal pool fairy shrimp and longhorn fairy shrimp critical habitat are evaluated in the
context of the range-wide condition of the critical habitat at the provincial and range-wide scales,
taking into account any cumulative effects, to determine if the critical habitat range-wide would
remain functional( or would retain the current ability for the PCEs to be functionally established
in areas of currently unsuitable but capable habitat) to serve its intended recovery role for the
vernal pool fairy shrimp and longhorn fairy shrimp.
Ms. Kathleen A. Dadey 14
The analysis in this Biological Opinion places an emphasis on using the intended range-wide
recovery function of vernal pool fairy shrimp and longhorn fairy shrimp critical habitat and the
role of the action area relative to that intended function as the context for evaluating the
significance of the effects of the proposed Federal action, taken together with cumulative effects,
for purposes of making the adverse modification determination.
Status ofthe Species
California red-leggedfrog
Listing Status: The California red-legged frog was listed as a threatened species on
May 23, 1996 (Service 1996). Critical habitat was designated for this species on April 13,2006
(Service 2006) and revisions to the critical habitat designation were published on
March 17,2010 (Service 2010). At this time, the Service recognized the taxonomic change from
Rana aurora draytonii to Rana draytonii (Shaffer et al. 2010). A recovery plan was published
for the California red-legged frog on September 1 2, 2002 (Service 2002a).
Status of the Species: In a study of California red-legged frog terrestrial activity in a xeric
environment in eastern Contra Costa County, Tatarian (2008) noted that a 57 percent majority of
frogs fitted with radio transmitters in the Round Valley study area stayed at their breeding pools,
whereas 43 percent moved into adjacent upland habitat or to other aquatic sites. Her study
reported a peak seasonal terrestrial movement occurring in the fall months associated with the
first 0.2-inch of precipitation and tapering off into spring. Upland movement activities ranged
from 3 to 233 feet, averaging 80 feet, and were associated with a variety of refugia including
grass thatch, crevices, cow hoof prints, ground squirrel burrows at the base of trees or rocks,
logs, and under man-made structures; others were associated with upland sites lacking refugia
(Tatarian 2008). The majority of terrestrial movements lasted from 1 to 4 days; however, one
adult female was reported to remain in upland habitat for 50 days (Tatarian 2008). Upland
refugia closer to aquatic sites were used more often and were more commonly associated with
areas exhibiting higher object cover, e.g., woody debris, rocks, and vegetative cover.
Subterranean cover was not significantly different between occupied upland habitat and non-
occupied upland habitat.
With the exception of the information provided above, the Service has determined that the Status
of the Species is substantively unchanged from the time the Service issued its Intra-Service
Opinion for the HCPINCCP. Therefore, the Service is incorporating by reference the Status of
the Species from that opinion. For additional information regarding the Status of the Species,
including description, distribution, status and natural history, and threats, refer to the Intra-
Service Opinion for the HCPINCCP.
Central California Tiger Salamander
Listing Status: The Service proposed to list the Central California tiger salamander as threatened
on May 23, 2003. At this time reclassification of the Santa Barbara County and Sonoma County
Ms. Kathleen A. Dadey 15
DPSs from endangered to threatened was also proposed (Service 2003). In the same notice the
Service also proposed a special rule under section 4( d) of the Act to exempt take for routine
ranching operations for the Central DPS and, if reclassified to threatened, for the Santa Barbara
and Sonoma County DPSs (Service 2003). On August 4, 2004, after determining that the listed
Central DPS was threatened (Service 2004), the Service determined that the Santa Barbara and
Sonoma County DPSs were threatened as well, and reclassified the California tiger salamander
as threatened throughout its range, removing the Santa Barbara and Sonoma County populations
as separately listed DPSs (Service 2004). In this notice we also finalized the special rule to
exempt take for routine ranching operations for the California tiger salamander throughout its
range (Service 2004).
On August 18, 2005, as a result of litigation of the August 4, 2004, final rule on the
reclassification of the California tiger salamander DPSs (Center for Biological Diversity et al. v.
United States Fish and Wildlife Service et al., C 04-04324 WHA (N.D. Cal. 2005), the District
Court of Northern California sustained the portion of the 2004 rule pertaining to listing the
Central California tiger salamander as threatened with a special rule, vacated the 2004 rule with
regard to the Santa Barbara and Sonoma DPSs, and reinstated their prior listing as endangered.
The List of Endangered and Threatened Wildlife in part 17, subchapter B of Chapter I, title 50 of
the Code of Federal Regulations (CFR) has not been amended to reflect the vacatures contained
in this order, and continues to show the range-wide reclassification of the California tiger
salamander as a threatened species with a special rule. We are currently in the process of
correcting the CFR to reflect the current status of the species throughout its range. The
California tiger salamander was listed by the State of California as a threatened species on
May20,2010.
Status of the Species: Thirty-one percent (221 of711 records and occurrences) of all Central
California tiger salamander records and occurrences are located in Alameda, Santa Clara, San
Benito (excluding the extreme western end of the County), southwestern San Joaquin, western
Stanislaus, western Merced, and southeastern San Mateo counties. Of these counties, most of the
records are from eastern Alameda and Santa Clara counties (CDFG 2010; Service 2004). The
CDFG (2010) now considers 13 of these records from the Bay Area region as extirpated or likely
to be extirpated.
Of the 140 reported California tiger salamander localities where wetland habitat was identified,
only 7 percent were located in vernal pools (CDFG 2010). The Bay Area is located within the
Central Coast and Livermore vernal pool regions (Keeler-Wolf et al. 1998). Vernal pools within
the Coast Range are more sporadically distributed than vernal pools in the Central Valley
(Holland 2003). This rate ofloss suggests that vernal pools in these counties are disappearing
faster than previously reported (Holland 2003). Most ofthe vernal pools in the Livermore
Region in Alameda County have been destroyed or degraded by urban development, agriculture,
water diversions, poor water quality, and long-term overgrazing (Keeler-Wolf et al. 1998).
During the 1980s and 1990s, vernal pools were lost at a 1.1 percent annual rate in Alameda
County (Holland 1998).
Ms. Kathleen A. Dadey 16
Due to the extensive losses of vernal pool complexes and their limited distribution in the Bay
Area region, many breeding sites consist of artificial water bodies. Overall, 89 percent (124) of
the identified water bodies are stock, farm, or berm ponds used by cattle grazing and/or as a
temporary water source for small farm irrigation (CDFG 2010). This places tbe California tiger
salamander at great risk of hybridization witb non-native tiger salamanders, especially in Santa
Clara and San Benito counties. Witbout long-term maintenance, the longevity of artificial
breeding habitats is uncertain relative to naturally occurring vernal pools that are dependent on
the continuation of seasonal weather patterns (Shaffer et al. 2004). California tiger salamanders
are now primarily restricted to artificial breeding ponds, such as bermed ponds or stock ponds,
which are typically located at higher elevations (CDFG 2010).
With tbe exception of tbe information provided above, the Service has determined that the Status
of the Species is substantively unchanlled from the time the Service issued its Intra-Service
Opinion for the HCP/NCCP. Therefore, the Service is incorporating by reference the Status of
the Species from that opinion. For additional information regarding the Status of the Species,
including description, distribution, status and natural history, and threats, refer to the Intra-
Service Opinion for the HCP/NCCP.
Alameda whipsnake
Listing Status: The Alameda whipsnake was federally listed as threatened on
December 5, 1997 (Service 1997). Approximately 406,598 acres within Contra Costa, Alameda,
Santa Clara, and San Joaquin counties were designated critical habitat for the Alameda
whipsnake on October 3, 2000 (Service 2000). The final rule was vacated and remanded on
May 9, 2003. Critical habitat was re-proposed on October 18, 2005 (Service 2005b). A final
rule on critical habitat was released on October 2, 2006 (Service 2006a). A draft recovery plan
was published in November 2002 (Service 2002b).
Status of the Species: The Alameda whipsnake is known to inhabit chemise-redshank chaparral,
mixed chaparral, coastal scrub, annual grassland, blue oak-foothill pine, blue oak woodland,
coastal oak woodland, valley oak woodland, eucalyptus, redwood, and riparian communities
(Mayer and Laudenslayer, Jr. 1988). Grassland and oak woodland habitat independent of
chaparral habitat may also be important for Alameda whipsnake populations. A recent
examination of recorded whipsnake observations revealed tbat the species has been found 32
percent of the time in grass-or woodland habitats on slopes of varying aspects (Alvarez 2006).
Additional data on habitat use gathered from incidental observations of free-ranging Alameda
whipsnakes and recapture data from trapping surveys showed regular use of these habitats at
distances greater than 600 feet from scrub and chaparral and included observations of tbe species
more than 3.7 miles from scrub and chaparral communities (Swaim pers. comm. 2004).
With the exception of the information provided above, tbe Service has determined that the Status
of the Species is substantively unchanged from the time the Service issued its Intra-Service
Opinion for the HCP/NCCP. Therefore, tbe Service is incorporating by reference tbe Status of
the Species from that opinion. For additional information regarding tbe Status oftbe Species,
Ms. Kathleen A. Dadey
including description, distribution, status and natural history, and threats, refer to the Intra-
Service Opinion for the HCPINCCP.
Giant garter snake
Listing Status: The giant garter snake was listed as a threatened species on October 20, 1993
(Service 1993). The Service published the Draft Recovery Plan for the Giant Garter Snake in
July 1999.
17
Status of the Species: With the exception ofthe infonnation provided above, the Service has
detennined that the Status of the Species is substantively unchanged from the time the Service
issued its Intra-Service Opinion for the HCPINCCP. Therefore, the Service is incorporating by
reference the Status of the Species from that opinion. For additional information regarding the
Status of the Species, including description, distribution, status and natural history, and threats,
refer to the Intra-Service Opinion for the HCPINCCP.
San Joaquin Kit Fox
Listing Status: The San Joaquin kit fox was listed as an endangered species on March 11, 1967
(Service 1967) and it was listed by the State of California as a threatened species on
June 27, 1971.
Status of the Species: The status of the San Joaquin kit fox population in Contra Costa County is
not well documented, but the infrequency of confirmed sightings suggest their density is low or
their occurrence could be periodic (Jones and Stokes 2006). Maintaining a cormection to core
San Joaquin kit fox populations in the San Joaquin Valley is likely critical to supporting a viable
kit fox population in Contra Costa Cormty. The HCPINCCP aims to protect land in the Plan
Area in order to protect San Joaquin kit fox habitat and to provide linkages to areas to the south
and east. Currently, the HCPINCCP has acquired numerous parcels to the east of Los Vaqueros
Reservoir area and in the vicinity of Black Diamond Mines Regional Preserve that are to be
incorporated into the preserve system of the HCPINCCP.
With the exception of the information provided above, the Service had detennined that the Status
of the Species is substantively unchanged from the time the Service issued its Intra-Service
Opinion for the HCPINCCP. Therefore, the Service is incorporating by reference the Status of
the Species from that opinion. For additional infonnation regarding the Status ofthe Species,
including description, distribution, status and natural history, and threats, refer to the Intra-
Service Opinion for the HCPINCCP.
Vernal Pool Fairy Shrimp
Listing Status: A final rule was published on September 19, 1994, listing the vernal pool fairy
shrimp as threatened under the Act (Service 1994). The final rule to designate critical habitat for
15 vernal pool species, including the vernal pool fairy shrimp, was published on August 6, 2003
(Service 2003). A final rule was published again on August 11,2005 (Service 2005a). Further
Ms. Kathleen A. Dadey 18
information on the life history and ecology of the vernal pool fairy shrimp may be found in the
final listing rule, the final rule to designate critical habitat, the Recovery Plan for Vernal Pool
Ecosystems of California and Southern Oregon (Service 2005c), Eng et al. (1990), Helm (1998),
Simovich et al. (1992), and Volmar (2002).
Status of the Species: With the exception of the information provided above, the Service has
determined that the Status of the Species is substantively unchanged from the time the Service
issued its Intra-Service Opinion for the HCPINCCP. Therefore, the Service is incorporating by
reference the Status of the Species from that opinion. For additional information regarding the
Status of the Species, including description, distribution, status and natural history, and threats,
refer to the Intra-Service Opinion for the HCPINCCP.
Longhorn Fairy Shrimp
Listing Status: A final rule was published on September 19, 1994, to list longhorn fairy shrimp
as endangered under the Act (Service 1994). The final rule to designate critical habitat for 15
vernal pool species, including the longhorn fairy shrimp, was published on August 6, 2003
(Service 2003). A final rule was published again on August 11,2005 (Service 2005a). Further
information on the life history and ecology of the longhorn fairy shrimp may be found in the
final listing rule, the final rule to designate critical habitat, the Recovery Plan for Vernal Pool
Ecosystems of California and Southern Oregon (Service 2005b), and Eng et al. (1990).
Status of the Species: Since the time of listing, surveys for longhorn fairy shrimp throughout its
range have not located additional populations of the species, although additional occurrences
within the four known populations have been detected. Currently, the California Natural
Diversity Database reports 11 occurrences oflonghorn fairy shrimp (CDFG 2010).
Informal monitoring of known populations of longhorn fairy shrimp has occurred within the
Brushy Peak Preserve, Alameda County. There are several vernal pools that have longhorn fairy
shrimp within the 507-acre Brushy Peak Preserve, which is owned by the Livermore Area
Recreation and Park District and managed by the East Bay Regional Park District (EBRPD).
These pools are within rock outcrops within mUltiple indentations that seasonally pool water, but
the exact number of vema I pools containing longhorn fairy shrimp has not been quantified.
With the exception ofthe information provided above, the Service has determined that the Status
of the Species is substantively unchanged from the time the Service issued its Intra-Service
Opinion for the HCPINCCP. Therefore, the Service is incorporating by reference the Status of
the Species from that opinion. For additional information regarding the Status of the Species,
including description, distribution, status and natural history, and threats, refer to the Intra-
Service Opinion for the HCPINCCP.
Ms. Kathleen A. Dadey
Vernal Pool Tadpole Shrimp
Listing Status: A final rule was published on September 19, 1994, to list vernal pool tadpole
shrimp as endangered under the Act (Service 1994). The final rule to designate critical habitat
for 15 vernal pool species, including the vernal pool tadpole shrimp, was published on
August 6, 2003 (Service 2003). A final rule was published again on August 11, 2005 (Service
2005a). Further information on the life history and ecology of the vernal pool tadpole shrimp
may be found in the final listing rule, the final rule to designate critical habitat, the Recovery
Plan/or Vernal Pool Ecosystems o/California and Southern Oregon (Service 2005b), and Eng
et al. (1990).
19
Status of the Species: The vernal pool tadpole shrimp is a California Great Central Valley
endemic species, with the majority of the populations occurring in the Sacramento Valley. This
species has also been reported from the Sacramento River Delta to the east side of San Francisco
Bay, and from a few scattered localities in the San Joaquin Valley from San Joaquin County to
Madera County (Rodgers 2001). Currently, the CNDDB lists 270 occurrences of vernal pool
tadpole shrimp with one occurrence in Contra Costa County within the city limits of Antioch
along Empire Mine Road (CDFG 2011). Currently the city of Antioch is not a permittee under
the HCPINCCP nor are any activities within the Antioch city limits covered by the HCPINCCP.
With the exception of the information provided above, the Service has determined that the Status
of the Species is substantively unchanged from the time the Service issued its Intra-Service
Opinion for the HCPINCCP. Therefore, the Service is incorporating by reference the Status of
the Species from that opinion. For additional information regarding the Status of the Species,
including description, distribution, status and natural history, and threats, refer to the Intra-
Service Opinion for the HCPINCCP.
Vernal Pool Fairy Shrimp and Longhorn Fairy Shrimp Critical Habitat
The Service designated 228,785 acres of critical habitat for the vernal pool fairy shrimp and
13,557 acres of critical habitat for the longhorn fairy shrimp in 2005 (Service 2005a). In a
February 10, 2006, revision, we identified the designated critical habitat on a species by unit
basis (Service 2006). In determining which areas to designate as critical habitat, the Service
considers those physical and biological features (primary constituent elements) that are essential
to the conservation of the species, and that may require special management considerations and
protections (50 CFR § 424.14).
The primary constituent elements of critical habitat for both vernal pool fairy shrimp and
longhorn fairy shrimp are the habitat components that provide:(I) topographic features
characterized by mounds and swales and depressions within a matrix of surrounding uplands that
result in complexes of continuously, or intermittently, flowing surface water in the swales
connecting the pools and providing for dispersal and promoting hydroperiods of adequate length
in the pools; (2) depressional features including isolated vernal pools with underlying restrictive
soil layers that become inundated during winter rains and that continuously hold water for a
Ms. Kathleen A. Dadey 20
minimum of 23 days in all but the driest years; thereby providing adequate water for incubation,
maturation, and reproduction. As these features are inundated on a seasonal basis, they do not
promote the development of obligate wetland vegetation habitats typical of permanently flooded
emergent wetlands; (3) sources offood, expected to be detritus occurring in the pools,
contributed by overland flow from the pools' watershed, or the results of biological processes
within the pools themselves, such as single-celled bacteria, algae, and dead organic matter, to
provide for feeding; and (4) structure within the pools consisting of organic and inorganic
materials, such as living and dead plants from plant species adapted to seasonally inundated
environments, rocks, and other inorganic debris that may be washed, blown, or otherwise
transported into the pools, that provide shelter.
Environmental Baseline
All Species
As of the 2010 annual report for the HCPINCCP, 61.4 acres of terrestrial impacts, 0.61 acres of
aquatic (non-stream) impacts, and 138.3 linear feet of aquatic (stream) impacts have been
authorized under the HCPINCCP. In addition, 4,475.7 acres of terrestrial habitat, 36.9 acres of
aquatic (non-stream) habitat, and 116,569.2 linear feet of aquatic (stream) habitat have been
conserved under the HCPINCCP, which support numerous occurrences of the Covered Species.
California Red-legged frog
The proposed action is located in the East San Francisco Bay Core Area of the East San
Francisco Bay Recovery Unit number 16 for the California red-legged frog (Service 2002a).
California red-legged frogs have been documented throughout the 18,500-acre Los Vaqueros
Watershed (Watershed) and stock ponds in the Watershed support some of the highest densities
of California red-legged frog in the region (Jones and Stokes Associates 2006). The CNDDB
reports 96 California red-legged frog occurrences in and near the Watershed (CDFG 2010).
The HCPINCCP provides a regional conservation strategy that includes the development and
acquisition of a preserve system. A completed preserve system will encompass 23,800 to 30,300
acres of land in eastern Contra Costa County and will include connections linking existing and
future protected private and public lands.
There are 127 occurrences of the California red-legged frog within the action area in the
CNDDB (CDFG 2011). A few additional occurrences of the California red-legged frog have
been documented within the action area and some additional take of the species has occurred
since the HCPINCCP was permitted. The current expansion of the Los Vaqueros Reservoir will
result in the inundation of 451.27 acres of upland habitat and two ponds and four marshes that
support California red-legged; however, the Service believes that the Environmental Baseline for
this species is not substantively different from that described in the Service's Intra-Service
Opinion for the HCPINCCP. Therefore, the Service is incorporating by reference the
Environmental Baseline from that opinion. For additional information regarding the
Ms. Kathleen A. Dadey 21
Environmental Baseline for the California red-legged frog, refer to the Intra-Service Opinion for
the HCP/NCCP.
Central California tiger salamander
The CNDDB describes over 150 occurrences of the Central California tiger salamanders in
Contra Costa County with the majority of these records from the vicinity of the Los Vaqueros
Watershed (CDFG 2010). A few additional occurrences of the Central California tiger
salamander have been documented within the action area and some additional take of the species
has occurred since the HCP/NCCP was permitted. The current expansion of the Los Vaqueros
Reservoir will result in the inundation of 451.27 acres of upland habitat and one pond and one
marsh known to support breeding populations of the Central California tiger salamander;
however, the Service believes that the Environmental Baseline for this species is not
substantively different from that described in the Service's Intra-Service Opinion for the
HCP/NCCP. Therefore, the Service is incorporating by reference the Environmental Baseline
from that opinion. For additional information regarding the Environmental Baseline for the
Central California tiger salamander, refer to the Intra-Service Opinion for the HCP/NCCP.
Alameda whipsnake
There are 22 occurrences of the Alameda whipsnake within the action area in the CNDDB
(CDFG 20 II). The Service believes that the Environmental Baseline for this species is not
substantively different from that described in the Service's Intra-Service Opinion for the
HCP/NCCP. Therefore, the Service is incorporating by reference the Environmental Baseline
from that opinion. For additional information regarding the Environmental Baseline for the
Alameda whipsnake, refer to the Intra-Service Opinion for the HCP/NCCP.
Giant garter snake
There are no records of the giant garter snake within the actio!} area in the CNDDB (CDFG
2011). The Service believes that the Environmental Baseline for this species is not substantively
different from that described in the Service's Intra-Service Opinion for the HCP/NCCP.
Therefore, the Service is incorporating by reference the Environmental Baseline from that
opinion. For additional information regarding the Environmental Baseline for the giant garter
snake refer to the Intra-Service Opinion for the HCP/NCCP.
San Joaquin Kit Fox
The Bureau of Reclamation recently completed formal consultation on the Contra Costa Water
District's (CCWD) proposed expansion of the Los Vaqueros Reservoir (Reservoir Expansion)
(Service file number 81420-2009-F-0201-1). The Reservoir Expansion will result in permanent
impacts to 410.21 acres of annual grasslands and 29.34 acres of oak woodland. The expanded
reservoir will also raise the waterline into three sections of oak woodland habitat to the west of
the existing reservoir isolating two large grassland areas (totaling 284.76 acres) from
Ms. Kathleen A. Dadey 22
surrounding grasslands likely rendering these areas inaccessible to San Joaquin kit fox. In
addition, a grassland corridor to the west of the reservoir will be interrupted by approximately
700 feet of oak woodland at each of three locations making it unlikely that San Joaquin kit fox
will use the remaining area to the west of the expanded reservoir following reservoir expansion.
Loss of this corridor will compromise the southern branch of the Round Valley corridor to Black
Diamond Mines Regional Preserve.
In order to compensate for temporary and permanent effects to San Joaquin kit fox from loss of
habitat from the Reservoir Expansion, the CCWD will acquire and preserve, in perpetuity, a
minimum of 4,890 acres. This includes additional lands preserved to those impacted in order to
account for the loss of habitat, movement corridors, and habitat connectivity for San Joaquin kit
fox within the northern portion of their range, and for the loss of San Joaquin kit fox
conservation easement lands. The compensation is expected to preserve existing movement
corridors within the northern San Joaquin kit fox range and currently includes one large under
crossing ofthe 1-580 corridor in Alameda County.
San Joaquin kit fox sightings have been documented within and surrounding the action area
(CDFG 2010, CCWD 2010). Documented sightings within and near the action area include:
multiple sightings between 1967 and 1989 along Brushy Creek east of Vasco Road (CDFG
2010); two San Joaquin kit fox sightings along the proposed Vasco Road alignment in 1989
(Jones and Stokes 1990); two records from May 2001 and June 2002 on Vasco Caves Regional
Preserve (Clark et al. 2003); and two sightings near Brushy Creek in 2002 (CDFG 2010).
CCWD has performed annual kit fox surveys throughout the Los Vaqueros Watershed since
constructing the reservoir in 1998. During this period a single San Joaquin kit fox was observed
in 2008 in close proximity to the Los Vaqueros Watershed Administrative Offices northeast of
the reservoir (Howard 2008).
Grasslands throughout the action area provide suitable San Joaquin kit fox habitat. Because San
Joaquin kit foxes can use native habitats interspersed with development if there is minimal
disturbance, adequate dispersal corridors, and sufficient prey-base the HCPINCCP considers
grassland habitat within wind turbine areas suitable for kit fox use. Threats within the action
area include the loss, fragmentation, and degradation of habitat through urban, rural, agricultural,
and wind development. Although the use of pesticides to control rodents and other pests is
restricted on CCWD and HCPINCCP preserve lands, use of pesticides on private land within the
action area may pose a threat to kit fox on private lands either directly through poisoning or
indirectly through reduction of prey abundance. In addition, coyotes, cited as a significant
source of San Joaquin kit fox mortality, are thought to have increased in number on the Los
Vaqueros Watershed since reservoir filling in 1998 (CCWD 2011).
Longhorn Fairy Shrimp
There are two known occurrences oflonghorn fairy shrimp within the action area in the CNDDB
(CDFG 2011). The Service believes that the Environmental Baseline for this species is not
substantively different from that described in the Service's Intra-Service Opinion for the
HCPINCCP. Therefore, the Service is incorporating by reference the Environmental Baseline
Ms. Kathleen A. Dadey
from that opinion. For additional information regarding the Environmental Baseline for the
longhorn fairy shrimp, refer to the Intra-Service Opinion for the HCP/NCCP.
Vernal Pool Fairy Shrimp
23
There are thirteen known occurrence of vernal pool fairy shrimp within the action area in the
CNDDB (CDFG 2011). The Service believes that the Environmental Baseline for this species is
not substantively different from that described in the Service's Intra-Service Opinion for the
HCP/NCCP. Therefore, the Service is incorporating by reference the Environmental Baseline
from that opinion. For additional information regarding the Environmental Baseline for the
vernal pool fairy shrimp, refer to the Intra-Service Opinion for the HCP/NCCP.
Vernal Pool Tadpole Shrimp
There are no known occurrences of vernal pool tadpole shrimp within the action area in the
CNDDB (CDFG 2011). The Service believes that the Environmental Baseline for this species is
not substantively different from that described in the Service's Intra-Service Opinion for the
HCP/NCCP. Therefore, the Service is incorporating by reference the Environmental Baseline
from that opinion. For additional information regarding the Environmental Baseline for the
vernal pool tadpole shrimp, refer to the Intra-Service Opinion for the HCP/NCCP.
Vernal Pool Fairy Shrimp and Longhorn Fairy Shrimp Critical Habitat
Critical Habitat Unit 19 for vernal pool fairy shrimp includes three subunits; Units 19A-B are
located in Contra Costa County. Unit 19C is located in Alameda County. Units 19A and 19B
fall within the Plan Area. Unit 19A lies just north of Marsh Creek Road and Unit 19B lies north
of Corral Hollow Road, west of Clifton Court Forebay (Service 2005a). Unit 19C is outside the
action area. Units 19A-B include approximately 6,439 acres (Service 2005a). These units are
essential to the conservation of the species because they support nearly all of the known
occurrences of vernal pool fairy shrimp within Contra Costa and Alameda Counties and because
they are necessary to maintain the current geographic and ecological distribution of the species.
Critical Habitat Unit 1 for longhorn fairy shrimp includes two subunits referred to as the
Altamont Pass Subunits; Unit IA is located in Contra Costa County and Unit IB in Alameda
County. Within the Altamont Pass subunits longhorn fairy shrimp occur within clear depression
pools in sandstone outcrops (Service 2005a). Unit lA falls within the Plan Area primarily within
the Vasco Caves Regional Preserve. Unit IB is outside the action area. Units IA-B include
approximately 791 acres (Service 2005a). These units are essential to the conservation of the
species because they support nearly all of the known occurrences of longhorn fairy shrimp within
Contra Costa and Alameda Counties and because they are necessary to maintain the current
geographic and ecological distribution of the species.
Ms. Kathleen A. Dadey 24
Effects of the Proposed Action
California Red-legged frog and Central California Tiger Salamander
The proposed action will result in temporary and permanent effects to aquatic and upland habitat
for California red-legged frog and Central California tiger salamander. This could result in
individuals being directly and/or indirectly injured or killed by activities that disturb breeding,
feeding, sheltering, and dispersal habitat. The effects of activities covered by the RGP were
analyzed in the Intra-Service Opinion for the HCPINCCP, including minimization and mitigation
measures for both species. No additional effects or effects different from those analyzed in the
Intra-Service Opinion for the HCPINCCP are expected. Therefore, the Service is incorporating
by reference the Effects of the Proposed Action from that opinion. For additional information
regarding the Effects of the Proposed Action on California red-legged frogs and the Central
California tiger salamander, refer to the Intra-Service Opinion for the HCPINCCP.
Alameda Whipsnake
The proposed action will result in temporary and permanent effects to habitat suitable for
Alameda whipsnake resulting in direct and indirect effects to the species. The effects of
activities covered by the RGP were analyzed in the Intra-Service Opinion for the HCPINCCP,
including minimization and mitigation measures. No additional effects or effects different from
those analyzed in the Intra-Service Opinion for the HCPINCCP are expected. Therefore, the
Service is incorporating by reference the Effects of the Proposed Action from that opinion. For
additional information regarding the Effects of the Proposed Action on Alameda whipsnakes,
refer to the Intra-Service Opinion for the HCPINCCP.
Giant Garter Snake
The proposed action will result in temporary and permanent effects to habitat suitable for giant
garter snake resulting in direct and indirect effects to the species. The effects of activities
covered by the RGP were analyzed in the Intra-Service Opinion for the HCPINCCP, including
minimization and mitigation measures. No additional effects or effects different from those
analyzed in the Intra-Service Opinion for the HCPINCCP are expected. Therefore, the Service is
incorporating by reference the Effects of the Proposed Action from that opinion. For additional
information regarding the Effects of the Proposed Action on giant garter snakes, refer to the
Intra-Service Opinion for the HCPINCCP.
San Joaquin Kit Fox
The proposed action will result in temporary and permanent effects to annual grassland habitat
suitable for San Joaquin kit fox denning, foraging, or dispersal resulting in direct and indirect
effects to the species. The effects of activities covered by the RGP were analyzed in the Intra-
Service Opinion for the HCPINCCP, including minimization and mitigation measures. No
additional effects or effects different from those analyzed in the Intra-Service Opinion for the
Ms. Kathleen A. Dadey 25
HCPINCCP are expected. Therefore, the Service is incorporating by reference the Effects of the
Proposed Action from that opinion. For additional information regarding the Effects of the
Proposed Action on San Joaquin kit foxes, refer to the Intra-Service Opinion for the HCPINCCP.
Vernal Pool Fairy Shrimp, Longhorn Fairy Shrimp, and Vernal Pool Tadpole Shrimp
Direct and indirect effects to vernal pool fairy shrimp, longhorn fairy shrimp, and tadpole shrimp
will result from activities covered by the proposed RGP. The effects of activities covered by the
RGP were analyzed in the Intra-Service Opinion for the HCPINCCP, including minimization and
mitigation measures for both species. No additional effects or effects different from those
analyzed in the Intra-Service Opinion for the HCPINCCP are expected. Therefore, the Service is
incorporating by reference the Effects of the Proposed Action from that opinion. For additional
information regarding the Effects of the Proposed Action on vernal pool fairy shrimp and
longhorn fairy shrimp, refer to the Intra-Service Opinion for the HCPINCCP.
Vernal Pool Fairy Shrimp Critical Habitat
Critical habitat for vernal pool fairy shrimp is found within the action area. Effects to vernal
pool fairy shrimp critical habitat will result from activities covered by the proposed RGP. The
effects of activities covered by the RGP were analyzed in the Intra-Service Opinion for the
HCPINCCP, including minimization and mitigation measures. No additional effects or effects
different from those analyzed in the Intra-Service Opinion for the HCPINCCP are expected.
Therefore, the Service is incorporating by reference the Effects of the Proposed Action from that
opinion. For additional information regarding the Effects of the Proposed Action on vernal pool
fairy shrimp critical habitat, refer to the Intra-Service Opinion for the HCPINCCP.
Longhorn Fairy Shrimp Critical Habitat
Critical habitat for longhorn fairy shrimp is found within the action area. Effects to longhorn
fairy shrimp critical habitat will result from activities covered by the proposed RGP. The effects
of activities covered by the RGP were analyzed in the Intra-Service Opinion for the HCPINCCP,
including minimization and mitigation measures. No additional effects or effects different from
those analyzed in the Intra-Service Opinion for the HCPINCCP are expected. Therefore, the
Service is incorporating by reference the Effects of the Proposed Action from that opinion. For
additional information regarding the Effects of the Proposed Action on longhorn fairy shrimp
critical habitat, refer to the Intra-Service Opinion for the HCPINCCP.
Cumulative Effects
Cumulative effects include the effects of future State, Tribal, local or private actions that are
reasonably certain to occur in the action area considered in this Biological Opinion. Future
Federal actions that are unrelated to the proposed action are not considered in this section
because they require separate consultation pursuant to section 7 of the Act.
Ms. Kathleen A. Dadey 26
The Service is aware of numerous non-federal actions currently planned in the vicinity of the
proposed action, defined here as eastern Contra Costa County. Enviroumental analysis is either
underway or completed for many of these projects. These projects include such actions as urban
expansion, road improvement projects, water transfers and developments, and continued
agricultural development. The cumulative effects of these known actions pose a significant
threat to the eventual recovery of all listed species in this area. However, many of these
activities will be reviewed under section 7 of the Act as a result of the Federal nexus provided by
section 404 of the Federal Water Pollution Control Act, as amended (Clean Water Act).
Additionally, many of these activities are included as Covered Activities for the HCPINCCP and
effects resulting from these activities are being mitigated for under the HCPINCCP.
Urban expansion in eastern Contra Costa and Alameda counties and western San Joaquin County
will further fragment and isolate populations of California red-legged frogs, California tiger
salamanders, and San Joaquin kit fox from other nearby populations. Urban expansion is
accompanied by increased traffic resulting in increased wildlife injury and mortality from vehicle
strikes. A 2009 wildlife movement study conducted along a 2.S-mile stretch of Vasco Road
adjacent to the action area documented substantial wildlife mortality from vehicle strikes
including 50 California tiger salamanders and 120 California red-legged frogs over a IS month
period (Mendelsohn et al. 2009). Continued development and maintenance of roadways and
water projects to serve expanding urban areas are also likely to further fragment and isolate
populations of these species. In addition, urban expansion is generally accompanied by
increased predation associated with domesticated pets or feral animals that negatively affect
populations of these species.
The global average temperature has risen by approximately 0.6 degrees Celsius during the 20th
Century (IPPC 2001, 2007; Adger et al. 2007). There is an international scientific consensus that
most of the warming observed has been caused by human activities (IPPC 2001, 2007; Adger et
al. 2007), and that it is "very likely" that it is largely due to manmade emissions of carbon
dioxide and other greenhouse gases (Adger et at. 2007). Ongoing climate change (Anonymous
2007; Inkley et al. 2004; Adger et al. 2007; Kanter 2007) likely imperils several listed species
including the California red-legged frog, Central California tiger salamander, Alameda
whipsnake, giant garter snake, San Joaquin kit fox, vernal pool fairy shrimp, longhorn fairy
shrimp, and vernal pool tadpole shrimp and the resources necessary for their survival. Since
climate change threatens to disrupt armual weather patterns, it may result in a loss of their
habitats and/or food sources, and/or increased numbers of their predators, parasites, and diseases.
Where populations are isolated, a changing climate may result in local extinction, with range
shifts precluded by lack of habitat.
Conclusion
After reviewing the current status of the California red-legged frog, Central California tiger
salamander, Alameda whipsnake, giant garter snake, San Joaquin kit fox, vernal pool fairy
shrimp, longhorn fairy shrimp, and vernal pool tadpole shrimp, the environmental baseline for
the action area, the effects of the proposed action, and the cumulative effects, it is the Service's
Ms. Kathleen A. Dadey 27
biological opinion that the RGP that would be used to authorize placement of dredged or fill
material into waters of the U.S. for multiple actions considered to be Covered Activities under
the East Contra Costa Habitat Conservation PlanlNatural Community Conservation Plan, as
proposed, is not likely to jeopardize the continued existence of the California red-legged frog,
Central California tiger salamander, Alameda whipsnake, giant garter snake, San Joaquin kit fox,
vernal pool fairy shrimp, longhorn fairy shrimp, or vernal pool tadpole shrimp. We base this
conclusion on the following: (J) some project effects are temporary in nature;(2) the proposed
action does not include effects to listed species that were not analyzed in the Intra-Service
Opinion for the HCPINCCP; and (3) establishment of a 23,800 to 30,300 acres preserve system
in eastern Contra Costa County to preserve and manage habitat for listed species in perpetuity.
The project is located within critical habitat for the vernal pool fairy shrimp and longhorn fairy
shrimp; however the proposed action will not result in its adverse modification or destruction.
We based this conclusion on the following: (1) only a small percentage of critical habitat for
vernal pool fairy shrimp and longhorn fairy shrimp would be affected by the proposed action; (2)
the PCEs that are essential to the conservation value of vernal pool fairy shrimp and longhorn
fairy shrimp critical habitat will remain and continue to contribute to the conservation function of
the unit as a whole; and (3) range-wide critical habitat for vernal pool fairy shrimp and longhorn
fairy shrimp would remain functional.
INCIDENTAL TAKE STATEMENT
Section 9(a)(J) of the Act and Federal regulations pursuant to section 4(d) of the Act prohibit the
take of endangered and threatened species without special exemption. Take is defined as harass,
harm, pursue, hunt, shoot, wound, kill, trap, capture or collect, or attempt to engage in any such
conduct. Harm is further defined by the Service to include significant habitat modification or
degradation that results in death or injury to listed species by significantly impairing behavioral
patterns, including breeding, feeding, or sheltering. Harass is defined by the Service as actions
that create the likelihood of injury to a listed species by annoying it to such an extent as to
significantly disrupt normal behavior patterns which include, but are not limited to, breeding,
feeding, or sheltering. Incidental take is defined as take that is incidental to, and not the purpose
of, the carrying out of an otherwise lawful activity. Under the terms of section 7(b)( 4) and
section 7(0)(2), taking that is incidental to and not intended as part ofthe agency action is not
considered to be prohibited taking under the Act provided that such taking is in compliance with
this Incidental Take Statement.
The measures described below are nondiscretionary, and must be implemented by the Corps so
that they become binding conditions of any grant or permit issued to the applicant, as
appropriate, for the exemption under section 7(0)(2) to apply. The Corps has a continuing duty
to regulate the activity that is covered by this incidental take statement. If the Corps (l) fails to
require the applicant, or any of its contractors to adhere to the terms and conditions of the
incidental take statement through enforceable terms, and/or (2) fails to retain oversight to ensure
compliance with these terms and conditions, the protective coverage of section 7(0)(2) may
lapse.
Ms. Kathleen A. Dadey 28
Amount or Extent of Take
All Listed Species
The amount of incidental take exempted from the prohibitions described under section 9 of the
Act through this Biological Opinion is a subset of the incidental take authorized under the
HCPINCCP. Take associated with activities carried out under the HCPINCCP has been
authorized under a section IO(a)(l)(B) permit; however, incidental take associated with actions
authorized, funded, or carried out by Federal Agencies cannot be authorized under section 10 of
the Act.
The extent of the take will be difficult to detect or quantifY because of the ecology and biology of
these species. Additionally, their size and cryptic nature makes the finding of a dead specimen
unlikely. Seasonal population fluctuations may also make losses of these species difficult to
quantifY. Due to the difficulty in quantifying the number of California red-legged frog, Central
California tiger salamander, Alameda whipsnake, giant garter snake, San Joaquin kit fox, vernal
pool fairy shrimp, longhorn fairy shrimp, or vernal pool tadpole shrimp that will be taken as a
result of the proposed action, the Service is quantifYing take incidental to the proposed project as
the number of acres of habitat that will become unsuitable for the species as a result of the
action.
The exact subset of incidental take expected in conjunction with the RGP cannot be specifically
segregated from the amount of take authorized under the HCPINCCP, therefore, the Service is
only authorizing the same amount of incidental take associated with the HCPINCCP (Le., the
take is not in addition to that associated with the HCPINCCP). The Service estimates that
incidental take of California red-legged frog, Central California tiger salamander, San Joaquin kit
fox, giant garter snake, Alameda whipsnake, vernal pool fairy shrimp, longhorn fairy shrimp, and
vernal pool tadpole shrimp associated with loss of up to 13,387 acres of habitat will be affected.
Upon implementation of the Reasonable and Prudent Measures, incidental take of California red-
legged frog, Central California tiger salamander, San Joaquin kit fox, giant garter snake,
Alameda whipsnake, vernal pool fairy shrimp, longhorn fairy shrimp, and vernal pool tadpole
shrimp associated with the Corps' proposed RGP will become exempt from the prohibitions
described under section 9 of the Act.
Effect of the Take
In the accompanying biological opinion and the Intra-Service Opinion for the HCP/NCCP, the
Service has determined that this level of anticipated take is not likely to result in jeopardy to the
California red-legged frog, Central California tiger salamander, San Joaquin kit fox, giant garter
snake, Alameda whipsnake, vernal pool fairy shrimp, longhorn fairy shrimp, and vernal pool
tadpole shrimp
Ms. Kathleen A. Dadey 29
Reasonable and Prudent Measures
The Service believes the following reasonable and prudent measure is necessary and appropriate
to minimize the effect of take on the Central California tiger salamander, San Joaquin kit fox,
giant garter snake, Alameda whipsnake, vernal pool fairy shrimp, longhorn fairy shrimp, and
vernal pool tadpole shrimp:
I. The proposed action will be implemented by the project proponent as described in the
Description of the Proposed Action and the East Contra Costa Habitat Conservation
PlaniNatural Communities Conservation Plan and further, conservation measures shall be
supplemented by terms and conditions (a) through (e).
Terms and Conditions
To be exempt from the prohibitions of Section 9 of the Act, the Corps shall ensure compliance
with the following terms and conditions, which implement the reasonable and prudent measure
described above. These terms and conditions are nondiscretionary.
The following terms and conditions will implement the Reasonable and Prudent Measure
described above:
a. The applicant shall minimize the potential for harm, harassment, injury, and death of
federally listed wildlife species resulting from project related activities including
implementation ofthe Conservation Measures in this Biological Opinion.
b. The applicant shall adhere to all of the conservation and management measures of the
HCP/NCCP and the Terms and Conditions of its Incidental Take Permit (TEl 60958-0).
c. All activities authorized by the Corps under this RGP must occur while the HCP/NCCP's
Incidental Take Permit (TE160958-0) is valid.
d. If the Corps determines that the activity complies with the terms and conditions of the
RGP, including confirmation that proposed impacts to aquatic resources are minimal,
written notification will be provided to the Conservancy, the Service, and CDFG
consistent with the reporting requirements of the HCP/NCCP; this confirmation will be
identified in the Corps' section 7 initiation letter to the Service for individual project
applications under the RGP.
e. The permittee must allow representatives from the Conservancy, Service and CDFG to
inspect the authorized activity at any time deemed necessary to ensure that it is being or
has been accomplished in accordance with East Contra Costa HCP/NCCP and the Terms
and Conditions of its Incidental Take Permit (TE160958-0).
Ms. Kathleen A. Dadey 30
f. All preserved, created, restored or enhanced waters of the U.S. and adjacent buffers on
the project site shall be preserved and permanently protected consistent with the
requirements of the East Contra Costa HCPINCCP and subject to review and approval by
the Service and CDFG.
Reporting Requirements
The Service is incorporating by reference the reporting requirements ofthe East Contra Costa
HCPINCCP and its associated permit and Terms and Conditions (TE160958-0).
CONSERVATION RECOMMENDATIONS
Section 7(a)(I) of the Act directs Federal agencies to utilize their authorities to further the
purposes of the Act by carrying out conservation programs for the benefit of endangered and
threatened species. Conservation recommendations are discretionary agency activities that can
be implemented to further the purposes of the Act, such as preservation of endangered species
habitat, implementation of recovery actions, or development of information and data bases.
The Service requests notification of the implementation of any conservation recommendations in
order to be kept informed of actions minimizing or avoiding adverse effects or benefiting listed
species or their habitats. No voluntary conservation recommendations are needed or proposed
for the proposed action. .
RENITIATION -CLOSING STATEMENT
This concludes formal consultation on the proposed issuance of a RGP for the East Contra Costa
Habitat Conservation PlanlNatural Community Conservation Plan in Contra Costa County,
California. As provided in 50 CFR 402.16, reinitiating of formal consultation is required where
discretionary Federal agency involvement or control over the action has been retained (or is
authorized by law) and if: (I) the amount or extent of incidental take is exceeded; (2) new
information reveals effects of the agency action that may affect listed species or critical habitat in
a manner or to an extent not considered in this opinion; (3) the agency action is subsequently
modified in a manner that causes an effect to the listed species or critical habitat that was not
considered in this Biological Opinion; or (4) a new species is listed or critical habitat designated
that may be affected by the action. In instances where the amount or extent of incidental take is
exceeded, any operations causing such take must immediately cease, pending reinitiating.
Ms. Kathleen A. Dadey
If you have any questions regarding this Biological Opinion on the proposed issuance of a
Regional General Permit for the East Contra Costa Habitat Conservation PlanlNatural
Community Conservation Plan in Contra Costa County, California, please contact Stephanie
Jentsch, Mike Thomas, or Eric Tattersall (Deputy Assistant Field Supervisor) of my staff at the
letterhead address or at telephone (916) 414-6600.
cc:
Sincerely,
Susan K. Moore
Field Supervisor
Scott Wilson, California Department of Fish and Game, Yountville, California.
John Kopchik, Contra Costa County, Martinez, California.
31
Ms. Kathleen A. Dadey 32
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(CCWD) Contra Costa Water District. 2010. Draft Los Vaqueros Reservoir Expansion Project
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__ 20 II. Draft Los Vaqueros Watershed 20 I 0 Annual Monitoring Report for California
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a 1996 Conference. California Native Plant Society, Sacramento, California.
Ms. Kathleen A. Dadey 33
Holland, R. F. 1998. No net loss? Changes in Great Valley vernal pool distribution from 1989
to 1997. Prepared for California Department of Fish and Game Natural Heritage
Division. Sacramento, California. 16pp.
__ . 2003. Distribution of vernal pool habitats in five counties of California's southern coast
range. California Department of Fish and Game, Sacramento, California. 23 pp.
Howard 2008. Personal account of San Joaquin kit fox sighting in the Los Vaqueros Watershed
on September 6, 2008. Email sent from J. Howard to M. Mueller, Los Vaqueros.
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J. Gregory, G. Heger!, M. Heimann, B. Hewitson, B. Hoskins, F. Joos, J. Jouzel, V.
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Qin, G. Raga, V. Ramaswamy, J. Ren, M. Rusticucci, S. Solomon, R. Somerville, T.F.
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http://www.ipcc.chl.
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Vaqueros project in and adjacent to Kellogg Creek Watershed. Prepared for the Contra
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__ 2006. Final East Contra Costa habitat conservation plan/natural communities
conservation plan. Prepared for the East Contra Costa Habitat Conservation Plan
Authority, October 2007;
Kanter, J. 2007. Scientists detail climate changes, Poles to Tropics. New York Times. April 10,
2007.
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Preliminary Report. State of California, Resources Agencies, Department of Fish and
Game, California.
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study report. Prepared for Contra Costa County Public Works Department, Martinez.
34
Rogers, D. C. 2001. Revision of the North American Lepidurus (Notostraca: Crustacea) with a
description of a new species previously confused with two other species. Journal of
Crustacean Biology 24(4): 991-1006.
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of Endangerment: Cryptic Variation and Historic Phylogeography of the California Tiger
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inland California environment. Herpetological Conservation and Biology 3(2):155-169.
(Service) U. S. Fish and Wildlife Service.1967. Native Fish and Wildlife, Endangered Species.
Federal Register 32: 4001.
__ 1993. Endangered and threatened wildlife and plants; determination of threatened status
for the giant garter snake. Federal Register 58:54053-54066.
__ 1994. Endangered and threatened wildlife and plants; determination of endangered status
for the Conservancy fairy shrimp, longhorn fairy shrimp, and the vernal pool tadpole
shrimp, and threatened status for the vernal pool fairy shrimp. Federal Register
59:48136-48153
__ 1996. Endangered and threatened wildlife and plants; determination of threatened status
for the California Red-Legged Frog. Federal Register 61 :25813-25833.
__ 1997. Endangered and threatened wildlife and plants; determination of endangered status
for the callippe silverspot butterfly and the Behren's silverspot butterfly and threatened
status for the Alameda whipsnake. Federal Register 62(234):64306-64320.
Ms. Kathleen A. Dadey 35
__ 2000. Endangered and threatened wildlife and plants; final determination of critical
habitat for the Alameda whipsnake (Masticophis lateralis euryxanthus). Federal Register
65: 58933-58962.
__ 2002a. Recovery plan for the California red-legged frog (Rana aurora draytonii).
Portland, Oregon. 173 pages.
__ 2002b. Draft Recovery Plan for Chaparral and Scrub Community Species East of San
Francisco Bay, California. Region 1, Portland, Oregon. xvi + 306 pages.
__ 2003. Endangered and Threatened Wildlife and Plants: Final Designation of Critical
Habitat for Four Vernal Pool Crustaceans and Eleven Vernal Pool Plants in California
and Southern Oregon; Final Rule. Federal Register68:46684-46762.
__ 2004. Endangered and Threatened Wildlife and Plants; Determination of Threatened
Status for the California Tiger Salamander; and Special Rule Exemption for Existing
Routine Ranching Activities; Final Rule. Federal Register 69: 47212-47248.
__ 2005a. Endangered and threatened wildlife and plants; final designation of critical
habitat for four vernal pool crustaceans and eleven vernal pool plants in California and
Southern Oregon; Evaluation of Economic Exclusions From August 2003 Final
Designation; Final Rule. Federal Register 70:46924-46999.
__ 2005b. Endangered and Threatened Wildlife and Plants; Proposed Designation of
Critical Habitat for the Alameda Whipsnake, Proposed Rule. Federal Register 70: 60607-
60656.
__ 2005c. Recovery Plan for Vernal Pool Ecosystems of California and Southern Oregon.
Portland, Oregon. xxvi + 606 pages.
__ 2006a. Endangered and threatened wildlife and plants; designation of critical habitat for
the California red-legged frog (Rana aurora draytonii), and special rule exemption
associated with final listing for existing routine ranching activities; final rule. Federal
Register 71(71):19244-19346. April 13 .
. __ 2006b. Endangered and Threatened Wildlife and Plants; Designation of Critical Habitat
for the Alameda Whipsnake, final rule. Federal Register 71 :58176-58231.
__ 2007. Federal Fish and Wildlife Permit: TEI60958-0. July 25, 2007.
__ 2010. Endangered and threatened wildlife and plants; revised critical habitat for the
California red-legged frog (Rana aurora draytonii); final rule. Federal Register
75(56):1286-12959.
Ms. Kathleen A. Dadey 36
Volmar, lE. 2002. Wildlife and rare plant ecology of eastern Merced County's vernal pool
grasslands. Merced, Calfiornia.
Personal Communication
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message to Don Hankins (Service). November 29,2004.