South Bay Salt Pond Restoration Project, Phase 2; Don Edwards National Wildlife Refuge, California; Record of Decision for Final Environmental Impact Statement/Environmental Impact Report, 53075-53077 [2018-22763]
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Federal Register / Vol. 83, No. 203 / Friday, October 19, 2018 / Notices
comment on the permit application,
which includes the proposed habitat
conservation plan, as well as on our
preliminary determination that the plan
qualifies as low-effect under the
National Environmental Policy Act. To
make this determination, we used our
environmental action statement and
low-effect screening form, which are
also available for review.
DATES: To ensure consideration, please
send your written comments by
November 19, 2018.
ADDRESSES: If you wish to review the
application, including the HCP, as well
as our environmental action statement
or low-effect screening form, you may
request the documents by email, phone,
or U.S. mail. These documents are also
available for public inspection by
appointment during normal business
hours at the office below. Send your
comments or requests by any one of the
following methods.
Email: northflorida@fws.gov. Use
‘‘Attn: TE98747C–0.’’
Fax: Field Supervisor, (904) 731–
3191, ‘‘Attn: TE98747C–0.’’
U.S. mail: Field Supervisor,
Jacksonville Ecological Services Field
Office, Attn: TE69161C–0, U.S. Fish and
Wildlife Service, 7915 Baymeadows
Way, Suite 200, Jacksonville, FL 32256.
In-person drop-off: You may drop off
information during regular business
hours at the above office address.
FOR FURTHER INFORMATION CONTACT: Erin
M. Gawera, telephone: (904) 731–3121;
email: erin_gawera@fws.gov.
SUPPLEMENTARY INFORMATION: We, the
Fish and Wildlife Service (Service),
have received an application for an
incidental take permit (ITP) under the
Endangered Species Act of 1973, as
amended (ESA; 16 U.S.C. 1531 et seq.).
McDonald Ventures XXXVIII, LLC
(applicant) is requesting a 5-year ITP to
take sand skink (Neoseps reynoldsi)
incidental to the conversion of
approximately 0.25 acres of occupied
sand skink foraging and sheltering
habitat for construction of a commercial
development. The 9.37-acre project site
is located on parcel Number Parcel ID
numbers 42226000200000400,
42226000200000500,
42226000200000700,
42226000200000800, and
42226000200000900, within Section 34,
Township 22 South, Range 26 East in
Lake County, Florida. The project
includes the clearing, infrastructure
building, and landscaping associated
with construction. The applicant
proposes to mitigate for the take of the
threatened sand skink by purchasing
0.50 mitigation credits within the Lake
Wales Ridge Conservation Bank or
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another Service-approved sand skink
conservation bank.
Our Preliminary Determination
We have determined that the
Applicant’s proposal, including the
proposed mitigation and minimization
measures, would have minor or
negligible effects on the species covered
in the HCP. Therefore, we have
determined that the incidental take
permit for this project would be ‘‘low
effect’’ and qualify for categorical
exclusion under the National
Environmental Policy Act (NEPA). A
low-effect HCP is one involving (1)
minor or negligible effects on federally
listed or candidate species and their
habitats, and (2) minor or negligible
effects on other environmental values or
resources.
Public Availability of Comments
Before including your address, phone
number, email address, or other
personal identifying information in your
comment, be aware that your entire
comment—including your personal
identifying information—may be made
publicly available at any time. While
you may request in your comment that
we withhold your personal identifying
information, we cannot guarantee that
we will be able to do so.
Next Steps
We will evaluate the HCP and
comments we receive to determine
whether the ITP application meets the
permit issuance requirements of section
10(a) of the ESA. We will also conduct
an intra-Service consultation pursuant
to section 7 of the ESA. If the
requirements for permit issuance are
met, we will issue ITP number
TE98747C–0 to the Applicant for
incidental take of the sand skink.
Authority
We provide this notice under section
10 of the Endangered Species Act of
1973, as amended (ESA; 16 U.S.C. 1531
et seq.) and the ESA’s regulations, the
National Environmental Policy Act
(NEPA; 42 U.S.C. 4321 et seq.) and
NEPA regulations (40 CFR 1506.6).
Jay B. Herrington,
Field Supervisor, Jacksonville Field Office,
Southeast Region.
[FR Doc. 2018–22749 Filed 10–18–18; 8:45 am]
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DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
[FWS–R8–NWRS–2018–N130;
FXRS282108E8PD0–190–F2013227943]
South Bay Salt Pond Restoration
Project, Phase 2; Don Edwards
National Wildlife Refuge, California;
Record of Decision for Final
Environmental Impact Statement/
Environmental Impact Report
Fish and Wildlife Service,
Interior.
ACTION: Notice of availability; record of
decision.
AGENCY:
We, the U.S. Fish and
Wildlife Service, and the California
State Coastal Conservancy, announce
the availability of the record of decision
(ROD) for the Don Edwards National
Wildlife Refuge—Phase 2 of the South
Bay Salt Pond Restoration Project final
environmental impact statement/
environmental impact report. The ROD
explains that the selected alternative is
the environmentally preferred
alternative.
SUMMARY:
ADDRESSES:
Document Availability: The ROD is
available at the following places:
Internet: https://www.southbay
restoration.org/planning/phase2/.
In Person: San Francisco Bay National
Wildlife Refuge Complex Headquarters,
1 Marshlands Rd., Fremont, CA 94555.
FOR FURTHER INFORMATION CONTACT:
Chris Barr, Deputy Project Leader, 510–
792–0222 (phone), or chris_barr@
fws.gov.
We, the
U.S. Fish and Wildlife Service (Service),
and the California State Coastal
Conservancy, announce the availability
of the record of decision (ROD) for the
final environmental impact statement/
environmental impact report (EIS/EIR)
for Phase 2 of the South Bay Salt Pond
Restoration Project (SBSP) at the Don
Edwards National Wildlife Refuge. The
ROD explains that the selected
alternative is the environmentally
preferred alternative.
SUPPLEMENTARY INFORMATION:
Background
In December 2007, the USFWS and
the California Department of Fish and
Wildlife (CDFW) published a Final EIS/
EIR for the SBSP Restoration Project at
the Don Edwards San Francisco Bay
National Wildlife Refuge (Refuge) and
the CDFW Eden Landing Ecological
Reserve (December 19, 2007; 72 FR
71937). The overall south bay salt pond
restoration area includes 15,100 acres,
which the USFWS and the CDFW
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acquired from Cargill, Inc., in 2003. The
lands acquired from Cargill are divided
into three pond complexes: The
Ravenswood Pond Complex, in San
Mateo County, managed by the USFWS;
the Alviso Pond complex, also managed
by the USFWS, which is mostly in Santa
Clara County, with five ponds in
Alameda County; and the Eden Landing
Pond Complex, in Alameda County,
which is owned and managed by the
CDFW. The SBSP Restoration Project
presented in the Final EIS/EIR was both
programmatic, covering a 50-year
period, and project-level, addressing the
specific components and
implementation of Phase 1.
In January 2008, we signed a Record
of Decision selecting the Tidal Emphasis
Alternative (Alternative C) for
implementation. This alternative will
result in 90 percent of the USFWS’s
ponds on the Refuge being restored to
tidal wetlands and 10 percent converted
to managed ponds. Under Phase 1 of
Alternative C, we restored ponds E8A,
E8X, E9, E12, and E13 at the Eden
Landing complex; A6, A8, A16, and A17
at the Alviso complex; and SF2 at the
Ravenswood complex. We also added
several trails, interpretive features, and
other recreational access points.
Construction was completed on the
USFWS ponds in 2013.
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Project
The SBSP Phase 2 project site is
located on the following three
geographically separate pond clusters:
the Ravenswood Pond Complex (R3, R4,
R5, and S5), the Alviso Pond ComplexMountain View Ponds (A1 and A2W),
the Alviso Pond Complex-A8 Ponds (A8
and A8S), and the Alviso Pond
Complex-Island Ponds (A19, A20, and
A21). These pond clusters are illustrated
in Figures 1–5 on the SBSP Restoration
Project website at https://www.southbay
restoration.org/planning/phase2/.
Phase 2 of the SBSP Restoration
Project will restore and enhance over
2,000 acres of tidal wetlands and
managed pond habitats in South San
Francisco Bay while providing for flood
management and wildlife-oriented
public access and recreation. On June 3,
2016, we announced the availability of
the Final EIS/EIR for Phase 2 (81 FR
35790).
Alternatives
We analyzed a range of alternatives in
the Final EIS/EIR, including No Action
Alternatives for each group of ponds.
The range of alternatives included
varying approaches to restoring tidal
marshes (including number and location
of breaches and other levee
modifications), habitat enhancements
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(islands, transition zones, and
channels), modifications to existing
levees and berms to maintain or
improve flood protection, and recreation
and public access components
(including trails, boardwalks, and
viewing platforms) which correspond to
the project objectives.
The alternatives for each group of
ponds, or pond cluster, are described
briefly below. The no-action alternatives
are described together, followed by the
action alternatives that were considered
for each pond cluster.
Alviso-Island Ponds, Alviso-Mountain
View Ponds, Alviso-A8 Ponds, and
Ravenswood Ponds—Alternatives A (No
Action)
Under Alternatives Island A,
Mountain View A, A8 A, and
Ravenswood A (the no-action
alternative at each of these pond
clusters), no new activities would be
implemented as part of Phase 2. The
pond clusters would continue to be
monitored and managed through the
activities described in the Adaptive
Management Plan (AMP) and in
accordance with current USFWS
practices.
Alviso Island Ponds
Alternative Island B
Alternative Island B would breach
Pond A19’s northern levee and remove
or lower levees between Ponds A19 and
A20 to increase connectivity and
improve the ecological function of both
ponds.
Alternative Island C
Alternative Island C would include
the components of Alternative Island B
with the addition of levee breaches on
the north sides of Ponds A20 and A21,
lowering of portions of levees around
Pond A20, pilot channels in Pond A19,
and widening the existing breaches on
the southern levee of Pond A19.
Alviso-Mountain View Ponds
Alternative Mountain View B
Under Alternative Mountain View B,
Ponds A1 and A2W levees would be
breached at several points to introduce
tidal flow in the ponds. Portions of
Pond A1’s western levee would be built
up to maintain current levels of flood
protection provided by the pond itself.
Habitat transition zones and habitat
islands would be constructed in the
ponds to increase habitat complexity
and quality for special-status species. A
new trail and viewing platform would
be installed to improve recreation and
public access at these ponds.
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Alternative Mountain View C
Under Alternative Mountain View C,
levees would be breached and lowered
to increase tidal flows in Pond A1, Pond
A2W, and Charleston Slough. The
inclusion of Charleston Slough (by
breaching and lowering much of Pond
A1’s western levee) is the primary
distinguishing feature between
Alternative Mountain View B and
Alternative Mountain View C. Several
additional new trails and viewing
platforms would be installed or replaced
to improve recreation and public access
at the pond cluster. To continue
providing water to the City of Mountain
View’s Shoreline Park sailing lake, a
new water intake would be constructed
at the proposed breach between Pond
A1 and Charleston Slough.
Alviso-A8 Ponds
Alternative A8 B
Alternative A8 B proposes the
construction of habitat transition zones
in Pond A8S’s southwest corner,
southeast corner, or both, depending on
the amount of material available.
Ravenswood Ponds
Alternative Ravenswood B
Alternative Ravenswood B would
open Pond R4 to tidal flows, improve
levees to provide additional flood
protection, create habitat transition zone
along the western edge of Pond R4,
establish managed ponds to improve
habitat for diving and dabbling birds,
increase pond connectivity, and add a
viewing platform to improve recreation
and public access.
Alternative Ravenswood C
Alternative Ravenswood C would be
similar to Alternative Ravenswood B,
with the following exceptions: Ponds R5
and S5 would be converted to a
particular type of managed pond that is
operated to maintain intertidal mudflat
elevation; water control structures
would be installed on Pond R3 to allow
for improvement to the habitat for
western snowy plover; an additional
habitat transition zone would be
constructed; and two public access and
recreational trails and additional
viewing platforms would be
constructed.
Alternative Ravenswood D
Alternative Ravenswood D would
open Pond R4 to tidal flows, improve
levees to provide additional flood
protection, create two habitat transition
zones in Pond R4, establish enhanced
managed ponds in Ponds R5 and S5,
increase pond connectivity, enhance
Pond R3 for western snowy plover
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habitat, remove the levees within and
between Ponds R5 and S5, and improve
recreation and public access.
Alternative Ravenswood D would also
allow temporary stormwater detention
into Ponds R5 and S5 via connections
with the City of Redwood City’s
Bayfront Canal and Atherton Channel
Project. This would treat a residual
salinity problem in Ponds R5 and S5.
Following public review of the Draft
EIS/EIR, USFWS and the California
State Coastal Conservancy, in
coordination with the Project
Management Team and other project
partners, identified the preferred
alternative, which is based on
restoration enhancements at all four
pond clusters, as well as maintained or
increased flood protection and
additional public access and recreation
features at two of the Phase 2 pond
clusters. The preferred alternative is
described in Chapter 6 of the Final EIS/
EIR. A summary is provided below.
Preferred Alternative: The preferred
alternative at each pond cluster is as
follows:
• At the Island Ponds it is Alternative
Island B, with one restoration
component of Alternative Island C
included, which is to widen only the
westernmost of the two existing
breaches on the south side of Pond A19.
• At the Mountain View Ponds it is
essentially Alternative Mountain View
B, with the substitution of one habitat
enhancement (do not include
Charleston Slough in tidal marsh
restoration but do construct a habitat
transition zone across the entire
southern extent of Pond A1, but only
across central portion of A2W) and the
addition of one public access
component drawn from Mountain View
C (add recreational trail on eastern levee
of Pond A2W to the northeast corner of
Pond A2W). There is also a modification
of one of the flood protection features
presented in the two action alternatives
(raise the Coast Casey Forebay levee
along southern border of Charleston
Slough and maintain necessary access to
existing utilities adjacent to that levee).
• At the A8 Ponds it is Alternative A8
B, except that the top elevation of the
proposed transition zones has been
increased to provide greater erosion
protection.
• At the Ravenswood Ponds it is
similar to Alternative Ravenswood B, in
its restoration goals and features for
Ponds R3, R4, R5, and S5, but it also
includes an additional habitat transition
zone and a trail on the eastern edge of
Ponds R5 and S5, all of which were
included in Alternatives Ravenswood C
and D.
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Selected Alternative
The ROD identifies the preferred
alternative as the selected alternative.
This alternative is also the
environmentally preferred alternative.
The basis for the decision, descriptions
of the alternatives considered, an
overview of the measures to be
implemented to avoid and minimized
environmental effects, and a summary
of the public involvement process are
provided in the ROD.
Authority
We publish this notice under the
authority of the National Environmental
Policy Act (42 U.S.C. 4371 et seq.) and
the Department of Interior’s
implementing regulations in title 43 of
the Code of Federal Regulations (43 CFR
part 46).
Jody Holzworth,
Acting Regional Director, Pacific Southwest
Region.
[FR Doc. 2018–22763 Filed 10–18–18; 8:45 am]
BILLING CODE 4333–15–P
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
[Docket No. FWS–R2–ES–2017–0105;
FXES11140200000–190–FF02ENEH00]
Final Environmental Impact Statement
on American Electric Power’s
American Burying Beetle Habitat
Conservation Plan in Arkansas,
Oklahoma, and Texas
Fish and Wildlife Service,
Interior.
ACTION: Notice of availability.
AGENCY:
We, the U.S. Fish and
Wildlife Service, under the National
Environmental Policy Act, make
available the final environmental impact
statement analyzing the impacts of
issuance of an incidental take permit
(ITP) for implementation of American
Electric Power’s American Burying
Beetle Habitat Conservation Plan in
Oklahoma, Arkansas, and Texas (HCP).
Our decision is to issue a 30-year ITP for
implementation of the HCP, which
authorizes incidental take of the
American burying beetle under the
Endangered Species Act.
DATES: We will finalize a record of
decision and issue a permit no sooner
than November 19, 2018.
ADDRESSES: You may obtain copies of
the documents in the following formats:
• Electronic:
Æ https://www.regulations.gov, in
Docket No. FWS–R2–ES–2017–0105.
SUMMARY:
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53077
Æ https://www.fws.gov/southwest/es/
Oklahoma/.
Æ CD–ROM: Contact Ms. Jonna Polk
(see FOR FURTHER INFORMATION CONTACT).
Æ Telephone: 918–581–7458.
• Hard copy: You may review the
final environmental impact statement
(EIS) at the following locations (by
appointment only):
Æ Department of the Interior, Natural
Resources Library, 1849 C Street NW,
Washington, DC 20240. Call 202–208–
5815.
Æ U.S. Fish and Wildlife Service, 500
Gold Avenue SW, Room 6034,
Albuquerque, NM 87102. Call 505–248–
6920.
Æ U.S. Fish and Wildlife Service,
9014 E 21st St., Tulsa, OK 74129. Call
918–581–7458.
FOR FURTHER INFORMATION CONTACT:
Jonna Polk, Field Supervisor, via U.S.
mail at Oklahoma Ecological Services
Field Office, U.S. Fish and Wildlife
Service, 9014 E. 21st St., Tulsa, OK
74129; or via phone at 918–581–7458.
SUPPLEMENTARY INFORMATION: We, the
U.S. Fish and Wildlife Service (Service),
announce the availability of several
documents related to an incidental take
permit (ITP) application under the
Endangered Species Act of 1973, as
amended (ESA; 16 U.S.C. 1531 et seq.).
The final EIS was developed in
compliance with the agency decisionmaking requirements of the National
Environmental Policy Act (NEPA; 42
U.S.C. 4321 et seq.), and is based on the
habitat conservation plan (HCP) as
submitted by American Electric Power
(applicant). We described, fully
evaluated, and analyzed all three
alternatives in detail in our 2018 final
EIS.
Our proposed action is to issue an ITP
to the applicant under section
10(a)(1)(B) of the ESA that authorizes
incidental take of the American burying
beetle (Nicrophorus americanus; ABB)
from the applicant’s maintenance,
operation, and expansion of its
electrical facilities in Oklahoma,
Arkansas, and Texas. American Electric
Power is one of the largest electric
utilities in the country, with an electric
system that includes transmission lines,
substations, switching stations, and a
distribution network. American Electric
Power’s ability to serve its customers
depends on the timely installation,
operation, and maintenance of its
electric facilities. The plan area for the
HCP includes areas where authorized
incidental take would occur and
conservation measures would take
place, a total of almost 32 million acres.
The applicant requested a term of 30
years from the date of ITP issuance. The
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Agencies
[Federal Register Volume 83, Number 203 (Friday, October 19, 2018)]
[Notices]
[Pages 53075-53077]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2018-22763]
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DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
[FWS-R8-NWRS-2018-N130; FXRS282108E8PD0-190-F2013227943]
South Bay Salt Pond Restoration Project, Phase 2; Don Edwards
National Wildlife Refuge, California; Record of Decision for Final
Environmental Impact Statement/Environmental Impact Report
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Notice of availability; record of decision.
-----------------------------------------------------------------------
SUMMARY: We, the U.S. Fish and Wildlife Service, and the California
State Coastal Conservancy, announce the availability of the record of
decision (ROD) for the Don Edwards National Wildlife Refuge--Phase 2 of
the South Bay Salt Pond Restoration Project final environmental impact
statement/environmental impact report. The ROD explains that the
selected alternative is the environmentally preferred alternative.
ADDRESSES:
Document Availability: The ROD is available at the following
places:
Internet: https://www.southbayrestoration.org/planning/phase2/.
In Person: San Francisco Bay National Wildlife Refuge Complex
Headquarters, 1 Marshlands Rd., Fremont, CA 94555.
FOR FURTHER INFORMATION CONTACT: Chris Barr, Deputy Project Leader,
510-792-0222 (phone), or [email protected].
SUPPLEMENTARY INFORMATION: We, the U.S. Fish and Wildlife Service
(Service), and the California State Coastal Conservancy, announce the
availability of the record of decision (ROD) for the final
environmental impact statement/environmental impact report (EIS/EIR)
for Phase 2 of the South Bay Salt Pond Restoration Project (SBSP) at
the Don Edwards National Wildlife Refuge. The ROD explains that the
selected alternative is the environmentally preferred alternative.
Background
In December 2007, the USFWS and the California Department of Fish
and Wildlife (CDFW) published a Final EIS/EIR for the SBSP Restoration
Project at the Don Edwards San Francisco Bay National Wildlife Refuge
(Refuge) and the CDFW Eden Landing Ecological Reserve (December 19,
2007; 72 FR 71937). The overall south bay salt pond restoration area
includes 15,100 acres, which the USFWS and the CDFW
[[Page 53076]]
acquired from Cargill, Inc., in 2003. The lands acquired from Cargill
are divided into three pond complexes: The Ravenswood Pond Complex, in
San Mateo County, managed by the USFWS; the Alviso Pond complex, also
managed by the USFWS, which is mostly in Santa Clara County, with five
ponds in Alameda County; and the Eden Landing Pond Complex, in Alameda
County, which is owned and managed by the CDFW. The SBSP Restoration
Project presented in the Final EIS/EIR was both programmatic, covering
a 50-year period, and project-level, addressing the specific components
and implementation of Phase 1.
In January 2008, we signed a Record of Decision selecting the Tidal
Emphasis Alternative (Alternative C) for implementation. This
alternative will result in 90 percent of the USFWS's ponds on the
Refuge being restored to tidal wetlands and 10 percent converted to
managed ponds. Under Phase 1 of Alternative C, we restored ponds E8A,
E8X, E9, E12, and E13 at the Eden Landing complex; A6, A8, A16, and A17
at the Alviso complex; and SF2 at the Ravenswood complex. We also added
several trails, interpretive features, and other recreational access
points. Construction was completed on the USFWS ponds in 2013.
Project
The SBSP Phase 2 project site is located on the following three
geographically separate pond clusters: the Ravenswood Pond Complex (R3,
R4, R5, and S5), the Alviso Pond Complex-Mountain View Ponds (A1 and
A2W), the Alviso Pond Complex-A8 Ponds (A8 and A8S), and the Alviso
Pond Complex-Island Ponds (A19, A20, and A21). These pond clusters are
illustrated in Figures 1-5 on the SBSP Restoration Project website at
https://www.southbayrestoration.org/planning/phase2/.
Phase 2 of the SBSP Restoration Project will restore and enhance
over 2,000 acres of tidal wetlands and managed pond habitats in South
San Francisco Bay while providing for flood management and wildlife-
oriented public access and recreation. On June 3, 2016, we announced
the availability of the Final EIS/EIR for Phase 2 (81 FR 35790).
Alternatives
We analyzed a range of alternatives in the Final EIS/EIR, including
No Action Alternatives for each group of ponds. The range of
alternatives included varying approaches to restoring tidal marshes
(including number and location of breaches and other levee
modifications), habitat enhancements (islands, transition zones, and
channels), modifications to existing levees and berms to maintain or
improve flood protection, and recreation and public access components
(including trails, boardwalks, and viewing platforms) which correspond
to the project objectives.
The alternatives for each group of ponds, or pond cluster, are
described briefly below. The no-action alternatives are described
together, followed by the action alternatives that were considered for
each pond cluster.
Alviso-Island Ponds, Alviso-Mountain View Ponds, Alviso-A8 Ponds, and
Ravenswood Ponds--Alternatives A (No Action)
Under Alternatives Island A, Mountain View A, A8 A, and Ravenswood
A (the no-action alternative at each of these pond clusters), no new
activities would be implemented as part of Phase 2. The pond clusters
would continue to be monitored and managed through the activities
described in the Adaptive Management Plan (AMP) and in accordance with
current USFWS practices.
Alviso Island Ponds
Alternative Island B
Alternative Island B would breach Pond A19's northern levee and
remove or lower levees between Ponds A19 and A20 to increase
connectivity and improve the ecological function of both ponds.
Alternative Island C
Alternative Island C would include the components of Alternative
Island B with the addition of levee breaches on the north sides of
Ponds A20 and A21, lowering of portions of levees around Pond A20,
pilot channels in Pond A19, and widening the existing breaches on the
southern levee of Pond A19.
Alviso-Mountain View Ponds
Alternative Mountain View B
Under Alternative Mountain View B, Ponds A1 and A2W levees would be
breached at several points to introduce tidal flow in the ponds.
Portions of Pond A1's western levee would be built up to maintain
current levels of flood protection provided by the pond itself. Habitat
transition zones and habitat islands would be constructed in the ponds
to increase habitat complexity and quality for special-status species.
A new trail and viewing platform would be installed to improve
recreation and public access at these ponds.
Alternative Mountain View C
Under Alternative Mountain View C, levees would be breached and
lowered to increase tidal flows in Pond A1, Pond A2W, and Charleston
Slough. The inclusion of Charleston Slough (by breaching and lowering
much of Pond A1's western levee) is the primary distinguishing feature
between Alternative Mountain View B and Alternative Mountain View C.
Several additional new trails and viewing platforms would be installed
or replaced to improve recreation and public access at the pond
cluster. To continue providing water to the City of Mountain View's
Shoreline Park sailing lake, a new water intake would be constructed at
the proposed breach between Pond A1 and Charleston Slough.
Alviso-A8 Ponds
Alternative A8 B
Alternative A8 B proposes the construction of habitat transition
zones in Pond A8S's southwest corner, southeast corner, or both,
depending on the amount of material available.
Ravenswood Ponds
Alternative Ravenswood B
Alternative Ravenswood B would open Pond R4 to tidal flows, improve
levees to provide additional flood protection, create habitat
transition zone along the western edge of Pond R4, establish managed
ponds to improve habitat for diving and dabbling birds, increase pond
connectivity, and add a viewing platform to improve recreation and
public access.
Alternative Ravenswood C
Alternative Ravenswood C would be similar to Alternative Ravenswood
B, with the following exceptions: Ponds R5 and S5 would be converted to
a particular type of managed pond that is operated to maintain
intertidal mudflat elevation; water control structures would be
installed on Pond R3 to allow for improvement to the habitat for
western snowy plover; an additional habitat transition zone would be
constructed; and two public access and recreational trails and
additional viewing platforms would be constructed.
Alternative Ravenswood D
Alternative Ravenswood D would open Pond R4 to tidal flows, improve
levees to provide additional flood protection, create two habitat
transition zones in Pond R4, establish enhanced managed ponds in Ponds
R5 and S5, increase pond connectivity, enhance Pond R3 for western
snowy plover
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habitat, remove the levees within and between Ponds R5 and S5, and
improve recreation and public access. Alternative Ravenswood D would
also allow temporary stormwater detention into Ponds R5 and S5 via
connections with the City of Redwood City's Bayfront Canal and Atherton
Channel Project. This would treat a residual salinity problem in Ponds
R5 and S5.
Following public review of the Draft EIS/EIR, USFWS and the
California State Coastal Conservancy, in coordination with the Project
Management Team and other project partners, identified the preferred
alternative, which is based on restoration enhancements at all four
pond clusters, as well as maintained or increased flood protection and
additional public access and recreation features at two of the Phase 2
pond clusters. The preferred alternative is described in Chapter 6 of
the Final EIS/EIR. A summary is provided below.
Preferred Alternative: The preferred alternative at each pond
cluster is as follows:
At the Island Ponds it is Alternative Island B, with one
restoration component of Alternative Island C included, which is to
widen only the westernmost of the two existing breaches on the south
side of Pond A19.
At the Mountain View Ponds it is essentially Alternative
Mountain View B, with the substitution of one habitat enhancement (do
not include Charleston Slough in tidal marsh restoration but do
construct a habitat transition zone across the entire southern extent
of Pond A1, but only across central portion of A2W) and the addition of
one public access component drawn from Mountain View C (add
recreational trail on eastern levee of Pond A2W to the northeast corner
of Pond A2W). There is also a modification of one of the flood
protection features presented in the two action alternatives (raise the
Coast Casey Forebay levee along southern border of Charleston Slough
and maintain necessary access to existing utilities adjacent to that
levee).
At the A8 Ponds it is Alternative A8 B, except that the
top elevation of the proposed transition zones has been increased to
provide greater erosion protection.
At the Ravenswood Ponds it is similar to Alternative
Ravenswood B, in its restoration goals and features for Ponds R3, R4,
R5, and S5, but it also includes an additional habitat transition zone
and a trail on the eastern edge of Ponds R5 and S5, all of which were
included in Alternatives Ravenswood C and D.
Selected Alternative
The ROD identifies the preferred alternative as the selected
alternative. This alternative is also the environmentally preferred
alternative. The basis for the decision, descriptions of the
alternatives considered, an overview of the measures to be implemented
to avoid and minimized environmental effects, and a summary of the
public involvement process are provided in the ROD.
Authority
We publish this notice under the authority of the National
Environmental Policy Act (42 U.S.C. 4371 et seq.) and the Department of
Interior's implementing regulations in title 43 of the Code of Federal
Regulations (43 CFR part 46).
Jody Holzworth,
Acting Regional Director, Pacific Southwest Region.
[FR Doc. 2018-22763 Filed 10-18-18; 8:45 am]
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