Takes of Marine Mammals Incidental To Specified Activities; Taking Marine Mammals Incidental to Elkhorn Slough Tidal Marsh Restoration Project, Phase III in Monterey County, California, 43204-43212 [2021-16858]
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estimates are conservative and the
project occurs in a small footprint
compared to the available habitat in
Southeast Alaska. For minke whales, in
the northern part of their range they are
believed to be migratory and so few
minke whales have been seen during
three offshore Gulf of Alaska surveys
that a population estimate could not be
determined. With only twelve
authorized takes for this species, the
percentage of take in relation to the
stock abundance is likely to be very
small.
Based on the analysis contained
herein of the planned activity (including
the mitigation and monitoring
measures) and the anticipated take of
marine mammals, NMFS finds that
small numbers of marine mammals will
be taken relative to the population size
of the affected species or stocks.
Unmitigable Adverse Impact Analysis
and Determination
In order to issue an IHA, NMFS must
find that the specified activity will not
have an ‘‘unmitigable adverse impact’’
on the subsistence uses of the affected
marine mammal species or stocks by
Alaskan Natives. NMFS has defined
‘‘unmitigable adverse impact’’ in 50 CFR
216.103 as an impact resulting from the
specified activity: (1) That is likely to
reduce the availability of the species to
a level insufficient for a harvest to meet
subsistence needs by: (i) Causing the
marine mammals to abandon or avoid
hunting areas; (ii) Directly displacing
subsistence users; or (iii) Placing
physical barriers between the marine
mammals and the subsistence hunters;
and (2) That cannot be sufficiently
mitigated by other measures to increase
the availability of marine mammals to
allow subsistence needs to be met.
The project area does not spatially
overlap any known subsistence hunting.
The project area is a developed area
with regular marine vessel traffic.
Nonetheless, the AKDOT&PF provided
advanced public notice of construction
activities to reduce construction impacts
on local residents, adjacent businesses,
and other users of Port Chester and
nearby areas. This included notification
to nearby Alaska Native tribes that may
have members who hunt marine
mammals for subsistence. Currently, the
Metlakatla Indian Community does not
authorize the harvest of marine
mammals for subsistence use (R. Cook,
personal communication, June 5, 2020
as cited in the application).
The planned project is not likely to
adversely impact the availability of any
marine mammal species or stocks that
are commonly used for subsistence
purposes or to impact subsistence
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harvest of marine mammals in the
region because construction activities
are localized and temporary and
mitigation measures will be
implemented to minimize disturbance
of marine mammals in the project area.
Accordingly, NMFS has determined that
there will not be an unmitigable adverse
impact on the availability of any marine
mammals for taking for subsistence uses
from the AKDOT&PF’s planned
activities.
Endangered Species Act
Section 7(a)(2) of the Endangered
Species Act of 1973 (ESA: 16 U.S.C.
1531 et seq.) requires that each Federal
agency insure that any action it
authorizes, funds, or carries out is not
likely to jeopardize the continued
existence of any endangered or
threatened species or result in the
destruction or adverse modification of
designated critical habitat. To ensure
ESA compliance for the issuance of
IHAs, NMFS consults internally
whenever we propose to authorize take
for endangered or threatened species, in
this case with the Alaska Regional
Office (AKRO).
NMFS is authorizing take of the
Central North Pacific stock of humpback
whales, including individuals from the
Mexico DPS of humpback whales,
which are listed under the ESA. The
Permit and Conservation Division
completed a Section 7 consultation with
the AKRO for the issuance of this IHA.
The AKRO’s biological opinion states
that the action is not likely to jeopardize
the continued existence of the Mexico
DPS of humpback whales.
Authorization
As a result of these determinations,
NMFS authorizes an IHA to the
AKDOT&PF for conducting for the
planned pile driving and removal
activities as well as DTH during
construction of the Metlakatla Seaplane
Facility Refurbishment Project,
Metlakatla, Alaska for one year,
beginning August 2021, provided the
previously mentioned mitigation,
monitoring, and reporting requirements
are incorporated.
Dated: August 3, 2021.
Catherine Marzin,
Acting Director, Office of Protected Resources,
National Marine Fisheries Service.
[FR Doc. 2021–16861 Filed 8–5–21; 8:45 am]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
[RTID 0648–XB270]
Takes of Marine Mammals Incidental
To Specified Activities; Taking Marine
Mammals Incidental to Elkhorn Slough
Tidal Marsh Restoration Project, Phase
III in Monterey County, California
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice; proposed issuance of an
incidental harassment authorization;
request for comments.
AGENCY:
NMFS has received a request
from the California Department of Fish
and Wildlife (CDFW) for authorization
to take marine mammals incidental to
the Elkhorn slough Tidal Marsh
Restoration Project (Phase III) in
Monterey County, CA. which includes
the excavation and movement of soil
with heavy machinery for marsh
restoration. NMFS is requesting
comments on its proposal to issue an
incidental harassment authorization
(IHA) to incidentally take marine
mammals during the specified activities.
NMFS is also requesting comments on
a possible one-time, one-year renewal
that could be issued under certain
circumstances and if all requirements
are met, as described in Request for
Public Comments at the end of this
notice. NMFS will consider public
comments prior to making any final
decision on the issuance of the
requested MMPA authorizations and
agency responses will be summarized in
the final notice of our decision.
DATES: Comments and information must
be received no later than September 7,
2021.
ADDRESSES: Comments should be
addressed to Jolie Harrison, Chief,
Permits and Conservation Division,
Office of Protected Resources, National
Marine Fisheries Service. Written
comments should be submitted via
email to ITP.Corcoran@noaa.gov.
Instructions: NMFS is not responsible
for comments sent by any other method,
to any other address or individual, or
received after the end of the comment
period. Comments, including all
attachments, must not exceed a 25megabyte file size. Attachments to
comments will be accepted in Microsoft
Word or Excel or Adobe PDF file
formats only. All comments received are
a part of the public record and will
generally be posted online at https://
SUMMARY:
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www.fisheries.noaa.gov/permit/
incidental-take-authorizations-undermarine-mammal-protection-act without
change. All personal identifying
information (e.g., name, address)
voluntarily submitted by the commenter
may be publicly accessible. Do not
submit confidential business
information or otherwise sensitive or
protected information.
Kim
Corcoran, Office of Protected Resources,
NMFS, (301) 427–8401. Electronic
copies of the original application and
supporting documents (including NMFS
FR notices of the prior authorizations),
as well as a list of the references cited
in this document, may be obtained
online at: https://
www.fisheries.noaa.gov/permit/
incidental-take-authorizations-undermarine-mammal-protection-act. In case
of problems accessing these documents,
please call the contact listed above.
FOR FURTHER INFORMATION CONTACT:
SUPPLEMENTARY INFORMATION:
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Background
The MMPA prohibits the ‘‘take’’ of
marine mammals, with certain
exceptions. Sections 101(a)(5)(A) and
(D) of the MMPA (16 U.S.C. 1361 et
seq.) direct the Secretary of Commerce
(as delegated to NMFS) 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
incidental take authorization may be
provided to the public for review.
Authorization for incidental takings
shall be granted if NMFS finds that the
taking will have a negligible impact on
the species or stock(s) and will not have
an unmitigable adverse impact on the
availability of the species or stock(s) for
taking for subsistence uses (where
relevant). Further, NMFS must prescribe
the permissible methods of taking and
other ‘‘means of effecting the least
practicable adverse impact’’ on the
affected species or stocks and their
habitat, paying particular attention to
rookeries, mating grounds, and areas of
similar significance, and on the
availability of such species or stocks for
taking for certain subsistence uses
(referred to in shorthand as
‘‘mitigation’’); and requirements
pertaining to the mitigation, monitoring
and reporting of such takings are set
forth.
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The definitions of all applicable
MMPA statutory terms cited above are
included in the relevant sections below.
National Environmental Policy Act
To comply with the National
Environmental Policy Act of 1969
(NEPA; 42 U.S.C. 4321 et seq.) and
NOAA Administrative Order (NAO)
216–6A, NMFS must review our
proposed action (i.e., the issuance of an
IHA) with respect to potential impacts
on the human environment.
The current action is consistent with
categories of activities identified in
Categorical Exclusion B4 (incidental
harassment authorizations with no
anticipated serious injury or mortality)
of the Companion Manual for NOAA
Administrative Order 216–6A, which do
not individually or cumulatively have
the potential for significant impacts on
the quality of the human environment
and for which we have not identified
any extraordinary circumstances that
would preclude this categorical
exclusion. Accordingly, NMFS has
preliminarily determined that the
issuance of the proposed renewal
qualifies to be categorically excluded
from further NEPA review just as the
initial IHA did.
We will review all comments
submitted in response to this notice
prior to concluding our NEPA process
or making a final decision on the IHA
request.
Summary of Request
On June 14, 2021, NMFS received a
request from CDFW for an IHA to take
marine mammals incidental to the
Elkhorn Slough Restoration Project,
Phase III, at the Seal Bend Restoration
Area in Monterey Country, CA. The
application was deemed adequate and
complete on July 27, 2021. CDFW’s
request is for take of a small number of
Pacific harbor seals (Phoca vitulina) by
Level B harassment only. Neither CDFW
nor NMFS expects serious injury or
mortality to result from this activity
and, therefore, an IHA is appropriate.
NMFS previously issued an IHA to
CDFW for Phase I (82 FR 16800; April
6, 2017) and Phase II (85 FR 14640;
March 13, 2020) of the Elkhorn Slough
Restoration Project. Restoration work
under the 2020 IHA at the MinhotoHester and Seal Bend restoration areas
was expected to be completed within
180 days within the one-year timeframe
of the IHA. However, on May 3, 2021
CDFW informed NMFS that the
estimated 180 days of construction for
both the Minhoto-Hester and Seal Bend
Restoration Areas would not be enough
to complete the project. This
preliminary estimate did not adequately
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account for variable weather conditions
experienced during construction (e.g.,
wet weather and soils required
extensive reworking of fill), the amount
of time to haul material from the borrow
area to the fill location, or contractor
availability which resulted in a smaller
crew than initially expected. Therefore,
only 118 days of construction occurred
under the initial IHA. To cover the
remaining work at the Minhoto-Hester
Restoration Area, CDFW requested an
IHA Renewal. NMFS published a notice
of a proposed IHA Renewal and request
for comments in the Federal Register on
June 8, 2021 to complete the remaining
62 days of work (86 FR 30412; June 8,
2021) (Hereafter referred to as the 2021
Renewal). We subsequently published
the final notice of our issuance of the
IHA Renewal on July 7, 2021 (86 FR
35751).
As work at the Seal Bend Restoration
Area had not begun and could not be
covered by the IHA Renewal, CDFW
requested that a new IHA be issued that
would be valid for one year from the
date of issuance. Under this proposed
IHA, CDFW would conduct 240 days of
work to restore 28.6 acres (11.57
hectares) of tidal marsh habitat in the
Seal Bend Restoration Area. The project
would include the use of haul trucks
and heavy earthmoving equipment to
transport dry material out onto the
marsh. The proposed project activities
will not differ from the 2020 IHA other
than the number of construction days,
and the means of calculating take.
Description of the Proposed Activity
Overview
Over the past 150 years, human
activities have altered the tidal,
freshwater, and sediment processes,
which are essential to support and
sustain Elkhorn Slough’s estuarine
habitats. In response to years of
anthropogenic degradation (e.g., diking
and marsh draining), the Elkhorn
Slough Tidal Marsh Restoration Project
(project) plans to restore approximately
122 acres (49.37 hectares) of tidal marsh
across three phases, all of which are
located in Monterey County, California
(Figure 1). Phase I of the project,
completed in 2018, restored 61 acres
(24.69 hectares) of tidal marsh within
the Minhoto-Hester Marsh in Elkhorn
Slough (Monterey, CA) (Figure 2) (82 FR
16800; April 06, 2017) (Hereafter
referred to as the 2017 IHA). Phase II of
the project, planned for completion in
September 2021, plans to restore 29.4
acres (11.90 hectares) of tidal marsh at
the Minhoto-Hester Restoration Area
adjacent to the Phase I Restoration Area
(see Figure 2). As the remainder of the
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work associated with the project has not
been completed and could not be
covered by the 2021 Renewal, CDFW
requests that this proposed IHA cover
take incidental to Phase III of the
project, which will restore 28.6 acres
(11.57 hectares) at the Seal Bend
Restoration Area shown in Figure 2.
Similar to previous projects, Phase III
will relocate soil from an upland area
called ‘‘the borrow’’ through use of
heavy earth moving equipment, within
a 12 month period. Construction
activities are expected to produce
airborne noise and visual disturbance
that have the potential to result in
behavioral harassment of Pacific harbor
seals (Phoca vitulina). NMFS is
proposing to authorize take, by Level B
Harassment, of Pacfic harbor seals as a
result of the specified activity. To
support public review and comment on
the IHA that NMFS is proposing to issue
here, we refer to the documents related
to the previously issued IHA and
discuss any new or changed information
here. The previous documents include
the Federal Register notice of the
issuance of the 2020 IHA (85 FR 14640;
March 13, 2020), the Federal Register
notice of the issuance of the 2021 IHA
Renewal (86 FR 35751; July 7, 2021),
and all associated references and
documents. We also refer the reader to
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CDFW’s previous and current
applications and monitoring reports
which can be found at https://
www.fisheries.noaa.gov/node/23111.
Dates and Duration
As previously mentioned, the Phase II
IHA covered restoration work at both
the Minhoto-Hester Restoration Area
and the Seal Bend Restoration Area for
180 total days of construction but the
work was not able to be completed for
both locations within the timeframe and
take estimate constraints of the 2020
IHA and 2021 Renewal IHA for the
reasons discussed above. Therefore,
CDFW is requesting this new
authorization for 240 construction days
to account for similar, anticipated
construction constraints at the Seal
Bend Restoration Area, such as likely
wet weather, the distance between the
borrow area and restoration site, and
limited contractor availability. CDFW is
prepared to start the work at Seal Bend
as soon as they receive authorization, so
this IHA will be valid for one year from
the date of issuance.
Specific Geographic Region
The project is located in the Elkhorn
Slough estuary, about 90 miles south of
San Francisco and 20 miles north of
Monterey in Monterey Country,
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California (Figure 1). The project sites
are located on land owned and operated
by CDFW as part of the Elkhorn Slough
Ecological and National Estuarine
Research Reserves. The waters of the
Elkhorn Slough State Marine Reserve
and Monterey Bay National Marine
Sanctuary run north of the Phase III
project site in Elkhorn Slough’s main
channel. Two additional Marine
Protected Areas are located within
approximately one mile of the project
site: Elkhorn Slough State Marine
Conservation Area and Moro Cojo
Slough State Marine Reserve.
Phase III would restore the Seal Bend
Restoration Area which includes about
28.6 acres (11.57 hectares) of historic
farmland adjacent to Elkhorn Slough
and west of the Phase I and II
restoration areas (Figure 2). The
proposed project area is low-lying area
consisting of subsided pickleweed
(Salicornia) marsh, intertidal mudflats,
and tidal channels. Fill material for Seal
Bend will be obtained from a 38 acre
(15.38 hectare) upland borrow area
south of the Minhoto-Hester (Phase II)
Restoration Area (Figure 2). Once
complete, the slopes of the borrow area
would be graded to increase marsh area
and create a gently sloping ecotone band
along the edge of the Phase I and II sites.
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Figure 2. Map depicting the location of each restoration site for the project for the
proposed and previous phases
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Figure 1. Location of the proposed restoration project in Monterey County,
California.
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Detailed Description of Specific Activity
As previously described, the proposed
project would restore 28.6 acres (11.57
hectares) of tidal marsh habitat at the
Seal Bend Restoration Area. As
described in more detail in the 2020
IHA, project components to restore
hydrologic function to the project area
would include raising the subsided
marsh plain, maintaining or reexcavating existing tidal channels, and
restoring marsh plain, ecotone, and
native grassland habitat within a
borrow/upland buffer area.
Up to 133,346 cubic yards (CY)
(101950.33 cubic meters (CM)) of soil
will be obtained from the upland
borrow area to raise the subsided marsh
plain to an average of 1.9 feet (0.58 m)
above the current height. This target
elevation would allow emergent
wetland vegetation to naturally be
reestablished. Sediment would be
placed to a fill elevation slightly higher
than the target marsh plain elevation to
allow for settlement and consolidation
of the underlying soils. After
construction is complete, the project
would rely primarily on natural
vegetation recruitment in the restored
marsh areas.
An additional detailed description of
the proposed restoration project is
found in the proposed and issued 2020
IHA. The location and nature of the
activities, including the types of
equipment planned for use, are identical
to those described in the previous
notices. Differences between the 2020
IHA and the proposed 2021–2022 IHA
occur in the number of days restoration
work would occur, the method for
calculating take, and visual monitoring
requirements, all of which are discussed
in detail below.
Description of Marine Mammals in the
Area of Specified Activities
A description of the marine mammals
in the area of the activities is found in
the 2020 IHA, which remains applicable
to the proposed 2021–2022 IHA as well.
In addition, NMFS has reviewed recent
2020 Stock Assessment Reports,
information on relevant Unusual
Mortality Events, and recent scientific
literature, and determined that no new
information affects our original analysis
of impacts under this proposed IHA.
Potential Effects of Specified Activities
on Marine Mammals and Their Habitat
A description of the potential effects
of the specified activities on marine
mammals and their habitat may be
found in the documents supporting the
2020 IHA, which remains applicable to
the issuance of the proposed 2021–2022
IHA. There is no new information on
potential effects.
Estimated Take
A detailed description of the previous
methods and inputs used to estimate
authorized take is found in the 2020
IHA. The total number of construction
days and the method of estimating take
have been modified from the 2020 IHA
to reflect construction delays as
discussed above and the monitoring
data received under the 2020 IHA. The
source levels and marine mammal
occurrence and density remain
unchanged from the 2020 IHA and
detailed information regarding these
figures can be found in the proposed
and issued 2020 IHA.
Take Calculation and Estimates
To repeat how take was calculated in
the 2020 IHA, we used the total number
of seals taken during Phase I
construction (i.e., 62 seals) divided by
the sum of the daily average number of
seals observed hourly during Phase I.
That percentage (8.79 percent) was
rounded to 9 percent and multiplied by
the sum of the highest daily count of
seals observed by the Reserve Otter
Monitoring Projects at all observation
areas between January 2018 and April
2019 (i.e., 417). That number was
multiplied by the total number of
construction days to arrive at the total
take estimate that was used.
For the Phase III project, we have
additional monitoring data that more
accurately reflects the amount of take
that occurs during this type of
restoration activity. In particular we
now have data that suggests the
maximum number of seals taken per day
within 300 m of construction activity
has been 8, which occurred on
September 8, 2020 (Table 1). Therefore,
we propose to use that maximum
number of seals taken per day to
estimate take using the following
formula:
Total Take Estimate = Max # of seals
taken per day * # of Construction Days
The average total individual takes per
day for Phase II was 1.33 which is
considerably lower than the proposed
maximum number of seals taken per day
(8) (Table 1). Therefore we believe this
approach is adequately precautionary
and reflects likely expected take. Using
this approach, a summary of estimated
takes of harbor seals incidental to the
proposed project activities are provided
in Table 2.
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TABLE 1—PHASE II HARBOR SEAL DISTURBANCE DATA—NUMBER OF SEALS EXPERIENCING LEVEL B HARASSMENT
Total
individuals
harassed 1
Date
Distance (m)
9/2/2020 ......................................................................................
9/8/2020 ......................................................................................
9/8/2020 ......................................................................................
9/9/2020 ......................................................................................
9/10/2020 ....................................................................................
9/15/2020 ....................................................................................
9/21/2020 ....................................................................................
9/21/2020 ....................................................................................
11/9/2020 ....................................................................................
3/17/2021 ....................................................................................
3/24/2021 ....................................................................................
3/24/2021 ....................................................................................
4/5/2021 ......................................................................................
4/5/2021 ......................................................................................
4/14/2021 ....................................................................................
9/2/2020 ......................................................................................
9/3/2020 ......................................................................................
9/8/2020 ......................................................................................
9/9/2020 ......................................................................................
300m ...........................................................................................
150m ...........................................................................................
150m ...........................................................................................
60m .............................................................................................
60m .............................................................................................
60m .............................................................................................
60m .............................................................................................
60m .............................................................................................
300m ...........................................................................................
200m ...........................................................................................
60m .............................................................................................
60m .............................................................................................
80m .............................................................................................
60m .............................................................................................
80m .............................................................................................
60m .............................................................................................
20m .............................................................................................
80m .............................................................................................
40m .............................................................................................
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0
0
0
0
0
1
0
2
1
5
1
1
2
1
2
0
1
8
0
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TABLE 1—PHASE II HARBOR SEAL DISTURBANCE DATA—NUMBER OF SEALS EXPERIENCING LEVEL B HARASSMENT—
Continued
Total
individuals
harassed 1
Date
Distance (m)
9/16/2020 ....................................................................................
9/22/2020 ....................................................................................
10/19/2020 ..................................................................................
10/28/2020 ..................................................................................
11/5/2020 ....................................................................................
12/3/2020 ....................................................................................
12/16/2020 ..................................................................................
5/4/2021 ......................................................................................
100m ...........................................................................................
40m .............................................................................................
40m .............................................................................................
100m ...........................................................................................
60m .............................................................................................
80m .............................................................................................
60m .............................................................................................
80m .............................................................................................
1
0
2
0
0
1
7
0
Total .....................................................................................
.....................................................................................................
36
1 ‘‘Total
Seals Taken’’ = the number of seals that moved or flushed during the incident. Alert responses are not considered to be takes.
TABLE 2—CALCULATED AND PROPOSED TAKE AND PERCENTAGE OF STOCK EXPOSED
Authorized take
Species
Level B
Pacific Harbor Seal ..
8 max seals taken per day 1 *(240 days 2) = 1920 ..........................................................
Percent of
stock 3
Level A
0
6.2
1 Maximum
number of seals harassed/taken in one day during Phase II.
of construction days at the Seal Bend Restoration Area.
from U.S. Pacific Marine Mammal Stock Assessments: 2014 (Carretta et al., 2015) (Abundance = 30,968).
2 Number
3 Data
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Proposed Mitigation, Monitoring and
Reporting Measures
In order to issue an IHA under section
101(a)(5)(D) of the MMPA, NMFS must
set forth the permissible methods of
taking pursuant to the activity, and
other means of effecting the least
practicable impact on the species or
stock and its habitat, paying particular
attention to rookeries, mating grounds,
and areas of similar significance, and on
the availability of the species or stock
for taking for certain subsistence uses
(latter not applicable for this action).
NMFS regulations require applicants for
incidental take authorizations to include
information about the availability and
feasibility (economic and technological)
of equipment, methods, and manner of
conducting the activity or other means
of effecting the least practicable adverse
impact upon the affected species or
stocks and their habitat (50 CFR
216.104(a)(11)).
In evaluating how mitigation may or
may not be appropriate to ensure the
least practicable adverse impact on
species or stocks and their habitat, as
well as subsistence uses where
applicable, we carefully consider two
primary factors:
(1) The manner in which, and the
degree to which, the successful
implementation of the measure(s) is
expected to reduce impacts to marine
mammals, marine mammal species or
stocks, and their habitat. This considers
the nature of the potential adverse
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impact being mitigated (likelihood,
scope, range). It further considers the
likelihood that the measure will be
effective if implemented (probability of
accomplishing the mitigating result if
implemented as planned), the
likelihood of effective implementation
(probability implemented as planned);
and
(2) The practicability of the measures
for applicant implementation, which
may consider such things as cost,
impact on operations, and, in the case
of a military readiness activity,
personnel safety, practicality of
implementation, and impact on the
effectiveness of the military readiness
activity.
Description of Proposed Mitigation
Some of the proposed mitigation
measures are identical to those included
in the Federal Register notification
announcing the final 2020 IHA and
detailed descriptions of these
requirements can be found in that
document. However, a few requirements
have been updated to reflect NMFS
more recent construction requirements
and those changes are discussed in
detail below and proposed for this
project:
Visual Monitoring—CDFW must
fulfill monitoring requirements as
described below. Required monitoring
must be conducted by dedicated,
trained, NMFS-approved Protected
Species Observer(s) (PSO(s)). CDFW
must monitor the project area to the
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maximum extent possible based on the
required number of PSOs, required
monitoring locations, and
environmental conditions.
• Level B Harassment Zone—PSOs
shall establish a Level B harassment
zone within 300 m of all construction
activities.
• When construction activities occur
either, (1) in water or; (2) within the
boundaries of the Seal Bend Restoration
Area (Phase III) identified in Figure 2,
monitoring must occur every other day
when work is occurring.
• When construction activities occur
near the ‘‘borrow’’ area where marsh fill
material is gathered, monitoring must
occur every fifth day when work is
occurring within 300 m from seal
haulouts or, if outside this area, when
work is occurring less than 200 m from
the water. Occurrence of marine
mammals within the Level B
harassment zone must be communicated
to the construction lead to prepare for
the potential shutdown when required.
Description of Proposed Monitoring and
Reporting
In order to issue an IHA 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 authorizations must include
the suggested means of accomplishing
the necessary monitoring and reporting
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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.
Effective reporting is critical both to
compliance as well as ensuring that the
most value is obtained from the required
monitoring.
Monitoring and reporting
requirements prescribed by NMFS
should contribute to improved
understanding of one or more of the
following:
• Occurrence of marine mammal
species or stocks in the area in which
take is anticipated (e.g., presence,
abundance, distribution, density);
• Nature, scope, or context of likely
marine mammal exposure to potential
stressors/impacts (individual or
cumulative, acute or chronic), through
better understanding of: (1) Action or
environment (e.g., source
characterization, propagation, ambient
noise); (2) affected species (e.g., life
history, dive patterns); (3) co-occurrence
of marine mammal species with the
action; or (4) biological or behavioral
context of exposure (e.g., age, calving or
feeding areas);
• Individual marine mammal
responses (behavioral or physiological)
to acoustic stressors (acute, chronic, or
cumulative), other stressors, or
cumulative impacts from multiple
stressors;
• How anticipated responses to
stressors impact either: (1) Long-term
fitness and survival of individual
marine mammals; or (2) populations,
species, or stocks;
• Effects on marine mammal habitat
(e.g., marine mammal prey species,
acoustic habitat, or other important
physical components of marine
mammal habitat); and
• Mitigation and monitoring
effectiveness.
Changes from the 2020 IHA include:
• 5(g)(v)(10): Notes should include
any of the following information to the
extent it is feasible to record:
Æ Age-class;
Æ Sex;
Æ Unusual activity or signs of stress;
Æ Activity of seals observed within
hour timeframe (e.g., resting, swimming,
etc.) and approximate number of seals
that have arrived or left since last hourly
count; and
Æ Any other information worth
noting;
• 6(a): The Holder must submit its
draft report(s) on all monitoring
conducted under this IHA within 90
calendar days of the completion of
monitoring or 60 calendar days prior to
the requested issuance of any
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subsequent IHA for construction activity
at the same location, whichever comes
first. A final report must be prepared
and submitted within 30 calendar days
following receipt of any NMFS
comments on the draft report. If no
comments are received from NMFS
within 30 calendar days of receipt of the
draft report, the report shall be
considered final.
The rest of proposed monitoring and
reporting measures are identical to those
included in the FR Notice announcing
the final 2020 IHA and detailed
descriptions of these requirements can
be found in that document.
Negligible Impact Analysis and
Determination
NMFS has defined negligible impact
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
(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 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 harassment, NMFS considers
other factors, such as the likely nature
of any responses (e.g., intensity,
duration), the context of any responses
(e.g., critical reproductive time or
location, migration), as well as effects
on habitat, and the likely effectiveness
of the mitigation. We also assess the
number, intensity, and context of
estimated takes by evaluating this
information relative to population
status. Consistent with the 1989
preamble for NMFS’s implementing
regulations (54 FR 40338; September 29,
1989), the impacts from other past and
ongoing anthropogenic activities are
incorporated into this analysis via their
impacts on the environmental baseline
(e.g., as reflected in the regulatory status
of the species, population size and
growth rate where known, ongoing
sources of human-caused mortality, or
ambient noise levels).
Construction activities associated
with this project have the potential to
disturb or displace marine mammals.
No serious injury or mortality is
expected, and with mitigation we expect
to avoid any potential for Level A
Harassment as a result of the Seal Bend
construction activities for Phase III. The
specified activities may result in take, in
the form of Level B harassment
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(behavioral disturbance) only, from
visual disturbance and/or noise from
construction activities. The project area
is within a portion of the local, year
round, habitat for harbor seals of the
greater Elkhorn Slough. Behavioral
disturbance associated with these
activities are expected to affect only a
small amount of the total population,
although those effects could be
recurring over the life of the project if
the same individuals remain in the
project vicinity. Harbor seals may avoid
the area or halt any behaviors (e.g.,
resting) when exposed to anthropogenic
noise or visual disturbance. Due to the
abundance of suitable and, in some
cases, newly restored haulout habitat
available in the greater Elkhorn Slough,
the short-term displacement of resting
harbor seals is not expected to affect the
overall fitness of any individual animal.
Effects on individuals that are taken
by Level B Harassment, on the basis of
reports in the literature as well as
monitoring from previous phases and
other similar activities, will likely be
limited to reactions such as
displacement from the area or
disturbance during resting. The
construction activities analyzed here,
such as equipment used, construction
approach, and turbidity management,
are the same as those activities
previously analyzed under the 2017 and
2020 IHAs. Both Phase I and Phase II of
the project reported no injuries or
mortality to marine mammals as a result
of the construction activities, and no
known long-term adverse consequences
from behavioral harassment have been
documented. Repeated exposures of
individuals to levels of noise or visual
disturbance at these levels, though they
may cause Level B Harassment, are
unlikely to result in hearing impairment
or significant disruption of foraging
behaviors. Many animals perform vital
functions, such as feeding, resting,
traveling, and socializing, on a diel
cycle (i.e., 24 hour cycle), and
behavioral reactions (such as disruption
of critical life functions, displacement,
or avoidance of important habitat) are
more likely to be significant if they last
more than one diel cycle or recur on
subsequent days (Southall et al., 2007).
However, Pacific harbor seals have been
hauling out at Elkhorn slough for
several years (including during pupping
season and while females are pregnant),
despite the presence of anthropogenic
noise and activities such as vessel
traffic, Union Pacific Railroad (UPRR)
trains, and human voices from kayaking
and recreational activities. Harbor seals
have repeatedly hauled out to rest
(inside and outside the project area) or
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pup (outside of the project area) despite
these potential stressors. The activities
are not expected to result in the
alteration of reproductive or feeding
behaviors. It is not likely that neonates
will be in the project area as females
prefer to keep their pups along the main
channel of Elkhorn Slough, which is
outside the area expected to be restored
by project activities (Figure 2). Seals are
primarily foraging outside of Elkhorn
Slough and at night in Monterey Bay,
outside the project area, and during
times when construction activities are
not occurring.
Pacific harbor seals, as the only
potentially affected marine mammal
species under NMFS jurisdiction in the
action area, are not listed as threatened
or endangered under the ESA and
NMFS SARs for this stock has shown to
be increasing in population size and is
considered stable (Caretta et al., 2015).
Even repeated Level B Harassment of
some small subset of the overall stock is
unlikely to result in any significant
decrease in viability for the affected
individuals, and thus will not result in
any adverse impacts to the stock as a
whole. The restoration of the marsh
habitat will have no adverse effect on
marine mammal habitat, but possibly a
long-term beneficial effect on harbor
seals by improving ecological function
of the slough, including higher species
diversity, increase species abundance,
larger fish, and improved habitat.
In summary and as described above,
the following factors primarily support
our preliminary determination that the
impacts resulting from this activity are
not expected to adversely affect the
species or stock through effects on
annual rates of recruitment or survival:
• No mortality is anticipated or
authorized;
• No Level A Harassment is
anticipated or authorized;
• Anticipated incidents of Level B
Harassment consist of, at worst,
temporary modifications in behavior;
• Primary foraging and reproductive
habitat are outside of the project area
and not expected to result in the
alteration of habitat important to these
behaviors or substantially impact the
behaviors themselves. There is
alternative haulout habitat just outside
the footprint of the construction area,
along the main channel of Elkhorn
Slough, and in Parson’s Slough, often
the preferred pupping grounds in recent
years (per comm Jim Harvey 2019), that
will be available for seals while some of
the haulouts are inaccessible;
• Restoration of the marsh habitat
will have no adverse effect on marine
mammal habitat, but possibly a longterm beneficial effect;
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• Presumed efficacy of the mitigation
measures in reducing the effects of the
specified activity to the level of least
practicable impact; and
• These stocks are not listed under
the ESA or considered depleted under
the MMPA.
In combination, we believe that these
factors, as well as the available body of
evidence from previous phases of the
project and other similar activities,
demonstrate that the potential effects of
the specified activities will have only
short-term effects on a relatively small
portion of the entire California stock.
The specified activities are not expected
to impact rates of recruitment or
survival and will therefore not result in
population-level impacts.
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 preliminarily finds
that the total marine mammal take from
the proposed activity will have a
negligible impact on all affected marine
mammal species or stocks.
Small Numbers
As noted above, only small numbers
of incidental take may be authorized
under sections 101(a)(5)(A) and (D) of
the MMPA for specified activities other
than military readiness activities. The
MMPA does not define small numbers
and so, in practice, where estimated
numbers are available, NMFS compares
the number of individuals taken to the
most appropriate estimation of
abundance of the relevant species or
stock in our determination of whether
an authorization is limited to small
numbers of marine mammals. When the
predicted number of individuals to be
taken is fewer than one third of the
species or stock abundance, the take is
considered to be of small numbers.
Additionally, other qualitative factors
may be considered in the analysis, such
as the temporal or spatial scale of the
activities.
For the proposed Phase III of the
Elkhorn Slough Tidal Marsh Restoration
Project, the authorized take (if we
conservatively assume that each take
occurred to a new animal, which is
unlikely) comprises approximately 6.2
percent of the abundance of Pacific
harbor seals in the California Stock.
Therefore, based on the analysis herein
of the proposed activity (including the
proposed mitigation and monitoring
measures) and the anticipated take of
marine mammals, NMFS preliminarily
finds that small numbers of marine
mammals will be taken relative to the
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43211
population size of the affected species
or stock.
Unmitigable Adverse Impact Analysis
and Determination
There are no relevant subsistence uses
of the affected marine mammal stock or
species implicated 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)
Section 7(a)(2) of the Endangered
Species Act of 1973 (ESA: 16. U.S.C.
1531 et seq.) requires that each Federal
agency insure that any action it
authorizes, funds, or carries out is not
likely to jeopardize the continued
existence of any endangered or
threatened species or result in the
destruction or adverse modification of
designated critical habitat. To ensure
ESA compliance for the issuance of
IHAs, NMFS consults internally
whenever we propose to authorize take
for endangered or threatened species.
No incidental take of ESA-listed
species is proposed for authorization or
expected to result from this activity in
the Elkhorn Slough Reserve. Therefore,
NMFS has determined that formal
consultation under section 7 of the ESA
is not required for this action.
Proposed Authorization
As a result of these preliminary
determinations, NMFS proposes to issue
an IHA to CDFW for conducting
restoration activities at the Seal Bend
Restoration Area in Elkhorn Slough
(Monterey County, CA) for 12 months
from the date of issuance, provided the
previously mentioned mitigation,
monitoring, and reporting requirements
are incorporated. A draft of the
proposed IHA can be found at https://
www.fisheries.noaa.gov/permit/
incidental-take-authorizations-undermarine-mammal-protection-act.
Request for Public Comments
We request comment on our analyses
(included in both this document and the
referenced documents supporting the
prior IHAs), the proposed authorization,
and any other aspect of this Notice of
Proposed IHA for the proposed Elkhorn
Slough Tidal Marsh Restoration Project,
Phase III, in Monterey County, CA. We
also request at this time comment on the
potential for renewal of this proposed
IHA as described in the paragraph
below. Please include with your
comments any supporting data or
literature citations to help inform our
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final decision on the request for MMPA
authorization.
On a case-by-case basis, NMFS may
issue a one-time, one-year Renewal IHA
following notice to the public providing
an additional 15 days for public
comments when (1) up to another year
of identical or nearly identical, or nearly
identical, activities as described in the
Detailed Description of Specific Activity
section of this notice is planned or (2)
the activities as described in the
Detailed Description of Specific Activity
section of this notice would not be
completed by the time the IHA expires
and a Renewal would allow for
completion of the activities beyond that
described in the Dates and Duration
section of this notice, provided all of the
following conditions are met:
• A request for renewal is received no
later than 60 days prior to the needed
Renewal IHA effective date (recognizing
that the Renewal IHA expiration date
cannot extend beyond one year from
expiration of the initial IHA);
• The request for renewal must
include the following:
(1) An explanation that the activities
to be conducted under the requested
Renewal IHA are identical to the
activities analyzed under the initial
IHA, are a subset of the activities, or
include changes so minor (e.g.,
reduction in pile size) that the changes
do not affect the previous analyses,
mitigation and monitoring
requirements, or take estimates (with
the exception of reducing the type or
amount of take); and
(2) A preliminary monitoring report
showing the results of the required
monitoring to date and an explanation
showing that the monitoring results do
not indicate impacts of a scale or nature
not previously analyzed or authorized;
and
• Upon review of the request for
Renewal, the status of the affected
species or stocks, and any other
pertinent information, NMFS
determines that there are no more than
minor changes in the activities, the
mitigation and monitoring measures
will remain the same and appropriate,
and the findings in the initial IHA
remain valid.
Dated: August 2, 2021.
Catherine Marzin,
Director, Office of Protected Resources,
National Marine Fisheries Service.
[FR Doc. 2021–16858 Filed 8–5–21; 8:45 am]
BILLING CODE 3510–22–P
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
[RTID 0648–XB227]
Takes of Marine Mammals Incidental to
Specified Activities; Taking Marine
Mammals Incidental to Marine Site
Characterization Surveys, Virginia and
North Carolina
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice; issuance of incidental
harassment authorization.
AGENCY:
In accordance with the
regulations implementing the Marine
Mammal Protection Act (MMPA) as
amended, notification is hereby given
that NMFS has issued an incidental
harassment authorization (IHA) to Kitty
Hawk Wind, LLC (Kitty Hawk Wind) to
incidentally harass, by Level B
harassment, marine mammals during
marine site characterization surveys
offshore Virginia and North Carolina.
DATES: The IHA is effective July 15,
2021 through October 31, 2021.
FOR FURTHER INFORMATION CONTACT:
Jaclyn Daly, Office of Protected
Resources, NMFS, (301) 427–8401.
Electronic copies of the application and
supporting documents, as well as a list
of the references cited in this document,
may be obtained online at: https://
www.fisheries.noaa.gov/permit/
incidental-take-authorizations-undermarine-mammal-protection-act. In case
of problems accessing these documents,
please call the contact listed above.
SUPPLEMENTARY INFORMATION:
SUMMARY:
Background
The MMPA prohibits the ‘‘take’’ of
marine mammals, with certain
exceptions. sections 101(a)(5)(A) and (D)
of the MMPA (16 U.S.C. 1361 et seq.)
direct the Secretary of Commerce (as
delegated to NMFS) 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
incidental take authorization may be
provided to the public for review.
Authorization for incidental takings
shall be granted if NMFS finds that the
taking will have a negligible impact on
the species or stock(s) and will not have
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an unmitigable adverse impact on the
availability of the species or stock(s) for
taking for subsistence uses (where
relevant). Further, NMFS must prescribe
the permissible methods of taking and
other ‘‘means of effecting the least
practicable adverse impact’’ on the
affected species or stocks and their
habitat, paying particular attention to
rookeries, mating grounds, and areas of
similar significance, and on the
availability of the species or stocks for
taking for certain subsistence uses
(referred to in shorthand as
‘‘mitigation’’); and requirements
pertaining to the mitigation, monitoring
and reporting of the takings are set forth.
Description of Proposed Activity
Overview
On April 27, 2021, NMFS received an
adequate and complete application from
Kitty Hawk Wind requesting an IHA
authorizing the take, by Level B
harassment only, of nine species of
marine mammals incidental to marine
site characterization surveys,
specifically in association with the use
of high-resolution geophysical (HRG)
survey equipment off North Carolina.
We note surveys will also occur off
Virginia; however, for reasons described
below, take of marine mammals
incidental to use of those surveys is not
expected to occur. The surveys will
support offshore wind development in
40 percent of the lease area (OCS–A
0508) in the northwest corner closest to
the North Carolina shoreline
(approximately 198 square kilometers
(km2)). Kitty Hawk Wind would use five
types of survey equipment; however, as
described below, only the Fugro SRP
EAH 2D sparker has the potential to
harass marine mammals. Exposure to
noise from the surveys may cause
behavioral changes in marine mammals
(e.g., avoidance, increased swim speeds,
etc.) rising to the level of take (Level B
harassment) as defined under the
MMPA. NMFS has issued the requested
IHA.
Dates and Duration
Kitty Hawk Wind would commence
the survey no earlier than July 15, with
the objective of completing the work by
September 31, 2021. The surveys would
cover approximately 3,300 km of survey
trackline over 25 days, not including
non-survey days likely needed for
weather down time. The IHA would be
effective from July 15 through October
31, 2021. Although the survey will
likely be completed by September 31,
2021, the additional month long
effective period will allow for any
unexpected weather delays while still
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[Federal Register Volume 86, Number 149 (Friday, August 6, 2021)]
[Notices]
[Pages 43204-43212]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2021-16858]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
[RTID 0648-XB270]
Takes of Marine Mammals Incidental To Specified Activities;
Taking Marine Mammals Incidental to Elkhorn Slough Tidal Marsh
Restoration Project, Phase III in Monterey County, California
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Notice; proposed issuance of an incidental harassment
authorization; request for comments.
-----------------------------------------------------------------------
SUMMARY: NMFS has received a request from the California Department of
Fish and Wildlife (CDFW) for authorization to take marine mammals
incidental to the Elkhorn slough Tidal Marsh Restoration Project (Phase
III) in Monterey County, CA. which includes the excavation and movement
of soil with heavy machinery for marsh restoration. NMFS is requesting
comments on its proposal to issue an incidental harassment
authorization (IHA) to incidentally take marine mammals during the
specified activities. NMFS is also requesting comments on a possible
one-time, one-year renewal that could be issued under certain
circumstances and if all requirements are met, as described in Request
for Public Comments at the end of this notice. NMFS will consider
public comments prior to making any final decision on the issuance of
the requested MMPA authorizations and agency responses will be
summarized in the final notice of our decision.
DATES: Comments and information must be received no later than
September 7, 2021.
ADDRESSES: Comments should be addressed to Jolie Harrison, Chief,
Permits and Conservation Division, Office of Protected Resources,
National Marine Fisheries Service. Written comments should be submitted
via email to [email protected].
Instructions: NMFS is not responsible for comments sent by any
other method, to any other address or individual, or received after the
end of the comment period. Comments, including all attachments, must
not exceed a 25-megabyte file size. Attachments to comments will be
accepted in Microsoft Word or Excel or Adobe PDF file formats only. All
comments received are a part of the public record and will generally be
posted online at https://
[[Page 43205]]
www.fisheries.noaa.gov/permit/incidental-take-authorizations-under-
marine-mammal-protection-act without change. All personal identifying
information (e.g., name, address) voluntarily submitted by the
commenter may be publicly accessible. Do not submit confidential
business information or otherwise sensitive or protected information.
FOR FURTHER INFORMATION CONTACT: Kim Corcoran, Office of Protected
Resources, NMFS, (301) 427-8401. Electronic copies of the original
application and supporting documents (including NMFS FR notices of the
prior authorizations), as well as a list of the references cited in
this document, may be obtained online at: https://www.fisheries.noaa.gov/permit/incidental-take-authorizations-under-marine-mammal-protection-act. In case of problems accessing these
documents, please call the contact listed above.
SUPPLEMENTARY INFORMATION:
Background
The MMPA prohibits the ``take'' of marine mammals, with certain
exceptions. Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361
et seq.) direct the Secretary of Commerce (as delegated to NMFS) 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 incidental take authorization may be provided to the public
for review.
Authorization for incidental takings shall be granted if NMFS finds
that the taking will have a negligible impact on the species or
stock(s) and will not have an unmitigable adverse impact on the
availability of the species or stock(s) for taking for subsistence uses
(where relevant). Further, NMFS must prescribe the permissible methods
of taking and other ``means of effecting the least practicable adverse
impact'' on the affected species or stocks and their habitat, paying
particular attention to rookeries, mating grounds, and areas of similar
significance, and on the availability of such species or stocks for
taking for certain subsistence uses (referred to in shorthand as
``mitigation''); and requirements pertaining to the mitigation,
monitoring and reporting of such takings are set forth.
The definitions of all applicable MMPA statutory terms cited above
are included in the relevant sections below.
National Environmental Policy Act
To comply with the National Environmental Policy Act of 1969 (NEPA;
42 U.S.C. 4321 et seq.) and NOAA Administrative Order (NAO) 216-6A,
NMFS must review our proposed action (i.e., the issuance of an IHA)
with respect to potential impacts on the human environment.
The current action is consistent with categories of activities
identified in Categorical Exclusion B4 (incidental harassment
authorizations with no anticipated serious injury or mortality) of the
Companion Manual for NOAA Administrative Order 216-6A, which do not
individually or cumulatively have the potential for significant impacts
on the quality of the human environment and for which we have not
identified any extraordinary circumstances that would preclude this
categorical exclusion. Accordingly, NMFS has preliminarily determined
that the issuance of the proposed renewal qualifies to be categorically
excluded from further NEPA review just as the initial IHA did.
We will review all comments submitted in response to this notice
prior to concluding our NEPA process or making a final decision on the
IHA request.
Summary of Request
On June 14, 2021, NMFS received a request from CDFW for an IHA to
take marine mammals incidental to the Elkhorn Slough Restoration
Project, Phase III, at the Seal Bend Restoration Area in Monterey
Country, CA. The application was deemed adequate and complete on July
27, 2021. CDFW's request is for take of a small number of Pacific
harbor seals (Phoca vitulina) by Level B harassment only. Neither CDFW
nor NMFS expects serious injury or mortality to result from this
activity and, therefore, an IHA is appropriate.
NMFS previously issued an IHA to CDFW for Phase I (82 FR 16800;
April 6, 2017) and Phase II (85 FR 14640; March 13, 2020) of the
Elkhorn Slough Restoration Project. Restoration work under the 2020 IHA
at the Minhoto-Hester and Seal Bend restoration areas was expected to
be completed within 180 days within the one-year timeframe of the IHA.
However, on May 3, 2021 CDFW informed NMFS that the estimated 180 days
of construction for both the Minhoto-Hester and Seal Bend Restoration
Areas would not be enough to complete the project. This preliminary
estimate did not adequately account for variable weather conditions
experienced during construction (e.g., wet weather and soils required
extensive reworking of fill), the amount of time to haul material from
the borrow area to the fill location, or contractor availability which
resulted in a smaller crew than initially expected. Therefore, only 118
days of construction occurred under the initial IHA. To cover the
remaining work at the Minhoto-Hester Restoration Area, CDFW requested
an IHA Renewal. NMFS published a notice of a proposed IHA Renewal and
request for comments in the Federal Register on June 8, 2021 to
complete the remaining 62 days of work (86 FR 30412; June 8, 2021)
(Hereafter referred to as the 2021 Renewal). We subsequently published
the final notice of our issuance of the IHA Renewal on July 7, 2021 (86
FR 35751).
As work at the Seal Bend Restoration Area had not begun and could
not be covered by the IHA Renewal, CDFW requested that a new IHA be
issued that would be valid for one year from the date of issuance.
Under this proposed IHA, CDFW would conduct 240 days of work to restore
28.6 acres (11.57 hectares) of tidal marsh habitat in the Seal Bend
Restoration Area. The project would include the use of haul trucks and
heavy earthmoving equipment to transport dry material out onto the
marsh. The proposed project activities will not differ from the 2020
IHA other than the number of construction days, and the means of
calculating take.
Description of the Proposed Activity
Overview
Over the past 150 years, human activities have altered the tidal,
freshwater, and sediment processes, which are essential to support and
sustain Elkhorn Slough's estuarine habitats. In response to years of
anthropogenic degradation (e.g., diking and marsh draining), the
Elkhorn Slough Tidal Marsh Restoration Project (project) plans to
restore approximately 122 acres (49.37 hectares) of tidal marsh across
three phases, all of which are located in Monterey County, California
(Figure 1). Phase I of the project, completed in 2018, restored 61
acres (24.69 hectares) of tidal marsh within the Minhoto-Hester Marsh
in Elkhorn Slough (Monterey, CA) (Figure 2) (82 FR 16800; April 06,
2017) (Hereafter referred to as the 2017 IHA). Phase II of the project,
planned for completion in September 2021, plans to restore 29.4 acres
(11.90 hectares) of tidal marsh at the Minhoto-Hester Restoration Area
adjacent to the Phase I Restoration Area (see Figure 2). As the
remainder of the
[[Page 43206]]
work associated with the project has not been completed and could not
be covered by the 2021 Renewal, CDFW requests that this proposed IHA
cover take incidental to Phase III of the project, which will restore
28.6 acres (11.57 hectares) at the Seal Bend Restoration Area shown in
Figure 2. Similar to previous projects, Phase III will relocate soil
from an upland area called ``the borrow'' through use of heavy earth
moving equipment, within a 12 month period. Construction activities are
expected to produce airborne noise and visual disturbance that have the
potential to result in behavioral harassment of Pacific harbor seals
(Phoca vitulina). NMFS is proposing to authorize take, by Level B
Harassment, of Pacfic harbor seals as a result of the specified
activity. To support public review and comment on the IHA that NMFS is
proposing to issue here, we refer to the documents related to the
previously issued IHA and discuss any new or changed information here.
The previous documents include the Federal Register notice of the
issuance of the 2020 IHA (85 FR 14640; March 13, 2020), the Federal
Register notice of the issuance of the 2021 IHA Renewal (86 FR 35751;
July 7, 2021), and all associated references and documents. We also
refer the reader to CDFW's previous and current applications and
monitoring reports which can be found at https://www.fisheries.noaa.gov/node/23111.
Dates and Duration
As previously mentioned, the Phase II IHA covered restoration work
at both the Minhoto-Hester Restoration Area and the Seal Bend
Restoration Area for 180 total days of construction but the work was
not able to be completed for both locations within the timeframe and
take estimate constraints of the 2020 IHA and 2021 Renewal IHA for the
reasons discussed above. Therefore, CDFW is requesting this new
authorization for 240 construction days to account for similar,
anticipated construction constraints at the Seal Bend Restoration Area,
such as likely wet weather, the distance between the borrow area and
restoration site, and limited contractor availability. CDFW is prepared
to start the work at Seal Bend as soon as they receive authorization,
so this IHA will be valid for one year from the date of issuance.
Specific Geographic Region
The project is located in the Elkhorn Slough estuary, about 90
miles south of San Francisco and 20 miles north of Monterey in Monterey
Country, California (Figure 1). The project sites are located on land
owned and operated by CDFW as part of the Elkhorn Slough Ecological and
National Estuarine Research Reserves. The waters of the Elkhorn Slough
State Marine Reserve and Monterey Bay National Marine Sanctuary run
north of the Phase III project site in Elkhorn Slough's main channel.
Two additional Marine Protected Areas are located within approximately
one mile of the project site: Elkhorn Slough State Marine Conservation
Area and Moro Cojo Slough State Marine Reserve.
Phase III would restore the Seal Bend Restoration Area which
includes about 28.6 acres (11.57 hectares) of historic farmland
adjacent to Elkhorn Slough and west of the Phase I and II restoration
areas (Figure 2). The proposed project area is low-lying area
consisting of subsided pickleweed (Salicornia) marsh, intertidal
mudflats, and tidal channels. Fill material for Seal Bend will be
obtained from a 38 acre (15.38 hectare) upland borrow area south of the
Minhoto-Hester (Phase II) Restoration Area (Figure 2). Once complete,
the slopes of the borrow area would be graded to increase marsh area
and create a gently sloping ecotone band along the edge of the Phase I
and II sites.
BILLING CODE 3510-22-P
[[Page 43207]]
[GRAPHIC] [TIFF OMITTED] TN06AU21.002
[[Page 43208]]
BILLING CODE 3510-22-C
Detailed Description of Specific Activity
As previously described, the proposed project would restore 28.6
acres (11.57 hectares) of tidal marsh habitat at the Seal Bend
Restoration Area. As described in more detail in the 2020 IHA, project
components to restore hydrologic function to the project area would
include raising the subsided marsh plain, maintaining or re-excavating
existing tidal channels, and restoring marsh plain, ecotone, and native
grassland habitat within a borrow/upland buffer area.
Up to 133,346 cubic yards (CY) (101950.33 cubic meters (CM)) of
soil will be obtained from the upland borrow area to raise the subsided
marsh plain to an average of 1.9 feet (0.58 m) above the current
height. This target elevation would allow emergent wetland vegetation
to naturally be reestablished. Sediment would be placed to a fill
elevation slightly higher than the target marsh plain elevation to
allow for settlement and consolidation of the underlying soils. After
construction is complete, the project would rely primarily on natural
vegetation recruitment in the restored marsh areas.
An additional detailed description of the proposed restoration
project is found in the proposed and issued 2020 IHA. The location and
nature of the activities, including the types of equipment planned for
use, are identical to those described in the previous notices.
Differences between the 2020 IHA and the proposed 2021-2022 IHA occur
in the number of days restoration work would occur, the method for
calculating take, and visual monitoring requirements, all of which are
discussed in detail below.
Description of Marine Mammals in the Area of Specified Activities
A description of the marine mammals in the area of the activities
is found in the 2020 IHA, which remains applicable to the proposed
2021-2022 IHA as well. In addition, NMFS has reviewed recent 2020 Stock
Assessment Reports, information on relevant Unusual Mortality Events,
and recent scientific literature, and determined that no new
information affects our original analysis of impacts under this
proposed IHA.
Potential Effects of Specified Activities on Marine Mammals and Their
Habitat
A description of the potential effects of the specified activities
on marine mammals and their habitat may be found in the documents
supporting the 2020 IHA, which remains applicable to the issuance of
the proposed 2021-2022 IHA. There is no new information on potential
effects.
Estimated Take
A detailed description of the previous methods and inputs used to
estimate authorized take is found in the 2020 IHA. The total number of
construction days and the method of estimating take have been modified
from the 2020 IHA to reflect construction delays as discussed above and
the monitoring data received under the 2020 IHA. The source levels and
marine mammal occurrence and density remain unchanged from the 2020 IHA
and detailed information regarding these figures can be found in the
proposed and issued 2020 IHA.
Take Calculation and Estimates
To repeat how take was calculated in the 2020 IHA, we used the
total number of seals taken during Phase I construction (i.e., 62
seals) divided by the sum of the daily average number of seals observed
hourly during Phase I. That percentage (8.79 percent) was rounded to 9
percent and multiplied by the sum of the highest daily count of seals
observed by the Reserve Otter Monitoring Projects at all observation
areas between January 2018 and April 2019 (i.e., 417). That number was
multiplied by the total number of construction days to arrive at the
total take estimate that was used.
For the Phase III project, we have additional monitoring data that
more accurately reflects the amount of take that occurs during this
type of restoration activity. In particular we now have data that
suggests the maximum number of seals taken per day within 300 m of
construction activity has been 8, which occurred on September 8, 2020
(Table 1). Therefore, we propose to use that maximum number of seals
taken per day to estimate take using the following formula:
Total Take Estimate = Max # of seals taken per day * # of Construction
Days
The average total individual takes per day for Phase II was 1.33
which is considerably lower than the proposed maximum number of seals
taken per day (8) (Table 1). Therefore we believe this approach is
adequately precautionary and reflects likely expected take. Using this
approach, a summary of estimated takes of harbor seals incidental to
the proposed project activities are provided in Table 2.
Table 1--Phase II Harbor Seal Disturbance Data--Number of Seals
Experiencing Level B Harassment
------------------------------------------------------------------------
Total
Date Distance (m) individuals
harassed \1\
------------------------------------------------------------------------
9/2/2020.......................... 300m................ 0
9/8/2020.......................... 150m................ 0
9/8/2020.......................... 150m................ 0
9/9/2020.......................... 60m................. 0
9/10/2020......................... 60m................. 0
9/15/2020......................... 60m................. 1
9/21/2020......................... 60m................. 0
9/21/2020......................... 60m................. 2
11/9/2020......................... 300m................ 1
3/17/2021......................... 200m................ 5
3/24/2021......................... 60m................. 1
3/24/2021......................... 60m................. 1
4/5/2021.......................... 80m................. 2
4/5/2021.......................... 60m................. 1
4/14/2021......................... 80m................. 2
9/2/2020.......................... 60m................. 0
9/3/2020.......................... 20m................. 1
9/8/2020.......................... 80m................. 8
9/9/2020.......................... 40m................. 0
[[Page 43209]]
9/16/2020......................... 100m................ 1
9/22/2020......................... 40m................. 0
10/19/2020........................ 40m................. 2
10/28/2020........................ 100m................ 0
11/5/2020......................... 60m................. 0
12/3/2020......................... 80m................. 1
12/16/2020........................ 60m................. 7
5/4/2021.......................... 80m................. 0
---------------
Total......................... .................... 36
------------------------------------------------------------------------
\1\ ``Total Seals Taken'' = the number of seals that moved or flushed
during the incident. Alert responses are not considered to be takes.
Table 2--Calculated and Proposed Take and Percentage of Stock Exposed
----------------------------------------------------------------------------------------------------------------
Authorized take
-----------------------------------------------------------------------------------------------------------------
Percent of
Species Level B Level A stock \3\
----------------------------------------------------------------------------------------------------------------
Pacific Harbor Seal........................ 8 max seals taken per day \1\ *(240 0 6.2
days \2\) = 1920.
----------------------------------------------------------------------------------------------------------------
\1\ Maximum number of seals harassed/taken in one day during Phase II.
\2\ Number of construction days at the Seal Bend Restoration Area.
\3\ Data from U.S. Pacific Marine Mammal Stock Assessments: 2014 (Carretta et al., 2015) (Abundance = 30,968).
Proposed Mitigation, Monitoring and Reporting Measures
In order to issue an IHA under section 101(a)(5)(D) of the MMPA,
NMFS must set forth the permissible methods of taking pursuant to the
activity, and other means of effecting the least practicable impact on
the species or stock and its habitat, paying particular attention to
rookeries, mating grounds, and areas of similar significance, and on
the availability of the species or stock for taking for certain
subsistence uses (latter not applicable for this action). NMFS
regulations require applicants for incidental take authorizations to
include information about the availability and feasibility (economic
and technological) of equipment, methods, and manner of conducting the
activity or other means of effecting the least practicable adverse
impact upon the affected species or stocks and their habitat (50 CFR
216.104(a)(11)).
In evaluating how mitigation may or may not be appropriate to
ensure the least practicable adverse impact on species or stocks and
their habitat, as well as subsistence uses where applicable, we
carefully consider two primary factors:
(1) The manner in which, and the degree to which, the successful
implementation of the measure(s) is expected to reduce impacts to
marine mammals, marine mammal species or stocks, and their habitat.
This considers the nature of the potential adverse impact being
mitigated (likelihood, scope, range). It further considers the
likelihood that the measure will be effective if implemented
(probability of accomplishing the mitigating result if implemented as
planned), the likelihood of effective implementation (probability
implemented as planned); and
(2) The practicability of the measures for applicant
implementation, which may consider such things as cost, impact on
operations, and, in the case of a military readiness activity,
personnel safety, practicality of implementation, and impact on the
effectiveness of the military readiness activity.
Description of Proposed Mitigation
Some of the proposed mitigation measures are identical to those
included in the Federal Register notification announcing the final 2020
IHA and detailed descriptions of these requirements can be found in
that document. However, a few requirements have been updated to reflect
NMFS more recent construction requirements and those changes are
discussed in detail below and proposed for this project:
Visual Monitoring--CDFW must fulfill monitoring requirements as
described below. Required monitoring must be conducted by dedicated,
trained, NMFS-approved Protected Species Observer(s) (PSO(s)). CDFW
must monitor the project area to the maximum extent possible based on
the required number of PSOs, required monitoring locations, and
environmental conditions.
Level B Harassment Zone--PSOs shall establish a Level B
harassment zone within 300 m of all construction activities.
When construction activities occur either, (1) in water
or; (2) within the boundaries of the Seal Bend Restoration Area (Phase
III) identified in Figure 2, monitoring must occur every other day when
work is occurring.
When construction activities occur near the ``borrow''
area where marsh fill material is gathered, monitoring must occur every
fifth day when work is occurring within 300 m from seal haulouts or, if
outside this area, when work is occurring less than 200 m from the
water. Occurrence of marine mammals within the Level B harassment zone
must be communicated to the construction lead to prepare for the
potential shutdown when required.
Description of Proposed Monitoring and Reporting
In order to issue an IHA 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
authorizations must include the suggested means of accomplishing the
necessary monitoring and reporting
[[Page 43210]]
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. Effective reporting is
critical both to compliance as well as ensuring that the most value is
obtained from the required monitoring.
Monitoring and reporting requirements prescribed by NMFS should
contribute to improved understanding of one or more of the following:
Occurrence of marine mammal species or stocks in the area
in which take is anticipated (e.g., presence, abundance, distribution,
density);
Nature, scope, or context of likely marine mammal exposure
to potential stressors/impacts (individual or cumulative, acute or
chronic), through better understanding of: (1) Action or environment
(e.g., source characterization, propagation, ambient noise); (2)
affected species (e.g., life history, dive patterns); (3) co-occurrence
of marine mammal species with the action; or (4) biological or
behavioral context of exposure (e.g., age, calving or feeding areas);
Individual marine mammal responses (behavioral or
physiological) to acoustic stressors (acute, chronic, or cumulative),
other stressors, or cumulative impacts from multiple stressors;
How anticipated responses to stressors impact either: (1)
Long-term fitness and survival of individual marine mammals; or (2)
populations, species, or stocks;
Effects on marine mammal habitat (e.g., marine mammal prey
species, acoustic habitat, or other important physical components of
marine mammal habitat); and
Mitigation and monitoring effectiveness.
Changes from the 2020 IHA include:
5(g)(v)(10): Notes should include any of the following
information to the extent it is feasible to record:
[cir] Age-class;
[cir] Sex;
[cir] Unusual activity or signs of stress;
[cir] Activity of seals observed within hour timeframe (e.g.,
resting, swimming, etc.) and approximate number of seals that have
arrived or left since last hourly count; and
[cir] Any other information worth noting;
6(a): The Holder must submit its draft report(s) on all
monitoring conducted under this IHA within 90 calendar days of the
completion of monitoring or 60 calendar days prior to the requested
issuance of any subsequent IHA for construction activity at the same
location, whichever comes first. A final report must be prepared and
submitted within 30 calendar days following receipt of any NMFS
comments on the draft report. If no comments are received from NMFS
within 30 calendar days of receipt of the draft report, the report
shall be considered final.
The rest of proposed monitoring and reporting measures are
identical to those included in the FR Notice announcing the final 2020
IHA and detailed descriptions of these requirements can be found in
that document.
Negligible Impact Analysis and Determination
NMFS has defined negligible impact 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 (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 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 harassment, NMFS considers other factors, such as the
likely nature of any responses (e.g., intensity, duration), the context
of any responses (e.g., critical reproductive time or location,
migration), as well as effects on habitat, and the likely effectiveness
of the mitigation. We also assess the number, intensity, and context of
estimated takes by evaluating this information relative to population
status. Consistent with the 1989 preamble for NMFS's implementing
regulations (54 FR 40338; September 29, 1989), the impacts from other
past and ongoing anthropogenic activities are incorporated into this
analysis via their impacts on the environmental baseline (e.g., as
reflected in the regulatory status of the species, population size and
growth rate where known, ongoing sources of human-caused mortality, or
ambient noise levels).
Construction activities associated with this project have the
potential to disturb or displace marine mammals. No serious injury or
mortality is expected, and with mitigation we expect to avoid any
potential for Level A Harassment as a result of the Seal Bend
construction activities for Phase III. The specified activities may
result in take, in the form of Level B harassment (behavioral
disturbance) only, from visual disturbance and/or noise from
construction activities. The project area is within a portion of the
local, year round, habitat for harbor seals of the greater Elkhorn
Slough. Behavioral disturbance associated with these activities are
expected to affect only a small amount of the total population,
although those effects could be recurring over the life of the project
if the same individuals remain in the project vicinity. Harbor seals
may avoid the area or halt any behaviors (e.g., resting) when exposed
to anthropogenic noise or visual disturbance. Due to the abundance of
suitable and, in some cases, newly restored haulout habitat available
in the greater Elkhorn Slough, the short-term displacement of resting
harbor seals is not expected to affect the overall fitness of any
individual animal.
Effects on individuals that are taken by Level B Harassment, on the
basis of reports in the literature as well as monitoring from previous
phases and other similar activities, will likely be limited to
reactions such as displacement from the area or disturbance during
resting. The construction activities analyzed here, such as equipment
used, construction approach, and turbidity management, are the same as
those activities previously analyzed under the 2017 and 2020 IHAs. Both
Phase I and Phase II of the project reported no injuries or mortality
to marine mammals as a result of the construction activities, and no
known long-term adverse consequences from behavioral harassment have
been documented. Repeated exposures of individuals to levels of noise
or visual disturbance at these levels, though they may cause Level B
Harassment, are unlikely to result in hearing impairment or significant
disruption of foraging behaviors. Many animals perform vital functions,
such as feeding, resting, traveling, and socializing, on a diel cycle
(i.e., 24 hour cycle), and behavioral reactions (such as disruption of
critical life functions, displacement, or avoidance of important
habitat) are more likely to be significant if they last more than one
diel cycle or recur on subsequent days (Southall et al., 2007).
However, Pacific harbor seals have been hauling out at Elkhorn slough
for several years (including during pupping season and while females
are pregnant), despite the presence of anthropogenic noise and
activities such as vessel traffic, Union Pacific Railroad (UPRR)
trains, and human voices from kayaking and recreational activities.
Harbor seals have repeatedly hauled out to rest (inside and outside the
project area) or
[[Page 43211]]
pup (outside of the project area) despite these potential stressors.
The activities are not expected to result in the alteration of
reproductive or feeding behaviors. It is not likely that neonates will
be in the project area as females prefer to keep their pups along the
main channel of Elkhorn Slough, which is outside the area expected to
be restored by project activities (Figure 2). Seals are primarily
foraging outside of Elkhorn Slough and at night in Monterey Bay,
outside the project area, and during times when construction activities
are not occurring.
Pacific harbor seals, as the only potentially affected marine
mammal species under NMFS jurisdiction in the action area, are not
listed as threatened or endangered under the ESA and NMFS SARs for this
stock has shown to be increasing in population size and is considered
stable (Caretta et al., 2015). Even repeated Level B Harassment of some
small subset of the overall stock is unlikely to result in any
significant decrease in viability for the affected individuals, and
thus will not result in any adverse impacts to the stock as a whole.
The restoration of the marsh habitat will have no adverse effect on
marine mammal habitat, but possibly a long-term beneficial effect on
harbor seals by improving ecological function of the slough, including
higher species diversity, increase species abundance, larger fish, and
improved habitat.
In summary and as described above, the following factors primarily
support our preliminary determination that the impacts resulting from
this activity are not expected to adversely affect the species or stock
through effects on annual rates of recruitment or survival:
No mortality is anticipated or authorized;
No Level A Harassment is anticipated or authorized;
Anticipated incidents of Level B Harassment consist of, at
worst, temporary modifications in behavior;
Primary foraging and reproductive habitat are outside of
the project area and not expected to result in the alteration of
habitat important to these behaviors or substantially impact the
behaviors themselves. There is alternative haulout habitat just outside
the footprint of the construction area, along the main channel of
Elkhorn Slough, and in Parson's Slough, often the preferred pupping
grounds in recent years (per comm Jim Harvey 2019), that will be
available for seals while some of the haulouts are inaccessible;
Restoration of the marsh habitat will have no adverse
effect on marine mammal habitat, but possibly a long-term beneficial
effect;
Presumed efficacy of the mitigation measures in reducing
the effects of the specified activity to the level of least practicable
impact; and
These stocks are not listed under the ESA or considered
depleted under the MMPA.
In combination, we believe that these factors, as well as the
available body of evidence from previous phases of the project and
other similar activities, demonstrate that the potential effects of the
specified activities will have only short-term effects on a relatively
small portion of the entire California stock. The specified activities
are not expected to impact rates of recruitment or survival and will
therefore not result in population-level impacts.
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 preliminarily finds that the total marine
mammal take from the proposed activity will have a negligible impact on
all affected marine mammal species or stocks.
Small Numbers
As noted above, only small numbers of incidental take may be
authorized under sections 101(a)(5)(A) and (D) of the MMPA for
specified activities other than military readiness activities. The MMPA
does not define small numbers and so, in practice, where estimated
numbers are available, NMFS compares the number of individuals taken to
the most appropriate estimation of abundance of the relevant species or
stock in our determination of whether an authorization is limited to
small numbers of marine mammals. When the predicted number of
individuals to be taken is fewer than one third of the species or stock
abundance, the take is considered to be of small numbers. Additionally,
other qualitative factors may be considered in the analysis, such as
the temporal or spatial scale of the activities.
For the proposed Phase III of the Elkhorn Slough Tidal Marsh
Restoration Project, the authorized take (if we conservatively assume
that each take occurred to a new animal, which is unlikely) comprises
approximately 6.2 percent of the abundance of Pacific harbor seals in
the California Stock. Therefore, based on the analysis herein of the
proposed activity (including the proposed mitigation and monitoring
measures) and the anticipated take of marine mammals, NMFS
preliminarily finds that small numbers of marine mammals will be taken
relative to the population size of the affected species or stock.
Unmitigable Adverse Impact Analysis and Determination
There are no relevant subsistence uses of the affected marine
mammal stock or species implicated 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)
Section 7(a)(2) of the Endangered Species Act of 1973 (ESA: 16.
U.S.C. 1531 et seq.) requires that each Federal agency insure that any
action it authorizes, funds, or carries out is not likely to jeopardize
the continued existence of any endangered or threatened species or
result in the destruction or adverse modification of designated
critical habitat. To ensure ESA compliance for the issuance of IHAs,
NMFS consults internally whenever we propose to authorize take for
endangered or threatened species.
No incidental take of ESA-listed species is proposed for
authorization or expected to result from this activity in the Elkhorn
Slough Reserve. Therefore, NMFS has determined that formal consultation
under section 7 of the ESA is not required for this action.
Proposed Authorization
As a result of these preliminary determinations, NMFS proposes to
issue an IHA to CDFW for conducting restoration activities at the Seal
Bend Restoration Area in Elkhorn Slough (Monterey County, CA) for 12
months from the date of issuance, provided the previously mentioned
mitigation, monitoring, and reporting requirements are incorporated. A
draft of the proposed IHA can be found at https://www.fisheries.noaa.gov/permit/incidental-take-authorizations-under-marine-mammal-protection-act.
Request for Public Comments
We request comment on our analyses (included in both this document
and the referenced documents supporting the prior IHAs), the proposed
authorization, and any other aspect of this Notice of Proposed IHA for
the proposed Elkhorn Slough Tidal Marsh Restoration Project, Phase III,
in Monterey County, CA. We also request at this time comment on the
potential for renewal of this proposed IHA as described in the
paragraph below. Please include with your comments any supporting data
or literature citations to help inform our
[[Page 43212]]
final decision on the request for MMPA authorization.
On a case-by-case basis, NMFS may issue a one-time, one-year
Renewal IHA following notice to the public providing an additional 15
days for public comments when (1) up to another year of identical or
nearly identical, or nearly identical, activities as described in the
Detailed Description of Specific Activity section of this notice is
planned or (2) the activities as described in the Detailed Description
of Specific Activity section of this notice would not be completed by
the time the IHA expires and a Renewal would allow for completion of
the activities beyond that described in the Dates and Duration section
of this notice, provided all of the following conditions are met:
A request for renewal is received no later than 60 days
prior to the needed Renewal IHA effective date (recognizing that the
Renewal IHA expiration date cannot extend beyond one year from
expiration of the initial IHA);
The request for renewal must include the following:
(1) An explanation that the activities to be conducted under the
requested Renewal IHA are identical to the activities analyzed under
the initial IHA, are a subset of the activities, or include changes so
minor (e.g., reduction in pile size) that the changes do not affect the
previous analyses, mitigation and monitoring requirements, or take
estimates (with the exception of reducing the type or amount of take);
and
(2) A preliminary monitoring report showing the results of the
required monitoring to date and an explanation showing that the
monitoring results do not indicate impacts of a scale or nature not
previously analyzed or authorized; and
Upon review of the request for Renewal, the status of the
affected species or stocks, and any other pertinent information, NMFS
determines that there are no more than minor changes in the activities,
the mitigation and monitoring measures will remain the same and
appropriate, and the findings in the initial IHA remain valid.
Dated: August 2, 2021.
Catherine Marzin,
Director, Office of Protected Resources, National Marine Fisheries
Service.
[FR Doc. 2021-16858 Filed 8-5-21; 8:45 am]
BILLING CODE 3510-22-P