Takes of Marine Mammals Incidental to Specified Activities; Taking Marine Mammals Incidental to San Francisco Bay Area Water Emergency Transportation Authority Central Bay Operations and Maintenance Facility Project in Alameda, California, 10060-10066 [2015-03850]
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Federal Register / Vol. 80, No. 37 / Wednesday, February 25, 2015 / Notices
7. Conduct a pilot study with some or
all fishers from some or all island
groups to evaluate the practicality of
permits in the U.S. Caribbean EEZ.
The goal of these scoping meetings is
to allow the public to comment on the
options listed above and to provide
alternative options not yet considered
by the Council and NMFS.
Copy of the Scoping Document to
address the Development of Federal
Permits in the U.S. Caribbean Exclusive
Economic Zone can be found at https://
sero.nmfs.noaa.gov/sustainable_
fisheries/caribbean/ under
Current Rule Making or and the
Caribbean Council Web site at
caribbeanfmc.com.
Special Accommodations
These meetings are physically
accessible to people with disabilities.
For more information or request for sign
language interpretation and other
auxiliary aids, please contact Mr.
´
Miguel A. Rolon, Executive Director,
Caribbean Fishery Management Council,
˜
270 Munoz Rivera Avenue, Suite 401,
San Juan, Puerto Rico, 00918–1903,
telephone (787) 766–5926, at least 5
days prior to the meeting date.
Dated: February 20, 2015.
Tracey L. Thompson,
Acting Deputy Director, Office of Sustainable
Fisheries, National Marine Fisheries Service.
[FR Doc. 2015–03892 Filed 2–24–15; 8:45 am]
BILLING CODE 3510–22–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
RIN 0648–XD444
Takes of Marine Mammals Incidental to
Specified Activities; Taking Marine
Mammals Incidental to San Francisco
Bay Area Water Emergency
Transportation Authority Central Bay
Operations and Maintenance Facility
Project in Alameda, California
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice; issuance of an incidental
take authorization.
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AGENCY:
In accordance with the
Marine Mammal Protection Act
(MMPA) regulations, notification is
hereby given that NMFS has issued an
Incidental Harassment Authorization
(IHA) to the San Francisco Bay Area
Water Emergency Transportation
Authority (WETA) to take, by
harassment, small numbers of two
SUMMARY:
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species of marine mammals incidental
to pile driving and removal associated
with the Central Bay Operations and
Maintenance Facility Project in the City
of Alameda, California, between
December 1, 2015, through November
30, 2016.
DATES: Effective December 1, 2015,
through November 30, 2016.
ADDRESSES: A copy of the application
containing a list of the references used
in this document, NMFS’s
Environmental Assessment (EA),
Finding of No Significant Impact
(FONSI), and the IHA may be obtained
visiting the Internet at: https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications.
Documents cited in this notice may be
viewed, by appointment, during regular
business hours, at 1315 East West
Highway, Silver Spring, MD 20910.
FOR FURTHER INFORMATION CONTACT:
Shane Guan, Office of Protected
Resources, NMFS, (301) 427–8401.
SUPPLEMENTARY INFORMATION:
Background
Sections 101(a)(5)(A) and (D) of the
MMPA (16 U.S.C. 1361 et seq.) direct
the Secretary of Commerce to allow,
upon request, the incidental, but not
intentional, taking of small numbers of
marine mammals by U.S. citizens who
engage in a specified activity (other than
commercial fishing) within a specified
geographical region if certain findings
are made and either regulations are
issued or, if the taking is limited to
harassment, a notice of a proposed
authorization is provided to the public
for review.
An authorization for incidental
takings shall be granted if NMFS finds
that the taking will have a negligible
impact on the species or stock(s), will
not have an unmitigable adverse impact
on the availability of the species or
stock(s) for subsistence uses (where
relevant), and if the permissible
methods of taking and requirements
pertaining to the mitigation, monitoring
and reporting of such takings are set
forth. NMFS has defined ‘‘negligible
impact’’ in 50 CFR 216.103 as ‘‘an
impact resulting from the specified
activity that cannot be reasonably
expected to, and is not reasonably likely
to, adversely affect the species or stock
through effects on annual rates of
recruitment or survival.’’
Except with respect to certain
activities not pertinent here, the MMPA
defines ‘‘harassment’’ as: Any act of
pursuit, torment, or annoyance which (i)
has the potential to injure a marine
mammal or marine mammal stock in the
wild [Level A harassment]; or (ii) has
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the potential to disturb a marine
mammal or marine mammal stock in the
wild by causing disruption of behavioral
patterns, including, but not limited to,
migration, breathing, nursing, breeding,
feeding, or sheltering [Level B
harassment].
Summary of Request
On April 9, 2014, NMFS received an
application from WETA for the taking of
marine mammals incidental to the
construction of a Central Bay Operations
and Maintenance Facility (Project). The
purpose of the Project is to serve as the
central San Francisco Bay (Bay) base for
WETA’s ferry fleet. After NMFS
provided comments on the draft IHA
application, WETA submitted a revised
IHA application on May 15, 2014.
NMFS determined that the application
was adequate and complete on July 31,
2014. No changes was made for the
proposed WETA’s construction Project
as described in the proposed IHA except
the Project duration was changed to
December 1, 2015, through November
30, 2016, from the original June 15
through October 15, 2014, due to
funding and other constraints. Please
refer to Federal Register notice for the
proposed IHA for a detailed description
of the project activities.
Comments and Responses
A notice of NMFS’ proposal to issue
an IHA to WETA was published in the
Federal Register on September 17, 2014
(79 FR 55479). That notice described, in
detail, WETA’s activity, the marine
mammal species that may be affected by
the activity, and the anticipated effects
on marine mammals. During the 30-day
public comment period, NMFS received
comments from the Marine Mammal
Commission (Commission), the Sierra
Club, the San Francisco Bay
Conservation and Development
Commission (BCDC), and 40 private
citizens.
All comments specific to WETA’s
application that address the statutory
and regulatory requirements or findings
NMFS must make to issue an IHA are
addressed in this section of the Federal
Register notice.
Comment 1: The Commission
recommends NMFS issue the IHA to
WETA, subject to inclusion of the
proposed mitigation and monitoring
measures described in the proposed
IHA. In addition, the Commission
recommends that NMFS only authorize
in-season adjustments in the sizes of the
exclusion and/or disturbance zones
(zones of influence) if the size(s) of the
estimated zones are determined to be
too small.
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Response: NMFS agrees with the
Commission’s recommendation and has
issued the IHA with mitigation and
monitoring measures described below in
this document, with the requirement
that the exclusion and/or zones of
influence be adjusted only of the size(s)
of the estimated zones are determined to
be too small.
Comment 2: Citing WETA’s permit
application to BCDC to construct the
Central Bay Operations and
Maintenance Facility Project, BCDC
points out that an abandoned small craft
floating dock located at the proposed
project site that harbor seals use as a
haul-out site, would be removed for the
construction. BCDC states that there are
relatively few haul-out locations in the
Bay for harbor seals, and BCDC is
concerned that removal of a haul-out
location may result in harmful impacts
to wildlife. The Sierra Club and 40
private citizens also have concerns
about the loss of a harbor seal haul-out
due to the removal of the floating dock.
BSDC recommends that NMFS review
the potential habitat impacts associated
with removal of these harbor seal haulout locations, including suggestions for
mitigation and monitoring, where
appropriate, as part of the IHA
application for the project.
Response: NMFS was not aware this
issue during its initial analysis of
potential impacts to the loss of one
harbor seal haul-out site as a result of
the proposed WETA construction
project in the Bay. Therefore, the
potential impact of marine mammal
habitat did not address this in the
Federal Register (79 FR 55479;
September 17, 2014) for the proposed
IHA. Subsequently, NMFS conducted
further investigation and worked with
NMFS West Coast Regional Office to
assess the potential impacts to harbor
seal haul-out and habitat in general in
the Bay.
The harbor seal haul-out site that
would be affected is a small craft dock
located at the project site and was
abandoned by the Navy when it vacated
the Naval Air Station-Alameda in 1997.
The unmaintained dock has been
deteriorating slowly over the last 17
years and the deterioration has appeared
to be accelerating in the last five years.
In 2010, the portion connecting the
floating dock to land broke off and sank,
leaving remnant parts of the floating
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dock isolated from land. Since 2010,
additional remnant parts of the marina
have also been lost. During this period
of time harbor seals have been
opportunistically using the dock for
haul-out purposes. At present, seals
have been observed by local residents
hauling out on the portion of the dock
that is furthest from shore.
It is observed that on an average,
about 10 to 20 harbor seals use the
floating dock as haul-out periodically.
Although during the spring of 2014, one
pup was observed reared at the floating
dock, the site is not a known breeding
area for harbor seal. Because the dock
has been in a gradual state of decay
since the closure of the naval base and
will likely continue to fall apart, the
haul-out area on the dock provided for
harbor seals is expected to decrease and
eventually disappear.
Finally, several nearby haul-out sites
are available in the Bay that are
available to resident harbor seals in the
area. These areas include the tip of
Breakwater Island (1 mile from the
WETA project site) and the haul-out at
Yerba Buena Island (4 to 5 miles from
the WETA project site) which is
identified as one of the five major haulout sites for harbor seals in the San
Francisco Bay (Gibble 2011).
Therefore, the removal of the remnant
abandoned dock would have negligible
impact to harbor seal habitat in the
proposed WETA construction site.
NMFS has thoroughly reviewed
WETA’s IHA application, including the
proposed mitigation and monitoring
measures to reduce potential impacts
from the construction activities. These
mitigation and monitoring measures
include using noise attenuation devices
for impact pile driving, power down/
shutdown of pile driving hammer if a
marine mammal is observed
approaching the exclusion zone, and
monitoring the exclusion zones and
zones of influence. Detailed description
of these monitoring and mitigation
measures and NMFS analysis is
provided in the Federal Register (79 FR
55479; September 17, 2014) for the
proposed IHA, therefore, it is not
repeated here.
Comment 3: The Sierra Club and
several private citizens recommend that
NMFS requires WETA to construct a
new haul-out dock nearby to
compensate and mitigate the loss of
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harbor seal haul-out, if the current old
floating dock is to be removed.
Response: NMFS does not consider
building an artificial harbor seal haulout is a good conservation measure to
compensate for the loss of the old
floating dock that is being used as a
haul-out by 10–20 harbor seals. As the
Sierra Club also stated in its comment,
‘‘[i]n the case of the WETA ferry facility
project, it is not a traditional natural
shoreline that will be disturbed or
destroyed.’’ The floating dock proposed
to be removed is a manmade structure
that is bound to disappear as it
deteriorates and falls apart. To build
another new structure without
maintenance will likely have the same
issue in the near future. Therefore,
NMFS considers it better conservation
practice not to construct a new structure
just to replace the current deteriorating
artificial one.
Description of Marine Mammals in the
Area of the Specified Activity
The marine mammal species under
NMFS jurisdiction most likely to occur
in the proposed construction area
include Pacific harbor seal (Phoca
vitulina richardsi) and California sea
lion (Zalophus californianus). Although
harbor porpoise (Phocoena phocoena),
killer whale (Orcinus orca), and gray
whale (Eschrichtius robustus) have been
sighted near the vicinity of the proposed
construction area, their presence at the
activity area is considered unlikely,
because the proposed construction area
is not typical habitat for these species.
The southern sea otter (Enhydra lutris)
also may occur in the proposed
construction area, but that species is
managed by the U.S. Fish and Wildlife
Service and is not considered further in
this proposed IHA notice. A list of the
marine mammal species under NMFS
jurisdiction and their abundance and
Endangered Species Act (ESA) status is
provided in Table 1.
Additional information on the marine
mammal species found in California
waters can be found in Caretta et al.
(2013), which is available at the
following URL: https://
www.nmfs.noaa.gov/pr/sars/pdf/
po2012.pdf, and in the Federal Register
notice (79 FR 55479) for the proposed
IHA.
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TABLE 1—LIST OF MARINE MAMMAL SPECIES UNDER NMFS JURISDICTION THAT OCCUR IN THE VICINITY OF THE WETA
CENTRAL BAY OPERATIONS AND MAINTENANCE FACILITY PROJECT AREA
Scientific name
Stock
ESA Status
California sea lion ...................................
Harbor seal .............................................
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Common name
Zalophus californianus ...........................
Phoca vitulina richardsi ..........................
U.S. ........................
California ................
Not listed ................
Not listed ................
Potential Effects of the Specified
Activity on Marine Mammals and
Marine Mammal Habitat
The primary potential impacts to
marine mammals and marine mammal
habitat are associated with elevated
sound levels, but the project may also
result in additional effects to marine
mammal prey species and short-term,
local water turbidity caused by in-water
construction due to pile removal and
pile driving. These potential effects are
discussed in detail in the Federal
Register notice for the proposed IHA
and are not repeated here. The potential
affected habitat on harbor seal haul-out
was not discussed in the proposed IHA
because NMFS was not aware of that
issue at the time. An analysis of the
potential effect on the removal of a
harbor seal haul-out is provided below.
The harbor seal haul-out site that
would be affected is a small craft dock
located at the project site and was
abandoned by the Navy when it vacated
the Naval Air Station-Alameda in 1997.
The unmaintained dock has been
deteriorating slowly over the last 17
years and the deterioration has appeared
to be accelerating in the last five years.
Later in 2010, the portion connecting
the floating dock to land broke off and
sank, leaving remnant parts of the
floating dock isolated from land. Since
2010, additional remnant parts of the
marina have also been lost. During this
period of time harbor seals have been
opportunistically using the dock for
haul-out purposes. At present, seals
have been observed by local residents
hauling out on the portion of the dock
that is furthest from shore.
It is observed that on an average,
about 10 to 20 harbor seals use the
floating dock as haul-out periodically.
Although during the spring of 2014, one
pup was observed reared at the floating
dock, the site is not a known breeding
area for harbor seal. Because the dock
has been in a gradual state of decay
since the closure of the naval base and
will likely continue to fall apart, the
haul-out area on the dock provided for
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18:05 Feb 24, 2015
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harbor seals is expected to decrease and
eventually disappear.
Finally, several nearby haul-out sites
are available in the Bay that are
available to resident harbor seals in the
area. These areas include the tip of
Breakwater Island (1 mile from the
WETA project site) and the haul-out at
Yerba Buena Island (4 to 5 miles from
the WETA project site) which is
identified as one of the five major haulout sites for harbor seals in the San
Francisco Bay (Gibble 2011).
Therefore, the removal of the remnant
abandoned dock would have negligible
impact to harbor seal habitat in the
proposed WETA construction site.
Mitigation
In order to issue an incidental take
authorization (ITA) under section
101(a)(5)(D) of the MMPA, NMFS must
set forth the permissible methods of
taking pursuant to such activity, and
other means of effecting the least
practicable impact on such species or
stock and its habitat, paying particular
attention to rookeries, mating grounds,
and areas of similar significance, and on
the availability of such species or stock
for taking for certain subsistence uses
(where relevant).
For WETA’s proposed Central Bay
Operations and Maintenance Facility
Project, NMFS required the following
mitigation measures to minimize the
potential impacts to marine mammals in
the Project vicinity. The primary
purposes of these mitigation measures
are to minimize sound levels from the
activities, to monitor marine mammals
within designated zones of influence
corresponding to NMFS’ current Level B
harassment thresholds and, if marine
mammals with the ZOI appear disturbed
by the work activity, to initiate
immediate shutdown or power down of
the piling hammer, making it very
unlikely potential injury or hearing
impairment to marine mammals would
occur and ensuring that Level B
behavioral harassment of marine
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Abundance
296,750
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mammals would be reduced to the
lowest level practicable.
Use of Noise Attenuation Devices
Noise attenuation systems (i.e., bubble
curtains) will be used during all impact
pile driving of steel piles to dampen the
acoustic pressure and reduce the impact
on marine mammals. By reducing
underwater sound pressure levels at the
source, bubble curtains would reduce
the area over which Level B harassment
would occur, thereby potentially
reducing the numbers of marine
mammals affected. In addition, the
bubble curtain system would reduce
sound levels below the threshold for
injury (Level A harassment), and thus
eliminate the need for an exclusion zone
for Level A harassment.
Time Restrictions
Work would occur only during
daylight hours, when visual monitoring
of marine mammals can be conducted.
In addition, all in-water construction
will be limited to the period between
August 1 and November 30, 2016.
Establishment of Harassment Zones of
Influence
Before the commencement of in-water
pile driving activities, WETA shall
establish Level B behavioral harassment
zones of influence (ZOIs) where
received underwater sound pressure
levels (SPLs) are higher than 160 dB
(rms) and 120 dB (rms) re 1 mPa for
impulse noise sources (impact pile
driving) and non-impulses noise sources
(vibratory pile driving and mechanic
dismantling), respectively. The ZOIs
delineate where Level B harassment
would occur. Because of the relatively
low source levels from vibratory pile
driving and from impact pile driving
with air bubble curtains, there will be
no area where the noise level would
exceed the threshold for Level A
harassment for pinnipeds, which is 190
dB (rms) re 1 mPa. The modeled
maximum isopleths for ZOIs are listed
in Table 2.
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TABLE 2—MODELED LEVEL B HARASSMENT ZONES OF INFLUENCE FOR VARIOUS PILE DRIVING ACTIVITIES
Pile driving methods
Impact pile driving with air bubble curtain ..............
Vibratory pile driving ...............................................
In addition, although Level A
harassment and injury by noise are not
expected to occur due to
implementation of noise attenuation
devices and vibratory pile driving, a
minimum shutdown zone of 10 m will
be established during all pile driving
and removal activities, regardless of the
estimated zone. These precautionary
measures are intended to prevent the
already unlikely possibility of physical
interaction with construction equipment
and to establish a precautionary
minimum zone with regard to acoustic
effects.
Once the underwater acoustic
measurements are conducted during
initial test pile driving, WETA shall
adjust the sizes of the exclusion zones
and ZOIs only if the measured exclusion
zones and ZOIs are larger than modeled
zones. These zones will be monitored as
described under the Proposed
Monitoring section below.
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Soft Start
A ‘‘soft-start’’ technique is intended to
allow marine mammals to vacate the
area before the pile driver reaches full
power. Whenever there has been
downtime of 30 minutes or more
without pile driving, the contractor will
initiate the driving with ramp-up
procedures described below.
For vibratory hammers, the contractor
will initiate the driving for 15 seconds
at reduced energy, followed by a 1minute waiting period. This procedure
shall be repeated two additional times
before continuous driving is started.
This procedure would also apply to
vibratory pile extraction.
For impact driving, an initial set of
three strikes would be made by the
hammer at 40 percent energy, followed
by a 1-minute waiting period, then two
subsequent three-strike sets at 40
percent energy, with 1-minute waiting
periods, before initiating continuous
driving.
Shutdown Measures
WETA shall implement shutdown
measures for pile driving or pile
removal activities if a marine mammal
is sighted within or is about to enter the
10 m exclusion zone.
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Distance to 120
dB re 1
μPa (rms) (m)
Pile material and size
30″
24″
18″
18″
epoxy coated
epoxy coated
epoxy coated
plastic fender
steel
steel
steel
piles
piles ..................................
piles ..................................
piles ..................................
...........................................
In addition, WETA shall discontinue
pile driving or pile removal activities if
a marine mammal within a ZOI appears
disturbed by the work activity. Work
may not resume until the animal is seen
to leave the ZOI or 30 minutes have
passed since the disturbed animal was
last sighted.
Furthermore, for in-water heavy
machinery work with the potential to
affect marine mammals (other than pile
driving), if a marine mammal comes
within 10 m, operations shall cease
until the animal has left the shutdown
zone or 15 minutes has passed. Heavy
machinery work could include setting
the pile and removal of the pile from the
water column/substrate via a crane (i.e.,
dead pull).
Finally, if any marine mammal
species not authorized for take are
encountered during pile driving or
removal and are likely to be exposed to
sound pressure levels (SPLs) greater
than or equal to 160 dB re 1 mPa (rms)
for impact pile driving or greater than or
equal to 120 dB re 1 mPa (rms) for
vibratory driving or removal, then the
Holder of this IHA must cease those
activities prior to the animal entering
the applicable Level B zone to avoid
take. Activities cannot commence until
the animal has left the Level B zone.
Mitigation Conclusions
NMFS has carefully evaluated the
mitigation measures and considered a
range of other measures in the context
of ensuring that NMFS prescribes the
means of effecting the least practicable
impact on the affected marine mammal
species and stocks and their habitat. Our
evaluation of potential measures
included consideration of the following
factors in relation to one another:
• The manner in which, and the
degree to which, the successful
implementation of the measure is
expected to minimize adverse impacts
to marine mammals.
• The proven or likely efficacy of the
specific measure to minimize adverse
impacts as planned.
• The practicability of the measure
for applicant implementation.
Any mitigation measure(s) prescribed
by NMFS should be able to accomplish,
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NA
NA
NA
2,154
Distance to 160
dB re 1
μPa (rms) (m)
250
185
93
NA
have a reasonable likelihood of
accomplishing (based on current
science), or contribute to the
accomplishment of one or more of the
general goals listed below:
(1) Avoidance or minimization of
injury or death of marine mammals
wherever possible (goals 2, 3, and 4 may
contribute to this goal).
(2) A reduction in the numbers of
marine mammals (total number or
number at biologically important time
or location) exposed to received levels
of pile driving and pile removal or other
activities expected to result in the take
of marine mammals (this goal may
contribute to 1, above, or to reducing
harassment takes only).
(3) A reduction in the number of
times (total number or number at
biologically important time or location)
individuals would be exposed to
received levels of pile driving and pile
removal, or other activities expected to
result in the take of marine mammals
(this goal may contribute to 1, above, or
to reducing harassment takes only).
(4) A reduction in the intensity of
exposures (either total number or
number at biologically important time
or location) to received levels of pile
driving, or other activities expected to
result in the take of marine mammals
(this goal may contribute to a, above, or
to reducing the severity of harassment
takes only).
(5) Avoidance or minimization of
adverse effects to marine mammal
habitat, paying special attention to the
food base, activities that block or limit
passage to or from biologically
important areas, permanent destruction
of habitat, or temporary destruction/
disturbance of habitat during a
biologically important time.
(6) For monitoring directly related to
mitigation—an increase in the
probability of detecting marine
mammals, thus allowing for more
effective implementation of the
mitigation.
Based on our evaluation of the
applicant’s proposed measures, as well
as other measures considered by NMFS,
NMFS has preliminarily determined
that the proposed mitigation measures
provide the means of effecting the least
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practicable impact on marine mammals
species or stocks and their habitat,
paying particular attention to rookeries,
mating grounds, and areas of similar
significance.
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Monitoring and Reporting
In order to issue an ITA for an
activity, section 101(a)(5)(D) of the
MMPA states that NMFS must set forth,
‘‘requirements pertaining to the
monitoring and reporting of such
taking.’’ The MMPA implementing
regulations at 50 CFR 216.104 (a)(13)
indicate that requests for ITAs must
include the suggested means of
accomplishing the necessary monitoring
and reporting that will result in
increased knowledge of the species and
of the level of taking or impacts on
populations of marine mammals that are
expected to be present in the proposed
action area. WETA submitted a marine
mammal monitoring plan as part of the
IHA application. It can be found at
https://www.nmfs.noaa.gov/pr/permits/
incidental.htm. The plan may be
modified or supplemented based on
comments or new information received
from the public during the public
comment period.
Monitoring measures prescribed by
NMFS should accomplish one or more
of the following general goals:
(1) An increase in the probability of
detecting marine mammals, both within
the mitigation zone (thus allowing for
more effective implementation of the
mitigation) and in general to generate
more data to contribute to the analyses
mentioned below;
(2) An increase in our understanding
of how many marine mammals are
likely to be exposed to levels of pile
driving that we associate with specific
adverse effects, such as behavioral
harassment, TTS, or PTS;
(3) An increase in our understanding
of how marine mammals respond to
stimuli expected to result in take and
how anticipated adverse effects on
individuals (in different ways and to
varying degrees) may impact the
population, species, or stock
(specifically through effects on annual
rates of recruitment or survival) through
any of the following methods:
D Behavioral observations in the
presence of stimuli compared to
observations in the absence of stimuli
(need to be able to accurately predict
received level, distance from source,
and other pertinent information);
D Physiological measurements in the
presence of stimuli compared to
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observations in the absence of stimuli
(need to be able to accurately predict
received level, distance from source,
and other pertinent information);
D Distribution and/or abundance
comparisons in times or areas with
concentrated stimuli versus times or
areas without stimuli;
(4) An increased knowledge of the
affected species; and
(5) An increase in our understanding
of the effectiveness of certain mitigation
and monitoring measures.
Monitoring Measures
WETA shall employee NMFSapproved protected species observers
(PSOs) to conduct marine mammal
monitoring for its Central Bay
Operations and Maintenance Facility
Project. The PSOs will observe and
collect data on marine mammals in and
around the project area for 30 minutes
before, during, and for 30 minutes after
all pile removal and pile installation
work. If a PSO observes a marine
mammal within a ZOI that appears to be
disturbed by the work activity, the PSO
will notify the work crew to initiate
shutdown measures.
Monitoring of marine mammals
around the construction site shall be
conducted using high-quality binoculars
(e.g., Zeiss, 10 × 42 power). Marine
mammal visual monitoring shall be
conducted from the best vantage point
available, including the pier,
breakwater, and adjacent docks within
the harbor, to maintain an excellent
view of the ZOIs and adjacent areas
during the survey period. Monitors
would be equipped with radios or cell
phones for maintaining contact with
work crews.
Data collection during marine
mammal monitoring will consist of a
count of all marine mammals by
species, a description of behavior (if
possible), location, direction of
movement, type of construction that is
occurring, time that pile replacement
work begins and ends, any acoustic or
visual disturbance, and time of the
observation. Environmental conditions
such as weather, visibility, temperature,
tide level, current, and sea state would
also be recorded.
Reporting Measures
WETA would be required to submit
weekly monitoring reports to NMFS that
summarize the monitoring results,
construction activities, and
environmental conditions.
A final monitoring report would be
submitted to NMFS within 90 days after
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completion of the construction work.
This report would detail the monitoring
protocol, summarize the data recorded
during monitoring, and estimate the
number of marine mammals that may
have been harassed. NMFS would have
an opportunity to provide comments on
the report, and if NMFS has comments,
WETA would address the comments
and submit a final report to NMFS
within 30 days.
In addition, NMFS would require
WETA to notify NMFS’ Office of
Protected Resources and NMFS’
Stranding Network within 48 hours of
sighting an injured or dead marine
mammal in the vicinity of the
construction site. WETA shall provide
NMFS with the species or description of
the animal(s), the condition of the
animal(s) (including carcass condition,
if the animal is dead), location, time of
first discovery, observed behaviors (if
alive), and photo or video (if available).
In the event that WETA finds an
injured or dead marine mammal that is
not in the vicinity of the construction
area, WETA would report the same
information as listed above to NMFS as
soon as operationally feasible.
Estimated Take by Incidental
Harassment
Except with respect to certain
activities not pertinent here, the MMPA
defines ‘‘harassment’’ as: Any act of
pursuit, torment, or annoyance which (i)
has the potential to injure a marine
mammal or marine mammal stock in the
wild [Level A harassment]; or (ii) has
the potential to disturb a marine
mammal or marine mammal stock in the
wild by causing disruption of behavioral
patterns, including, but not limited to,
migration, breathing, nursing, breeding,
feeding, or sheltering [Level B
harassment].
As discussed above, in-water pile
removal and pile driving (vibratory and
impact) generate loud noises that could
potentially harass marine mammals in
the vicinity of WETA’s proposed Central
Bay Operations and Maintenance
Facility Project.
Currently, NMFS uses 120 dB re 1 mPa
and 160 dB re 1 mPa at the received
levels for the onset of Level B
harassment from non-impulse (vibratory
pile driving and removal) and impulse
sources (impact pile driving)
underwater, respectively. Table 3
summarizes the current NMFS marine
mammal take criteria.
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TABLE 3—CURRENT ACOUSTIC EXPOSURE CRITERIA FOR NON-EXPLOSIVE SOUND UNDERWATER
Criterion
Criterion definition
Threshold
Level A Harassment (Injury) ...........
Permanent Threshold Shift (PTS) (Any level above that which is
known to cause TTS).
Level B Harassment ........................
Level B Harassment ........................
Behavioral Disruption (for impulse noises) ............................................
Behavioral Disruption (for non-impulse noise) ......................................
180 dB re 1 μPa (cetaceans) 190
dB re 1 μPa (pinnipeds) root
mean square (rms).
160 dB re 1 μPa (rms).
120 dB re 1 μPa (rms).
As explained above, ZOIs will be
established that encompass the areas
where received underwater SPLs exceed
the applicable thresholds for Level B
harassment. There will not be a zone for
Level A harassment in this case, because
the bubble curtain system will keep all
underwater noise below the threshold
for Level A harassment.
Incidental take is estimated for each
species by estimating the likelihood of
a marine mammal being present within
a ZOI during active pile removal or
driving. Expected marine mammal
presence is determined by past
observations and general abundance
near the project area during the
construction window. Typically,
potential take is estimated by
multiplying the area of the ZOI by the
local animal density. This provides an
estimate of the number of animals that
might occupy the ZOI at any given
moment. However, this type of
calculation is not applicable in this
case, because the ZOI will be relatively
small and there is no specific local
animal density for harbor seals or
California sea lions. Based on
observational data, the maximum
number of harbor seals observed along
the closest breakwater near the project
vicinity ranges from 10 to 20
individuals. Observational data on
California sea lions are not available,
but they are generally less abundant
than harbor seals; therefore, the number
of harbor seals will be used to estimate
impacts for both species.
While it is unlikely that 10 to 20
individuals would be present inside the
ZOI at any one time, given the distance
from the nearest haul-out site, as a
worst-case, this analysis assumes that
up to 20 individuals might be present.
For the Project, the total number of
pile removal hours is estimated to not
exceed 18 hours over 3 days, and the
total number of pile driving hours is
estimated to not exceed 60 hours over
10 days. Therefore, the estimated total
number of days of activities that might
impact marine mammals is 13 days. For
the exposure estimate, it is assumed that
the highest count of harbor seals
observed, and the same number of
California sea lions, will be foraging
within the ZOI and be exposed multiple
times during the Project.
The calculation for marine mammal
exposures for this Project is estimated
by:
Exposure estimate = N * (10 days of
pile driving activity + 3 days of pile
removal activity), where:
N = # of animals potentially present
= 20.
This formula results in the following
exposure estimate:
Exposure estimate = 20 animals * 13
days = 260 animals.
Therefore, WETA is requesting
authorization for Level B acoustical
harassment of up to 260 harbor seals
and up to 260 California sea lions due
to pile removal and driving. A summary
of the take estimates and the
proportions of the stocks potentially
affected is provided in Table 4.
TABLE 4—SUMMARY OF POTENTIAL MARINE MAMMAL TAKES AND PERCENTAGES OF STOCKS AFFECTED
Estimated density
California sea lion .............................
Harbor seal .......................................
Estimated take by
level B harassment
Abundance of stock
Percentage of stock
potentially affected
NA .......................
NA .......................
260
260
396,750
30,196
0.06%
0.86%
Analysis and Determinations
asabaliauskas on DSK5VPTVN1PROD with NOTICES
Negligible Impact
Negligible impact is ‘‘an impact
resulting from the specified activity that
cannot be reasonably expected to, and is
not reasonably likely to, adversely affect
the species or stock through effects on
annual rates of recruitment or survival’’
(50 CFR 216.103). A negligible impact
finding is based on the lack of likely
adverse effects on annual rates of
recruitment or survival (i.e., populationlevel effects). An estimate of the number
of Level B harassment takes, alone, is
not enough information on which to
base an impact determination. In
addition to considering estimates of the
number of marine mammals that might
be ‘‘taken’’ through behavioral
harassment, NMFS must consider other
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factors, such as the likely nature of any
responses (their intensity, duration,
etc.), the context of any responses
(critical reproductive time or location,
migration, etc.), as well as the number
and nature of estimated Level A
harassment takes, the number of
estimated mortalities, and effects on
habitat.
WETA’s proposed Central Bay
Operations and Maintenance Facility
Project would involve pile removal and
pile driving activities. Elevated
underwater noises are expected to be
generated as a result of these activities;
however, these noises are expected to
result in no mortality or Level A
harassment and limited, if any, Level B
harassment of marine mammals. WETA
would use noise attenuation devices
(i.e., bubble curtains) during the impact
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Population trend
Stable.
Stable.
pile driving, thus eliminating the
potential for injury (including PTS) and
TTS from impact driving. For vibratory
pile removal and pile driving, noise
levels are not expected to reach the level
that may cause TTS, injury (including
PTS), or mortality to marine mammals.
Therefore, NMFS does not expect that
any animals would experience Level A
harassment (including injury or PTS) or
Level B harassment in the form of TTS
from being exposed to in-water pile
removal and pile driving associated
with WETA’s construction project.
In addition, WETA’s proposed
activities are localized and of short
duration. The entire project area is
limited to WETA’s Central Bay
Operations and Maintenance Facility
near Pier 3 in the City of Alameda. The
entire Project would involve the
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Federal Register / Vol. 80, No. 37 / Wednesday, February 25, 2015 / Notices
removal of 35 existing concrete piles
and installation of a total of 61 steel
piles ranging from 18 inches to 30
inches in diameter and 24 plastic piles
of 18-inch diameter. The duration for
pile removal is expected to be fewer
than three days and the duration for pile
driving is expected to be fewer than 10
days, for a total of 13 days of activity.
The duration for removing each pile
would be about 30 minutes, and the
duration for driving each pile would be
about 10 to 30 minutes for impact steel
pile driving and about 10 to 20 minutes
for plastic vibratory pile driving. These
low-intensity, localized, and short-term
noise exposures may cause brief startle
reactions or short-term behavioral
modification by the animals. These
reactions and behavioral changes are
expected to subside quickly when the
exposures cease. Moreover, the
proposed mitigation and monitoring
measures are expected to reduce
potential exposures and behavioral
modifications even further.
Additionally, no important feeding and/
or reproductive areas for marine
mammals are known to be near the
proposed action area. Therefore, the
take resulting from the proposed Central
Bay Operations and Maintenance
Project is not reasonably expected to,
and is not reasonably likely to,
adversely affect the marine mammal
species or stocks through effects on
annual rates of recruitment or survival.
The Project also is not expected to
have significant adverse effects on
affected marine mammals’ habitat, as
analyzed in detail in the ‘‘Anticipated
Effects on Marine Mammal Habitat’’
section in the Federal Register notice
(79 FR 55479; September 17, 2014). The
project activities would not modify
existing marine mammal habitat. The
activities may cause some fish to leave
the area of disturbance, thus temporarily
impacting marine mammals’ foraging
opportunities in a limited portion of the
foraging range, but because of the short
duration of the activities and the
relatively small area of the habitat that
may be affected, the impacts to marine
mammal habitat are not expected to
cause significant or long-term negative
consequences.
Based on the analysis contained
herein of the likely effects of the
specified activity on marine mammals
and their habitat, and taking into
consideration the implementation of the
proposed monitoring and mitigation
measures, NMFS finds that the total
marine mammal take from WETA’s
Central Bay Operations and
Maintenance Facility Project will have a
negligible impact on the affected marine
mammal species or stocks.
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Small Number
Based on analyses provided above, it
is estimated that approximately 260
California sea lions and 260 Pacific
harbor seals could be exposed to
received noise levels that could cause
Level B behavioral harassment from the
proposed construction work at the
WETA Central Bay Operations and
Maintenance Facility in Alameda, CA.
These numbers represent approximately
0.06% and 0.86% of the stocks and
populations of these species that could
be affected by Level B behavioral
harassment, respectively (see Table 4
above), which are small percentages
relative to the total populations of the
affected species or stocks.
Based on the analysis contained
herein of the likely effects of the
specified activity on marine mammals
and their habitat, and taking into
consideration the implementation of the
mitigation and monitoring measures,
which are expected to reduce the
number of marine mammals potentially
affected by the proposed action, NMFS
finds that small numbers of marine
mammals will be taken relative to the
populations of the affected species or
stocks.
Impact on Availability of Affected
Species for Taking for Subsistence Uses
There are no subsistence uses of
marine mammals in the proposed
project area, and thus no subsistence
uses impacted by this action. Therefore,
NMFS has determined that the total
taking of affected species or stocks
would not have an unmitigable adverse
impact on the availability of such
species or stocks for taking for
subsistence purposes.
Endangered Species Act (ESA)
No species listed under the ESA are
expected to be affected by these
activities. Therefore, NMFS has
determined that a section 7 consultation
under the ESA is not required.
National Environmental Policy Act
(NEPA)
NMFS prepared an Environmental
Assessment (EA) and analyzed the
potential impacts to marine mammals
that would result from WETA’s Central
Bay Operations and Maintenance
Facility project in Alameda, California.
Therefore, A Finding of No Significant
Impact (FONSI) was issued for this
action. A copy of the EA and FONSI is
available upon request.
Authorization
NMFS has issued an IHA to USCG for
the potential harassment of small
numbers of marine mammal species
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incidental to its waterfront repair
project at Station Monterey in
California, provided the previously
mentioned mitigation, monitoring, and
reporting requirements are incorporated.
Dated: February 19, 2015.
Donna S. Wieting,
Director, Office of Protected Resources,
National Marine Fisheries Service.
[FR Doc. 2015–03850 Filed 2–24–15; 8:45 am]
BILLING CODE 3510–22–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
RIN 0648–XD660
Takes of Marine Mammals Incidental to
Specified Activities; Seabird Research
Activities in Central California, 2015–
2016
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice; issuance of an incidental
harassment authorization.
AGENCY:
In accordance with the
Marine Mammal Protection Act
(MMPA) regulations, we hereby give
notification that the National Marine
Fisheries Service has issued an
Incidental Harassment Authorization
(IHA) to Point Blue Conservation
Science (Point Blue), to take marine
mammals, by Level B harassment,
incidental to conducting seabird and
pinniped research activities in central
California, January 2015 through
January 2016.
DATES: Effective January 31, 2015,
through January 30, 2016.
ADDRESSES: The public may obtain an
electronic copy of the Point Blue’s
application, supporting documentation,
the authorization, and a list of the
references cited in this document by
visiting: https://www.nmfs.noaa.gov/pr/
permits/incidental/research.htm. In the
case of problems accessing these
documents, please call the contact listed
here (see FOR FURTHER INFORMATION
CONTACT).
The Environmental Assessment and
associated Finding of No Significant
Impact, prepared pursuant to the
National Environmental Policy Act of
1969, are also available at the same site.
FOR FURTHER INFORMATION CONTACT:
Jeannine Cody, Office of Protected
Resources, NMFS (301) 427–8401.
SUPPLEMENTARY INFORMATION: Section
101(a)(5)(D) of the Marine Mammal
Protection Act (MMPA; 16 U.S.C. 1361
SUMMARY:
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Agencies
[Federal Register Volume 80, Number 37 (Wednesday, February 25, 2015)]
[Notices]
[Pages 10060-10066]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2015-03850]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
RIN 0648-XD444
Takes of Marine Mammals Incidental to Specified Activities;
Taking Marine Mammals Incidental to San Francisco Bay Area Water
Emergency Transportation Authority Central Bay Operations and
Maintenance Facility Project in Alameda, California
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Notice; issuance of an incidental take authorization.
-----------------------------------------------------------------------
SUMMARY: In accordance with the Marine Mammal Protection Act (MMPA)
regulations, notification is hereby given that NMFS has issued an
Incidental Harassment Authorization (IHA) to the San Francisco Bay Area
Water Emergency Transportation Authority (WETA) to take, by harassment,
small numbers of two species of marine mammals incidental to pile
driving and removal associated with the Central Bay Operations and
Maintenance Facility Project in the City of Alameda, California,
between December 1, 2015, through November 30, 2016.
DATES: Effective December 1, 2015, through November 30, 2016.
ADDRESSES: A copy of the application containing a list of the
references used in this document, NMFS's Environmental Assessment (EA),
Finding of No Significant Impact (FONSI), and the IHA may be obtained
visiting the Internet at: https://www.nmfs.noaa.gov/pr/permits/incidental.htm#applications.
Documents cited in this notice may be viewed, by appointment,
during regular business hours, at 1315 East West Highway, Silver
Spring, MD 20910.
FOR FURTHER INFORMATION CONTACT: Shane Guan, Office of Protected
Resources, NMFS, (301) 427-8401.
SUPPLEMENTARY INFORMATION:
Background
Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.)
direct the Secretary of Commerce to allow, upon request, the
incidental, but not intentional, taking of small numbers of marine
mammals by U.S. citizens who engage in a specified activity (other than
commercial fishing) within a specified geographical region if certain
findings are made and either regulations are issued or, if the taking
is limited to harassment, a notice of a proposed authorization is
provided to the public for review.
An authorization for incidental takings shall be granted if NMFS
finds that the taking will have a negligible impact on the species or
stock(s), will not have an unmitigable adverse impact on the
availability of the species or stock(s) for subsistence uses (where
relevant), and if the permissible methods of taking and requirements
pertaining to the mitigation, monitoring and reporting of such takings
are set forth. NMFS has defined ``negligible impact'' in 50 CFR 216.103
as ``an impact resulting from the specified activity that cannot be
reasonably expected to, and is not reasonably likely to, adversely
affect the species or stock through effects on annual rates of
recruitment or survival.''
Except with respect to certain activities not pertinent here, the
MMPA defines ``harassment'' as: Any act of pursuit, torment, or
annoyance which (i) has the potential to injure a marine mammal or
marine mammal stock in the wild [Level A harassment]; or (ii) has the
potential to disturb a marine mammal or marine mammal stock in the wild
by causing disruption of behavioral patterns, including, but not
limited to, migration, breathing, nursing, breeding, feeding, or
sheltering [Level B harassment].
Summary of Request
On April 9, 2014, NMFS received an application from WETA for the
taking of marine mammals incidental to the construction of a Central
Bay Operations and Maintenance Facility (Project). The purpose of the
Project is to serve as the central San Francisco Bay (Bay) base for
WETA's ferry fleet. After NMFS provided comments on the draft IHA
application, WETA submitted a revised IHA application on May 15, 2014.
NMFS determined that the application was adequate and complete on July
31, 2014. No changes was made for the proposed WETA's construction
Project as described in the proposed IHA except the Project duration
was changed to December 1, 2015, through November 30, 2016, from the
original June 15 through October 15, 2014, due to funding and other
constraints. Please refer to Federal Register notice for the proposed
IHA for a detailed description of the project activities.
Comments and Responses
A notice of NMFS' proposal to issue an IHA to WETA was published in
the Federal Register on September 17, 2014 (79 FR 55479). That notice
described, in detail, WETA's activity, the marine mammal species that
may be affected by the activity, and the anticipated effects on marine
mammals. During the 30-day public comment period, NMFS received
comments from the Marine Mammal Commission (Commission), the Sierra
Club, the San Francisco Bay Conservation and Development Commission
(BCDC), and 40 private citizens.
All comments specific to WETA's application that address the
statutory and regulatory requirements or findings NMFS must make to
issue an IHA are addressed in this section of the Federal Register
notice.
Comment 1: The Commission recommends NMFS issue the IHA to WETA,
subject to inclusion of the proposed mitigation and monitoring measures
described in the proposed IHA. In addition, the Commission recommends
that NMFS only authorize in-season adjustments in the sizes of the
exclusion and/or disturbance zones (zones of influence) if the size(s)
of the estimated zones are determined to be too small.
[[Page 10061]]
Response: NMFS agrees with the Commission's recommendation and has
issued the IHA with mitigation and monitoring measures described below
in this document, with the requirement that the exclusion and/or zones
of influence be adjusted only of the size(s) of the estimated zones are
determined to be too small.
Comment 2: Citing WETA's permit application to BCDC to construct
the Central Bay Operations and Maintenance Facility Project, BCDC
points out that an abandoned small craft floating dock located at the
proposed project site that harbor seals use as a haul-out site, would
be removed for the construction. BCDC states that there are relatively
few haul-out locations in the Bay for harbor seals, and BCDC is
concerned that removal of a haul-out location may result in harmful
impacts to wildlife. The Sierra Club and 40 private citizens also have
concerns about the loss of a harbor seal haul-out due to the removal of
the floating dock.
BSDC recommends that NMFS review the potential habitat impacts
associated with removal of these harbor seal haul-out locations,
including suggestions for mitigation and monitoring, where appropriate,
as part of the IHA application for the project.
Response: NMFS was not aware this issue during its initial analysis
of potential impacts to the loss of one harbor seal haul-out site as a
result of the proposed WETA construction project in the Bay. Therefore,
the potential impact of marine mammal habitat did not address this in
the Federal Register (79 FR 55479; September 17, 2014) for the proposed
IHA. Subsequently, NMFS conducted further investigation and worked with
NMFS West Coast Regional Office to assess the potential impacts to
harbor seal haul-out and habitat in general in the Bay.
The harbor seal haul-out site that would be affected is a small
craft dock located at the project site and was abandoned by the Navy
when it vacated the Naval Air Station-Alameda in 1997. The unmaintained
dock has been deteriorating slowly over the last 17 years and the
deterioration has appeared to be accelerating in the last five years.
In 2010, the portion connecting the floating dock to land broke off and
sank, leaving remnant parts of the floating dock isolated from land.
Since 2010, additional remnant parts of the marina have also been lost.
During this period of time harbor seals have been opportunistically
using the dock for haul-out purposes. At present, seals have been
observed by local residents hauling out on the portion of the dock that
is furthest from shore.
It is observed that on an average, about 10 to 20 harbor seals use
the floating dock as haul-out periodically. Although during the spring
of 2014, one pup was observed reared at the floating dock, the site is
not a known breeding area for harbor seal. Because the dock has been in
a gradual state of decay since the closure of the naval base and will
likely continue to fall apart, the haul-out area on the dock provided
for harbor seals is expected to decrease and eventually disappear.
Finally, several nearby haul-out sites are available in the Bay
that are available to resident harbor seals in the area. These areas
include the tip of Breakwater Island (1 mile from the WETA project
site) and the haul-out at Yerba Buena Island (4 to 5 miles from the
WETA project site) which is identified as one of the five major haul-
out sites for harbor seals in the San Francisco Bay (Gibble 2011).
Therefore, the removal of the remnant abandoned dock would have
negligible impact to harbor seal habitat in the proposed WETA
construction site.
NMFS has thoroughly reviewed WETA's IHA application, including the
proposed mitigation and monitoring measures to reduce potential impacts
from the construction activities. These mitigation and monitoring
measures include using noise attenuation devices for impact pile
driving, power down/shutdown of pile driving hammer if a marine mammal
is observed approaching the exclusion zone, and monitoring the
exclusion zones and zones of influence. Detailed description of these
monitoring and mitigation measures and NMFS analysis is provided in the
Federal Register (79 FR 55479; September 17, 2014) for the proposed
IHA, therefore, it is not repeated here.
Comment 3: The Sierra Club and several private citizens recommend
that NMFS requires WETA to construct a new haul-out dock nearby to
compensate and mitigate the loss of harbor seal haul-out, if the
current old floating dock is to be removed.
Response: NMFS does not consider building an artificial harbor seal
haul-out is a good conservation measure to compensate for the loss of
the old floating dock that is being used as a haul-out by 10-20 harbor
seals. As the Sierra Club also stated in its comment, ``[i]n the case
of the WETA ferry facility project, it is not a traditional natural
shoreline that will be disturbed or destroyed.'' The floating dock
proposed to be removed is a manmade structure that is bound to
disappear as it deteriorates and falls apart. To build another new
structure without maintenance will likely have the same issue in the
near future. Therefore, NMFS considers it better conservation practice
not to construct a new structure just to replace the current
deteriorating artificial one.
Description of Marine Mammals in the Area of the Specified Activity
The marine mammal species under NMFS jurisdiction most likely to
occur in the proposed construction area include Pacific harbor seal
(Phoca vitulina richardsi) and California sea lion (Zalophus
californianus). Although harbor porpoise (Phocoena phocoena), killer
whale (Orcinus orca), and gray whale (Eschrichtius robustus) have been
sighted near the vicinity of the proposed construction area, their
presence at the activity area is considered unlikely, because the
proposed construction area is not typical habitat for these species.
The southern sea otter (Enhydra lutris) also may occur in the proposed
construction area, but that species is managed by the U.S. Fish and
Wildlife Service and is not considered further in this proposed IHA
notice. A list of the marine mammal species under NMFS jurisdiction and
their abundance and Endangered Species Act (ESA) status is provided in
Table 1.
Additional information on the marine mammal species found in
California waters can be found in Caretta et al. (2013), which is
available at the following URL: https://www.nmfs.noaa.gov/pr/sars/pdf/po2012.pdf, and in the Federal Register notice (79 FR 55479) for the
proposed IHA.
[[Page 10062]]
Table 1--List of Marine Mammal Species Under NMFS Jurisdiction That Occur in the Vicinity of the WETA Central
Bay Operations and Maintenance Facility Project Area
----------------------------------------------------------------------------------------------------------------
Common name Scientific name Stock ESA Status Abundance
----------------------------------------------------------------------------------------------------------------
California sea lion.............. Zalophus U.S................ Not listed......... 296,750
californianus.
Harbor seal...................... Phoca vitulina California......... Not listed......... 30,196
richardsi.
----------------------------------------------------------------------------------------------------------------
Potential Effects of the Specified Activity on Marine Mammals and
Marine Mammal Habitat
The primary potential impacts to marine mammals and marine mammal
habitat are associated with elevated sound levels, but the project may
also result in additional effects to marine mammal prey species and
short-term, local water turbidity caused by in-water construction due
to pile removal and pile driving. These potential effects are discussed
in detail in the Federal Register notice for the proposed IHA and are
not repeated here. The potential affected habitat on harbor seal haul-
out was not discussed in the proposed IHA because NMFS was not aware of
that issue at the time. An analysis of the potential effect on the
removal of a harbor seal haul-out is provided below.
The harbor seal haul-out site that would be affected is a small
craft dock located at the project site and was abandoned by the Navy
when it vacated the Naval Air Station-Alameda in 1997. The unmaintained
dock has been deteriorating slowly over the last 17 years and the
deterioration has appeared to be accelerating in the last five years.
Later in 2010, the portion connecting the floating dock to land broke
off and sank, leaving remnant parts of the floating dock isolated from
land. Since 2010, additional remnant parts of the marina have also been
lost. During this period of time harbor seals have been
opportunistically using the dock for haul-out purposes. At present,
seals have been observed by local residents hauling out on the portion
of the dock that is furthest from shore.
It is observed that on an average, about 10 to 20 harbor seals use
the floating dock as haul-out periodically. Although during the spring
of 2014, one pup was observed reared at the floating dock, the site is
not a known breeding area for harbor seal. Because the dock has been in
a gradual state of decay since the closure of the naval base and will
likely continue to fall apart, the haul-out area on the dock provided
for harbor seals is expected to decrease and eventually disappear.
Finally, several nearby haul-out sites are available in the Bay
that are available to resident harbor seals in the area. These areas
include the tip of Breakwater Island (1 mile from the WETA project
site) and the haul-out at Yerba Buena Island (4 to 5 miles from the
WETA project site) which is identified as one of the five major haul-
out sites for harbor seals in the San Francisco Bay (Gibble 2011).
Therefore, the removal of the remnant abandoned dock would have
negligible impact to harbor seal habitat in the proposed WETA
construction site.
Mitigation
In order to issue an incidental take authorization (ITA) under
section 101(a)(5)(D) of the MMPA, NMFS must set forth the permissible
methods of taking pursuant to such activity, and other means of
effecting the least practicable impact on such species or stock and its
habitat, paying particular attention to rookeries, mating grounds, and
areas of similar significance, and on the availability of such species
or stock for taking for certain subsistence uses (where relevant).
For WETA's proposed Central Bay Operations and Maintenance Facility
Project, NMFS required the following mitigation measures to minimize
the potential impacts to marine mammals in the Project vicinity. The
primary purposes of these mitigation measures are to minimize sound
levels from the activities, to monitor marine mammals within designated
zones of influence corresponding to NMFS' current Level B harassment
thresholds and, if marine mammals with the ZOI appear disturbed by the
work activity, to initiate immediate shutdown or power down of the
piling hammer, making it very unlikely potential injury or hearing
impairment to marine mammals would occur and ensuring that Level B
behavioral harassment of marine mammals would be reduced to the lowest
level practicable.
Use of Noise Attenuation Devices
Noise attenuation systems (i.e., bubble curtains) will be used
during all impact pile driving of steel piles to dampen the acoustic
pressure and reduce the impact on marine mammals. By reducing
underwater sound pressure levels at the source, bubble curtains would
reduce the area over which Level B harassment would occur, thereby
potentially reducing the numbers of marine mammals affected. In
addition, the bubble curtain system would reduce sound levels below the
threshold for injury (Level A harassment), and thus eliminate the need
for an exclusion zone for Level A harassment.
Time Restrictions
Work would occur only during daylight hours, when visual monitoring
of marine mammals can be conducted.
In addition, all in-water construction will be limited to the
period between August 1 and November 30, 2016.
Establishment of Harassment Zones of Influence
Before the commencement of in-water pile driving activities, WETA
shall establish Level B behavioral harassment zones of influence (ZOIs)
where received underwater sound pressure levels (SPLs) are higher than
160 dB (rms) and 120 dB (rms) re 1 [mu]Pa for impulse noise sources
(impact pile driving) and non-impulses noise sources (vibratory pile
driving and mechanic dismantling), respectively. The ZOIs delineate
where Level B harassment would occur. Because of the relatively low
source levels from vibratory pile driving and from impact pile driving
with air bubble curtains, there will be no area where the noise level
would exceed the threshold for Level A harassment for pinnipeds, which
is 190 dB (rms) re 1 [mu]Pa. The modeled maximum isopleths for ZOIs are
listed in Table 2.
[[Page 10063]]
Table 2--Modeled Level B Harassment Zones of Influence for Various Pile Driving Activities
----------------------------------------------------------------------------------------------------------------
Distance to 120 Distance to 160
Pile driving methods Pile material and size dB re 1 [mu]Pa dB re 1 [mu]Pa
(rms) (m) (rms) (m)
----------------------------------------------------------------------------------------------------------------
Impact pile driving with air bubble curtain 30'' epoxy coated steel piles NA 250
24'' epoxy coated steel piles NA 185
18'' epoxy coated steel piles NA 93
Vibratory pile driving..................... 18'' plastic fender piles.... 2,154 NA
----------------------------------------------------------------------------------------------------------------
In addition, although Level A harassment and injury by noise are
not expected to occur due to implementation of noise attenuation
devices and vibratory pile driving, a minimum shutdown zone of 10 m
will be established during all pile driving and removal activities,
regardless of the estimated zone. These precautionary measures are
intended to prevent the already unlikely possibility of physical
interaction with construction equipment and to establish a
precautionary minimum zone with regard to acoustic effects.
Once the underwater acoustic measurements are conducted during
initial test pile driving, WETA shall adjust the sizes of the exclusion
zones and ZOIs only if the measured exclusion zones and ZOIs are larger
than modeled zones. These zones will be monitored as described under
the Proposed Monitoring section below.
Soft Start
A ``soft-start'' technique is intended to allow marine mammals to
vacate the area before the pile driver reaches full power. Whenever
there has been downtime of 30 minutes or more without pile driving, the
contractor will initiate the driving with ramp-up procedures described
below.
For vibratory hammers, the contractor will initiate the driving for
15 seconds at reduced energy, followed by a 1-minute waiting period.
This procedure shall be repeated two additional times before continuous
driving is started. This procedure would also apply to vibratory pile
extraction.
For impact driving, an initial set of three strikes would be made
by the hammer at 40 percent energy, followed by a 1-minute waiting
period, then two subsequent three-strike sets at 40 percent energy,
with 1-minute waiting periods, before initiating continuous driving.
Shutdown Measures
WETA shall implement shutdown measures for pile driving or pile
removal activities if a marine mammal is sighted within or is about to
enter the 10 m exclusion zone.
In addition, WETA shall discontinue pile driving or pile removal
activities if a marine mammal within a ZOI appears disturbed by the
work activity. Work may not resume until the animal is seen to leave
the ZOI or 30 minutes have passed since the disturbed animal was last
sighted.
Furthermore, for in-water heavy machinery work with the potential
to affect marine mammals (other than pile driving), if a marine mammal
comes within 10 m, operations shall cease until the animal has left the
shutdown zone or 15 minutes has passed. Heavy machinery work could
include setting the pile and removal of the pile from the water column/
substrate via a crane (i.e., dead pull).
Finally, if any marine mammal species not authorized for take are
encountered during pile driving or removal and are likely to be exposed
to sound pressure levels (SPLs) greater than or equal to 160 dB re 1
[mu]Pa (rms) for impact pile driving or greater than or equal to 120 dB
re 1 [mu]Pa (rms) for vibratory driving or removal, then the Holder of
this IHA must cease those activities prior to the animal entering the
applicable Level B zone to avoid take. Activities cannot commence until
the animal has left the Level B zone.
Mitigation Conclusions
NMFS has carefully evaluated the mitigation measures and considered
a range of other measures in the context of ensuring that NMFS
prescribes the means of effecting the least practicable impact on the
affected marine mammal species and stocks and their habitat. Our
evaluation of potential measures included consideration of the
following factors in relation to one another:
The manner in which, and the degree to which, the
successful implementation of the measure is expected to minimize
adverse impacts to marine mammals.
The proven or likely efficacy of the specific measure to
minimize adverse impacts as planned.
The practicability of the measure for applicant
implementation.
Any mitigation measure(s) prescribed by NMFS should be able to
accomplish, have a reasonable likelihood of accomplishing (based on
current science), or contribute to the accomplishment of one or more of
the general goals listed below:
(1) Avoidance or minimization of injury or death of marine mammals
wherever possible (goals 2, 3, and 4 may contribute to this goal).
(2) A reduction in the numbers of marine mammals (total number or
number at biologically important time or location) exposed to received
levels of pile driving and pile removal or other activities expected to
result in the take of marine mammals (this goal may contribute to 1,
above, or to reducing harassment takes only).
(3) A reduction in the number of times (total number or number at
biologically important time or location) individuals would be exposed
to received levels of pile driving and pile removal, or other
activities expected to result in the take of marine mammals (this goal
may contribute to 1, above, or to reducing harassment takes only).
(4) A reduction in the intensity of exposures (either total number
or number at biologically important time or location) to received
levels of pile driving, or other activities expected to result in the
take of marine mammals (this goal may contribute to a, above, or to
reducing the severity of harassment takes only).
(5) Avoidance or minimization of adverse effects to marine mammal
habitat, paying special attention to the food base, activities that
block or limit passage to or from biologically important areas,
permanent destruction of habitat, or temporary destruction/disturbance
of habitat during a biologically important time.
(6) For monitoring directly related to mitigation--an increase in
the probability of detecting marine mammals, thus allowing for more
effective implementation of the mitigation.
Based on our evaluation of the applicant's proposed measures, as
well as other measures considered by NMFS, NMFS has preliminarily
determined that the proposed mitigation measures provide the means of
effecting the least
[[Page 10064]]
practicable impact on marine mammals species or stocks and their
habitat, paying particular attention to rookeries, mating grounds, and
areas of similar significance.
Monitoring and Reporting
In order to issue an ITA for an activity, section 101(a)(5)(D) of
the MMPA states that NMFS must set forth, ``requirements pertaining to
the monitoring and reporting of such taking.'' The MMPA implementing
regulations at 50 CFR 216.104 (a)(13) indicate that requests for ITAs
must include the suggested means of accomplishing the necessary
monitoring and reporting that will result in increased knowledge of the
species and of the level of taking or impacts on populations of marine
mammals that are expected to be present in the proposed action area.
WETA submitted a marine mammal monitoring plan as part of the IHA
application. It can be found at https://www.nmfs.noaa.gov/pr/permits/incidental.htm. The plan may be modified or supplemented based on
comments or new information received from the public during the public
comment period.
Monitoring measures prescribed by NMFS should accomplish one or
more of the following general goals:
(1) An increase in the probability of detecting marine mammals,
both within the mitigation zone (thus allowing for more effective
implementation of the mitigation) and in general to generate more data
to contribute to the analyses mentioned below;
(2) An increase in our understanding of how many marine mammals are
likely to be exposed to levels of pile driving that we associate with
specific adverse effects, such as behavioral harassment, TTS, or PTS;
(3) An increase in our understanding of how marine mammals respond
to stimuli expected to result in take and how anticipated adverse
effects on individuals (in different ways and to varying degrees) may
impact the population, species, or stock (specifically through effects
on annual rates of recruitment or survival) through any of the
following methods:
[ssquf] Behavioral observations in the presence of stimuli compared
to observations in the absence of stimuli (need to be able to
accurately predict received level, distance from source, and other
pertinent information);
[ssquf] Physiological measurements in the presence of stimuli
compared to observations in the absence of stimuli (need to be able to
accurately predict received level, distance from source, and other
pertinent information);
[ssquf] Distribution and/or abundance comparisons in times or areas
with concentrated stimuli versus times or areas without stimuli;
(4) An increased knowledge of the affected species; and
(5) An increase in our understanding of the effectiveness of
certain mitigation and monitoring measures.
Monitoring Measures
WETA shall employee NMFS-approved protected species observers
(PSOs) to conduct marine mammal monitoring for its Central Bay
Operations and Maintenance Facility Project. The PSOs will observe and
collect data on marine mammals in and around the project area for 30
minutes before, during, and for 30 minutes after all pile removal and
pile installation work. If a PSO observes a marine mammal within a ZOI
that appears to be disturbed by the work activity, the PSO will notify
the work crew to initiate shutdown measures.
Monitoring of marine mammals around the construction site shall be
conducted using high-quality binoculars (e.g., Zeiss, 10 x 42 power).
Marine mammal visual monitoring shall be conducted from the best
vantage point available, including the pier, breakwater, and adjacent
docks within the harbor, to maintain an excellent view of the ZOIs and
adjacent areas during the survey period. Monitors would be equipped
with radios or cell phones for maintaining contact with work crews.
Data collection during marine mammal monitoring will consist of a
count of all marine mammals by species, a description of behavior (if
possible), location, direction of movement, type of construction that
is occurring, time that pile replacement work begins and ends, any
acoustic or visual disturbance, and time of the observation.
Environmental conditions such as weather, visibility, temperature, tide
level, current, and sea state would also be recorded.
Reporting Measures
WETA would be required to submit weekly monitoring reports to NMFS
that summarize the monitoring results, construction activities, and
environmental conditions.
A final monitoring report would be submitted to NMFS within 90 days
after completion of the construction work. This report would detail the
monitoring protocol, summarize the data recorded during monitoring, and
estimate the number of marine mammals that may have been harassed. NMFS
would have an opportunity to provide comments on the report, and if
NMFS has comments, WETA would address the comments and submit a final
report to NMFS within 30 days.
In addition, NMFS would require WETA to notify NMFS' Office of
Protected Resources and NMFS' Stranding Network within 48 hours of
sighting an injured or dead marine mammal in the vicinity of the
construction site. WETA shall provide NMFS with the species or
description of the animal(s), the condition of the animal(s) (including
carcass condition, if the animal is dead), location, time of first
discovery, observed behaviors (if alive), and photo or video (if
available).
In the event that WETA finds an injured or dead marine mammal that
is not in the vicinity of the construction area, WETA would report the
same information as listed above to NMFS as soon as operationally
feasible.
Estimated Take by Incidental Harassment
Except with respect to certain activities not pertinent here, the
MMPA defines ``harassment'' as: Any act of pursuit, torment, or
annoyance which (i) has the potential to injure a marine mammal or
marine mammal stock in the wild [Level A harassment]; or (ii) has the
potential to disturb a marine mammal or marine mammal stock in the wild
by causing disruption of behavioral patterns, including, but not
limited to, migration, breathing, nursing, breeding, feeding, or
sheltering [Level B harassment].
As discussed above, in-water pile removal and pile driving
(vibratory and impact) generate loud noises that could potentially
harass marine mammals in the vicinity of WETA's proposed Central Bay
Operations and Maintenance Facility Project.
Currently, NMFS uses 120 dB re 1 [mu]Pa and 160 dB re 1 [mu]Pa at
the received levels for the onset of Level B harassment from non-
impulse (vibratory pile driving and removal) and impulse sources
(impact pile driving) underwater, respectively. Table 3 summarizes the
current NMFS marine mammal take criteria.
[[Page 10065]]
Table 3--Current Acoustic Exposure Criteria for Non-Explosive Sound
Underwater
------------------------------------------------------------------------
Criterion Criterion definition Threshold
------------------------------------------------------------------------
Level A Harassment (Injury)... Permanent Threshold 180 dB re 1
Shift (PTS) (Any [mu]Pa
level above that (cetaceans) 190
which is known to dB re 1 [mu]Pa
cause TTS). (pinnipeds)
root mean
square (rms).
Level B Harassment............ Behavioral Disruption 160 dB re 1
(for impulse noises). [mu]Pa (rms).
Level B Harassment............ Behavioral Disruption 120 dB re 1
(for non-impulse [mu]Pa (rms).
noise).
------------------------------------------------------------------------
As explained above, ZOIs will be established that encompass the
areas where received underwater SPLs exceed the applicable thresholds
for Level B harassment. There will not be a zone for Level A harassment
in this case, because the bubble curtain system will keep all
underwater noise below the threshold for Level A harassment.
Incidental take is estimated for each species by estimating the
likelihood of a marine mammal being present within a ZOI during active
pile removal or driving. Expected marine mammal presence is determined
by past observations and general abundance near the project area during
the construction window. Typically, potential take is estimated by
multiplying the area of the ZOI by the local animal density. This
provides an estimate of the number of animals that might occupy the ZOI
at any given moment. However, this type of calculation is not
applicable in this case, because the ZOI will be relatively small and
there is no specific local animal density for harbor seals or
California sea lions. Based on observational data, the maximum number
of harbor seals observed along the closest breakwater near the project
vicinity ranges from 10 to 20 individuals. Observational data on
California sea lions are not available, but they are generally less
abundant than harbor seals; therefore, the number of harbor seals will
be used to estimate impacts for both species.
While it is unlikely that 10 to 20 individuals would be present
inside the ZOI at any one time, given the distance from the nearest
haul-out site, as a worst-case, this analysis assumes that up to 20
individuals might be present.
For the Project, the total number of pile removal hours is
estimated to not exceed 18 hours over 3 days, and the total number of
pile driving hours is estimated to not exceed 60 hours over 10 days.
Therefore, the estimated total number of days of activities that might
impact marine mammals is 13 days. For the exposure estimate, it is
assumed that the highest count of harbor seals observed, and the same
number of California sea lions, will be foraging within the ZOI and be
exposed multiple times during the Project.
The calculation for marine mammal exposures for this Project is
estimated by:
Exposure estimate = N * (10 days of pile driving activity + 3 days
of pile removal activity), where:
N = # of animals potentially present = 20.
This formula results in the following exposure estimate:
Exposure estimate = 20 animals * 13 days = 260 animals.
Therefore, WETA is requesting authorization for Level B acoustical
harassment of up to 260 harbor seals and up to 260 California sea lions
due to pile removal and driving. A summary of the take estimates and
the proportions of the stocks potentially affected is provided in Table
4.
Table 4--Summary of Potential Marine Mammal Takes and Percentages of Stocks Affected
--------------------------------------------------------------------------------------------------------------------------------------------------------
Percentage of
Estimated density Estimated take by Abundance of stock stock potentially Population trend
level B harassment affected
--------------------------------------------------------------------------------------------------------------------------------------------------------
California sea lion................... NA....................... 260 396,750 0.06% Stable.
Harbor seal........................... NA....................... 260 30,196 0.86% Stable.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Analysis and Determinations
Negligible Impact
Negligible impact is ``an impact resulting from the specified
activity that cannot be reasonably expected to, and is not reasonably
likely to, adversely affect the species or stock through effects on
annual rates of recruitment or survival'' (50 CFR 216.103). A
negligible impact finding is based on the lack of likely adverse
effects on annual rates of recruitment or survival (i.e., population-
level effects). An estimate of the number of Level B harassment takes,
alone, is not enough information on which to base an impact
determination. In addition to considering estimates of the number of
marine mammals that might be ``taken'' through behavioral harassment,
NMFS must consider other factors, such as the likely nature of any
responses (their intensity, duration, etc.), the context of any
responses (critical reproductive time or location, migration, etc.), as
well as the number and nature of estimated Level A harassment takes,
the number of estimated mortalities, and effects on habitat.
WETA's proposed Central Bay Operations and Maintenance Facility
Project would involve pile removal and pile driving activities.
Elevated underwater noises are expected to be generated as a result of
these activities; however, these noises are expected to result in no
mortality or Level A harassment and limited, if any, Level B harassment
of marine mammals. WETA would use noise attenuation devices (i.e.,
bubble curtains) during the impact pile driving, thus eliminating the
potential for injury (including PTS) and TTS from impact driving. For
vibratory pile removal and pile driving, noise levels are not expected
to reach the level that may cause TTS, injury (including PTS), or
mortality to marine mammals. Therefore, NMFS does not expect that any
animals would experience Level A harassment (including injury or PTS)
or Level B harassment in the form of TTS from being exposed to in-water
pile removal and pile driving associated with WETA's construction
project.
In addition, WETA's proposed activities are localized and of short
duration. The entire project area is limited to WETA's Central Bay
Operations and Maintenance Facility near Pier 3 in the City of Alameda.
The entire Project would involve the
[[Page 10066]]
removal of 35 existing concrete piles and installation of a total of 61
steel piles ranging from 18 inches to 30 inches in diameter and 24
plastic piles of 18-inch diameter. The duration for pile removal is
expected to be fewer than three days and the duration for pile driving
is expected to be fewer than 10 days, for a total of 13 days of
activity. The duration for removing each pile would be about 30
minutes, and the duration for driving each pile would be about 10 to 30
minutes for impact steel pile driving and about 10 to 20 minutes for
plastic vibratory pile driving. These low-intensity, localized, and
short-term noise exposures may cause brief startle reactions or short-
term behavioral modification by the animals. These reactions and
behavioral changes are expected to subside quickly when the exposures
cease. Moreover, the proposed mitigation and monitoring measures are
expected to reduce potential exposures and behavioral modifications
even further. Additionally, no important feeding and/or reproductive
areas for marine mammals are known to be near the proposed action area.
Therefore, the take resulting from the proposed Central Bay Operations
and Maintenance Project is not reasonably expected to, and is not
reasonably likely to, adversely affect the marine mammal species or
stocks through effects on annual rates of recruitment or survival.
The Project also is not expected to have significant adverse
effects on affected marine mammals' habitat, as analyzed in detail in
the ``Anticipated Effects on Marine Mammal Habitat'' section in the
Federal Register notice (79 FR 55479; September 17, 2014). The project
activities would not modify existing marine mammal habitat. The
activities may cause some fish to leave the area of disturbance, thus
temporarily impacting marine mammals' foraging opportunities in a
limited portion of the foraging range, but because of the short
duration of the activities and the relatively small area of the habitat
that may be affected, the impacts to marine mammal habitat are not
expected to cause significant or long-term negative consequences.
Based on the analysis contained herein of the likely effects of the
specified activity on marine mammals and their habitat, and taking into
consideration the implementation of the proposed monitoring and
mitigation measures, NMFS finds that the total marine mammal take from
WETA's Central Bay Operations and Maintenance Facility Project will
have a negligible impact on the affected marine mammal species or
stocks.
Small Number
Based on analyses provided above, it is estimated that
approximately 260 California sea lions and 260 Pacific harbor seals
could be exposed to received noise levels that could cause Level B
behavioral harassment from the proposed construction work at the WETA
Central Bay Operations and Maintenance Facility in Alameda, CA. These
numbers represent approximately 0.06% and 0.86% of the stocks and
populations of these species that could be affected by Level B
behavioral harassment, respectively (see Table 4 above), which are
small percentages relative to the total populations of the affected
species or stocks.
Based on the analysis contained herein of the likely effects of the
specified activity on marine mammals and their habitat, and taking into
consideration the implementation of the mitigation and monitoring
measures, which are expected to reduce the number of marine mammals
potentially affected by the proposed action, NMFS finds that small
numbers of marine mammals will be taken relative to the populations of
the affected species or stocks.
Impact on Availability of Affected Species for Taking for Subsistence
Uses
There are no subsistence uses of marine mammals in the proposed
project area, and thus no subsistence uses impacted by this action.
Therefore, NMFS has determined that the total taking of affected
species or stocks would not have an unmitigable adverse impact on the
availability of such species or stocks for taking for subsistence
purposes.
Endangered Species Act (ESA)
No species listed under the ESA are expected to be affected by
these activities. Therefore, NMFS has determined that a section 7
consultation under the ESA is not required.
National Environmental Policy Act (NEPA)
NMFS prepared an Environmental Assessment (EA) and analyzed the
potential impacts to marine mammals that would result from WETA's
Central Bay Operations and Maintenance Facility project in Alameda,
California. Therefore, A Finding of No Significant Impact (FONSI) was
issued for this action. A copy of the EA and FONSI is available upon
request.
Authorization
NMFS has issued an IHA to USCG for the potential harassment of
small numbers of marine mammal species incidental to its waterfront
repair project at Station Monterey in California, provided the
previously mentioned mitigation, monitoring, and reporting requirements
are incorporated.
Dated: February 19, 2015.
Donna S. Wieting,
Director, Office of Protected Resources, National Marine Fisheries
Service.
[FR Doc. 2015-03850 Filed 2-24-15; 8:45 am]
BILLING CODE 3510-22-P