Takes of Marine Mammals Incidental to Specified Activities; Taking Marine Mammals Incidental to Rocky Intertidal Monitoring Surveys Along the Oregon and California Coasts, 73048-73053 [2014-28807]
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Federal Register / Vol. 79, No. 236 / Tuesday, December 9, 2014 / Notices
Port group
Halibut
standard
ex-vessel price
Period ending
November 30 ................................................................
Sablefish
standard
ex-vessel price
6.50
3.92
1. Note:
In many instances prices have not been reported to comply with confidentiality guidelines that prevent price reports when there are
fewer than three processors operating in a location during a month.
2. Landing locations Within Port Group—Bering Sea: Adak, Akutan, Akutan Bay, Atka, Bristol Bay, Chefornak, Dillingham, Captains Bay, Dutch
Harbor, Egegik, Ikatan Bay, Hooper Bay, King Cove, King Salmon, Kipnuk, Mekoryuk, Naknek, Nome, Quinhagak, Savoonga, St. George, St.
Lawrence, St. Paul, Togiak, Toksook Bay, Tununak, Beaver Inlet, Ugadaga Bay, Unalaska.
3. Landing Locations Within Port Group—Central Gulf of Alaska: Anchor Point, Anchorage, Alitak, Chignik, Cordova, Eagle River, False Pass,
West Anchor Cove, Girdwood, Chinitna Bay, Halibut Cove, Homer, Kasilof, Kenai, Kenai River, Alitak, Kodiak, Port Bailey, Nikiski, Ninilchik, Old
Harbor, Palmer, Sand Point, Seldovia, Resurrection Bay, Seward, Valdez, Whittier.
4. Landing Locations Within Port Group—Southeast Alaska: Angoon, Baranof Warm Springs, Craig, Edna Bay, Elfin Cove, Excursion Inlet,
Gustavus, Haines, Hollis, Hoonah, Hyder, Auke Bay, Douglas, Tee Harbor, Juneau, Kake, Ketchikan, Klawock, Metlakatla, Pelican, Petersburg,
Portage Bay, Port Alexander, Port Graham, Port Protection, Point Baker, Sitka, Skagway, Tenakee Springs, Thorne Bay, Wrangell, Yakutat.
5. Landing Locations Within Port Group—All: For Alaska: All landing locations included in 2, 3, and 4. For California: Eureka, Fort Bragg, Other
California. For Oregon: Astoria, Aurora, Lincoln City, Newport, Warrenton, Other Oregon. For Washington: Anacortes, Bellevue, Bellingham,
Nagai Island, Edmonds, Everett, Granite Falls, Ilwaco, La Conner, Port Angeles, Port Orchard, Port Townsend, Ranier, Fox Island, Mercer Island, Seattle, Standwood, Other Washington. For Canada: Port Hardy, Port Edward, Prince Rupert, Vancouver, Haines Junction, Other Canada.
Authority: 16 U.S.C. 1801 et seq.
Dated: December 3, 2014.
Alan D. Risenhoover,
Director, Office of Sustainable Fisheries,
National Marine Fisheries Service.
[FR Doc. 2014–28724 Filed 12–8–14; 8:45 am]
BILLING CODE 3510–22–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
RIN 0648–XD531
Takes of Marine Mammals Incidental to
Specified Activities; Taking Marine
Mammals Incidental to Rocky Intertidal
Monitoring Surveys Along the Oregon
and California Coasts
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice; issuance of an incidental
harassment authorization.
AGENCY:
In accordance with the
Marine Mammal Protection Act
(MMPA) regulations, notification is
hereby given that NMFS has issued an
Incidental Harassment Authorization
(IHA) to the Partnership for
Interdisciplinary Study of Coastal
Oceans (PISCO) at the University of
California (UC) Santa Cruz for an
Incidental Harassment Authorization
(IHA) to take marine mammals, by
harassment, incidental to rocky
intertidal monitoring surveys.
DATES: Effective December 17, 2014,
through December 16, 2015.
ADDRESSES: A copy of the authorization,
application, and associated
Environmental Assessment (EA) and
Finding of No Significant Impact
(FONSI) may be obtained by writing to
Jolie Harrison, Chief, Permits and
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SUMMARY:
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Conservation Division, Office of
Protected Resources, National Marine
Fisheries Service, 1315 East-West
Highway, Silver Spring, MD 20910,
telephoning the contact listed below
(see FOR FURTHER INFORMATION CONTACT),
or visiting the internet at: https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm. Documents cited in this
notice may also be viewed, by
appointment, during regular business
hours, at the aforementioned address.
FOR FURTHER INFORMATION CONTACT:
Robert Pauline, Office of Protected
Resources, NMFS, (301) 427–8401.
SUPPLEMENTARY INFORMATION:
Background
Sections 101(a)(5)(A) and (D) of the
MMPA (16 U.S.C. 1361 et seq.) direct
the Secretary of Commerce to allow,
upon request, the incidental, but not
intentional, taking of small numbers of
marine mammals by U.S. citizens who
engage in a specified activity (other than
commercial fishing) within a specified
geographical region if certain findings
are made and either regulations are
issued or, if the taking is limited to
harassment, a notice of a proposed
authorization is provided to the public
for review.
Authorization for incidental takings
shall be granted if NMFS finds that the
taking will have a negligible impact on
the species or stock(s), will not have an
unmitigable adverse impact on the
availability of the species or stock(s) for
subsistence uses (where relevant), and if
the permissible methods of taking, other
means of effecting the least practicable
impact on the species or stock and its
habitat, and requirements pertaining to
the mitigation, monitoring and reporting
of such takings are set forth. NMFS has
defined ‘‘negligible impact’’ in 50 CFR
216.103 as ‘‘. . . an impact resulting
from the specified activity that cannot
be reasonably expected to, and is not
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reasonably likely to, adversely affect the
species or stock through effects on
annual rates of recruitment or survival.’’
Section 101(a)(5)(D) of the MMPA
established an expedited process by
which citizens of the United States can
apply for an authorization to
incidentally take small numbers of
marine mammals by harassment.
Section 101(a)(5)(D) establishes a 45-day
time limit for NMFS review of an
application followed by a 30-day public
notice and comment period on any
proposed authorizations for the
incidental harassment of marine
mammals. Within 45 days of the close
of the comment period, NMFS must
either issue or deny the authorization.
Except with respect to certain activities
not pertinent here, the MMPA defines
‘‘harassment’’ as: ‘‘any act of pursuit,
torment, or annoyance which (i) has the
potential to injure a marine mammal or
marine mammal stock in the wild [Level
A harassment]; or (ii) has the potential
to disturb a marine mammal or marine
mammal stock in the wild by causing
disruption of behavioral patterns,
including, but not limited to, migration,
breathing, nursing, breeding, feeding, or
sheltering [Level B harassment].’’
Summary of Request
On July 30, 2014, NMFS received an
application from PISCO for the taking of
marine mammals incidental to rocky
intertidal monitoring surveys along the
Oregon and California coasts. NMFS
determined that the application was
adequate and complete on August 22,
2014. On October 8, 2014, we published
a notice in the Federal Register of our
proposal to issue an IHA with
preliminary determinations and
explained the basis for the proposal and
preliminary determinations (78 FR
64918). The notice initiated a 30-day
public comment period. Responses are
discussed below. In December 2012,
NMFS issued a 1-year IHA to PISCO to
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take marine mammals incidental to
these same proposed activities (77 FR
72327, December 5, 2012). That IHA
expired on December 2, 2013. In
December 2013 NMFS issued another 1
year IHA to PISCO to take marine
mammals incidental to continuation of
proposed activities which expires on
December 16, 2014 (78 FR 79403,
December 30, 2013).
The research group at UC Santa Cruz
operates in collaboration with two largescale marine research programs: PISCO
and the Multi-agency Rocky Intertidal
Network. The research group at UC
Santa Cruz (PISCO) is responsible for
many of the ongoing rocky intertidal
monitoring programs along the Pacific
coast. Monitoring occurs at rocky
intertidal sites, often large bedrock
benches, from the high intertidal to the
water’s edge. Long-term monitoring
projects include Community Structure
Monitoring, Intertidal Biodiversity
Surveys, Marine Protected Area
Baseline Monitoring, Intertidal
Recruitment Monitoring, and Ocean
Acidification. Research is conducted
throughout the year along the California
and Oregon coasts and will continue
indefinitely. Most sites are sampled one
to two times per year over a 4–6 hour
period during a negative low tide series.
This IHA is only effective for a 12month period. The following specific
aspects of the proposed activities are
likely to result in the take of marine
mammals: Presence of survey personnel
near pinniped haulout sites and
approach of survey personnel towards
hauled out pinnipeds. Take, by Level B
harassment only, of individuals of three
species of marine mammals is
anticipated to result from the specified
activity.
Description of the Specified Activity
and Specified Geographic Region
PISCO focuses on understanding the
nearshore ecosystems of the U.S. west
coast through a number of
interdisciplinary collaborations. PISCO
integrates long-term monitoring of
ecological and oceanographic processes
at dozens of sites with experimental
work in the lab and field. A short
description of each project is contained
here. Additional information can be
found in PISCO’s application (see
ADDRESSES) and the Notice of Proposed
IHA (79 FR 60831, October 8, 2014).
Community Structure Monitoring
involves the use of permanent photoplot
quadrats which target specific algal and
invertebrate assemblages (e.g. mussels,
rockweeds, barnacles). This project
provides managers with insight into the
causes and consequences of changes in
species abundance. Each Community
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Structure site is surveyed over a 1-day
period during a low tide series one to
two times a year. Sites, location, number
of times sampled per year, and typical
sampling months for each site are
presented in Table 1 in PISCO’s
application (see ADDRESSES).
Biodiversity Surveys, which are part
of a long-term monitoring project and
are conducted every 3–5 years at
established sites, involve point contact
identification along permanent
transects, mobile invertebrate quadrat
counts, sea star band counts, and tidal
height topographic measurements. Table
2 in PISCO’s application (see
ADDRESSES) lists established
biodiversity sites in Oregon and
California.
In September 2007, the state of
California began establishing a network
of Marine Protected Areas along the
California coast as part of the Marine
Life Protection Act (MLPA). Under
baseline monitoring programs funded by
Sea Grant and the Ocean Protection
Council, PISCO established additional
intertidal monitoring sites in the Central
Coast, North Central Coast, and South
Coast study regions. Six additional sites
will be established and sampled in the
North Coast study region during 2015
(see Table 3 in PISCO’s application).
Baseline characterization of newly
established areas involves sampling of
these new sites, as well as established
sites both within and outside of marine
protected areas. These sites were
sampled using existing Community
Structure and Biodiversity protocols for
consistency. Resampling of these sites
may take place as part of future marine
protected area evaluation.
Specified Geographic Location and
Activity Timeframe
PISCO’s research is conducted
throughout the year along the California
and Oregon coasts. Most sites are
sampled one to two times per year over
a 1-day period (4–6 hours per site)
during a negative low tide series. Due to
the large number of research sites,
scheduling constraints, the necessity for
negative low tides and favorable
weather/ocean conditions, exact survey
dates are variable and difficult to
predict. Some sampling is anticipated to
occur in all months, except for January,
August, and September.
The intertidal zones where PISCO
conducts intertidal monitoring are also
areas where pinnipeds can be found
hauled out on the shore at or adjacent
to some research sites. Accessing
portions of the intertidal habitat may
cause incidental Level B (behavioral)
harassment of pinnipeds through some
unavoidable approaches if pinnipeds
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are hauled out directly in the study
plots or while biologists walk from one
location to another. No motorized
equipment is involved in conducting
these surveys. The species for which
Level B harassment is requested are:
California sea lions (Zalophus
californianus californianus); harbor
seals (Phoca vitulina richardii); and
northern elephant seals (Mirounga
angustirostris).
Comments and Responses
A Notice of Proposed IHA was
published in the Federal Register on
October 8, 2014 (79 FR 60831) for public
comment. During the 30-day public
comment period, NMFS received one
letter from the Marine Mammal
Commission. No other organizations
provided comments on the proposed
issuance of an IHA for this activity. The
Marine Mammal Commission
recommended that NMFS issue the IHA,
subject to inclusion of the proposed
mitigation and monitoring measures.
NMFS has included all of the mitigation
and monitoring measures proposed in
the Notice of Proposed IHA (79 FR
60831, October 8, 2014) in the issued
IHA.
Description of Marine Mammals in the
Area of the Specified Activity
Several pinniped species can be
found along the California and Oregon
coasts. The three that are most likely to
occur at some of the research sites are
California sea lion, harbor seal, and
northern elephant seal. On rare
occasions, PISCO researchers have seen
very small numbers (i.e., five or fewer)
of Steller sea lions at one of the
sampling sites. These sightings are rare.
Therefore, encounters are not expected.
However, if Steller sea lions are sighted
before approaching a sampling site,
researchers will abandon approach and
return at a later date. For this reason,
this species is not considered further in
this IHA notice.
We refer the public to Carretta et al.
(2014) for general information on these
species. The publication is available on
the internet at: https://
www.nmfs.noaa.gov/pr/sars/pdf/
pacific2013_final.pdf. Additional
information on the status, distribution,
seasonal distribution, and life history
can also be found in PISCO’s
application and NMFS’ Notice of
Proposed IHA (79 FR 60831, October 8,
2014). The information has not changed
and is therefore not repeated here.
California (southern) sea otters
(Enhydra lutris nereis), listed as
threatened under the ESA and
categorized as depleted under the
MMPA, usually range in coastal waters
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within 2 km (1.2 mi) of shore. This
species is managed by the U.S. Fish and
Wildlife Service and is not considered
further in this notice.
Potential Effects of the Specified
Activity on Marine Mammals
The appearance of researchers may
have the potential to cause Level B
harassment of any pinnipeds hauled out
at sampling sites. Although marine
mammals are never deliberately
approached by abalone survey
personnel, approach may be
unavoidable if pinnipeds are hauled out
in the immediate vicinity of the
permanent study plots. Disturbance may
result in reactions ranging from an
animal simply becoming alert to the
presence of researchers (e.g., turning the
head, assuming a more upright posture)
to flushing from the haul-out site into
the water. NMFS does not consider the
lesser reactions to constitute behavioral
harassment, or Level B harassment
takes, but rather assumes that pinnipeds
that move greater than 1 m (3.3 ft) or
change the speed or direction of their
movement in response to the presence
of researchers are behaviorally harassed,
and thus subject to Level B taking.
Animals that respond to the presence of
researchers by becoming alert, but do
not move or change the nature of
locomotion as described, are not
considered to have been subject to
behavioral harassment. NMFS’ Notice of
Proposed IHA (79 FR 60831, October 8,
2014) contains information regarding
potential impacts to marine mammals
from the specified activity. The
information has not changed and is
therefore not repeated here.
Typically, even those reactions
constituting Level B harassment would
result at most in temporary, short-term
disturbance. In any given study season,
researchers will visit sites one to two
times per year for a total of 4–6 hours
per visit. Therefore, disturbance of
pinnipeds resulting from the presence of
researchers lasts only for short periods
of time and is separated by significant
amounts of time in which no
disturbance occurs. Because such
disturbance is sporadic, rather than
chronic, and of low intensity, individual
marine mammals are unlikely to incur
any detrimental impacts to vital rates or
ability to forage and, thus, loss of
fitness. Correspondingly, even local
populations, much less the overall
stocks of animals, are extremely
unlikely to accrue any significantly
detrimental impacts.
NMFS does not anticipate that the
activities would result in the injury,
serious injury, or mortality of pinnipeds
because pups are only found at a couple
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of the sampling locations during certain
times of the year and that many
rookeries occur on the offshore islands
and not the mainland areas where the
activities would occur. In addition,
researchers will exercise appropriate
caution approaching sites, especially
when pups are present and will redirect
activities when pups are present.
Anticipated Effects on Marine Mammal
Habitat
The only habitat modification
associated with the activity is the
placement of permanent bolts and other
sampling equipment in the intertidal.
Bolts are installed during the set-up of
a site and, at existing sites, this has
already occurred. In some instances,
bolts will need to be replaced or
installed for new plots. Bolts are 7.6 to
12.7 cm (2 to 5 in) long, stainless steel
1 cm (3/8 in) Hex or Carriage bolts. They
are installed by drilling a hole with a
battery powered DeWalt 24 volt rotary
hammer drill with a 1 cm (3/8 in) bit.
The bolts protrude 1.3–7.6 cm (0.5–3 in)
above the rock surface and are held in
place with marine epoxy. Although the
drill does produce noticeable noise,
researchers have never observed an
instance where near-by or offshore
marine mammals were disturbed by it.
Any marine mammal at the site would
likely be disturbed by the presence of
researchers and retreat to a distance
where the noise of the drill would not
increase the disturbance. In most
instances, wind and wave noise also
drown out the noise of the drill. The
installation of bolts and other sampling
equipment is conducted under the
appropriate permits (Monterey Bay
National Marine Sanctuary, California
State Parks). Once a particular study has
ended, the respective sampling
equipment is removed. No trash or field
gear is left at a site. Thus, the proposed
activity is not expected to have any
habitat-related effects, including to
marine mammal prey species, that could
cause significant or long-term
consequences for individual marine
mammals or their populations.
Mitigation
In order to issue an incidental take
authorization (ITA) under section
101(a)(5)(D) of the MMPA, NMFS must,
where applicable, set forth the
permissible methods of taking pursuant
to such activity, and other means of
effecting the least practicable impact on
such species or stock and its habitat,
paying particular attention to rookeries,
mating grounds, and areas of similar
significance, and on the availability of
such species or stock for taking for
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certain subsistence uses (where
relevant).
PISCO shall implement several
mitigation measures to reduce potential
take by Level B (behavioral disturbance)
harassment. Measures include: (1)
Approaching study sites cautiously and
quietly, such that any disturbance of
pinnipeds is minimized and stampeding
is avoided; (2) avoiding disturbance that
may place pinniped pups at risk; (3)
using binoculars to detect pinnipeds
before close approach to avoid being
seen by the animals; (4) monitoring the
offshore area for predators (such as
killer whales and white sharks) and
avoid flushing of pinnipeds when
predators are observed in nearshore
waters; (5) rescheduling work at sites
where pups are present, unless other
means to accomplishing the work can be
done without causing disturbance to
mothers and dependent pups; (6) only
flushing pinnipeds if they are located in
the sampling plots and there are no
other means to accomplish the survey
(however, flushing must be done slowly
and quietly so as not to cause a
stampede); (7) not intentionally flushing
pups if present at the sampling; and (8)
rescheduling sampling if Steller sea
lions are present at the study site.
The methodologies and actions noted
in this section will be utilized and
included as mitigation measures in the
IHA to ensure that impacts to marine
mammals are mitigated to the lowest
level practicable. The primary method
of mitigating the risk of disturbance to
pinnipeds, which will be in use at all
times, is the selection of judicious
routes of approach to study sites,
avoiding close contact with pinnipeds
hauled out on shore, and the use of
extreme caution upon approach. In no
case will marine mammals be
deliberately approached by survey
personnel, and in all cases every
possible measure will be taken to select
a pathway of approach to study sites
that minimizes the number of marine
mammals potentially harassed. In
general, researchers will stay inshore of
pinnipeds whenever possible to allow
maximum escape to the ocean. Each
visit to a given study site will last for
approximately 4–6 hours, after which
the site is vacated and can be reoccupied by any marine mammals that
may have been disturbed by the
presence of researchers. By arriving
before low tide, worker presence will
tend to encourage pinnipeds to move to
other areas for the day before they haul
out and settle onto rocks at low tide.
PISCO will suspend sampling and
monitoring operations immediately if an
injured marine mammal is found in the
vicinity of the project area and the
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monitoring activities could aggravate its
condition.
NMFS has carefully evaluated
PISCO’s mitigation measures and
considered a range of other measures in
the context of ensuring that NMFS
prescribes the means of effecting the
least practicable impact on the affected
marine mammal species and stocks and
their habitat. Our evaluation of potential
measures included consideration of the
following factors in relation to one
another:
• The manner in which, and the
degree to which, the successful
implementation of the measure is
expected to minimize adverse impacts
to marine mammals;
• The proven or likely efficacy of the
specific measure to minimize adverse
impacts as planned; and
• The practicability of the measure
for applicant implementation.
Based on our evaluation of the
applicant’s final measures, NMFS has
determined that the mitigation measures
provide the means of effecting the least
practicable impact on marine mammal
species or stocks and their habitat,
paying particular attention to rookeries,
mating grounds, and areas of similar
significance.
Monitoring and Reporting
In order to issue an ITA for an
activity, section 101(a)(5)(D) of the
MMPA states that NMFS must, where
applicable, set forth ‘‘requirements
pertaining to the monitoring and
reporting of such taking’’. The MMPA
implementing regulations at 50 CFR
216.104 (a)(13) indicate that requests for
ITAs must include the suggested means
of accomplishing the necessary
monitoring and reporting that will result
in increased knowledge of the species
and of the level of taking or impacts on
populations of marine mammals that are
expected to be present in the proposed
action area.
PISCO can add to the knowledge of
pinnipeds in California and Oregon by
noting observations of: (1) Unusual
behaviors, numbers, or distributions of
pinnipeds, such that any potential
follow-up research can be conducted by
the appropriate personnel; (2) tagbearing carcasses of pinnipeds, allowing
transmittal of the information to
appropriate agencies and personnel; and
(3) rare or unusual species of marine
mammals for agency follow-up.
Monitoring requirements in relation
to PISCO’s rocky intertidal monitoring
will include observations made by the
applicant. Information recorded will
include species counts (with numbers of
pups/juveniles when possible), numbers
of observed disturbances, and
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descriptions of the disturbance
behaviors during the monitoring
surveys, including location, date, and
time of the event. In addition,
observations regarding the number and
species of any marine mammals
observed, either in the water or hauled
out, at or adjacent to the site, will be
recorded as part of field observations
during research activities. Observations
of unusual behaviors, numbers, or
distributions of pinnipeds will be
reported to NMFS so that any potential
follow-up observations can be
conducted by the appropriate personnel.
In addition, observations of tag-bearing
pinniped carcasses as well as any rare
or unusual species of marine mammals
will be reported to NMFS. Information
regarding physical and biological
conditions pertaining to a site, as well
as the date and time that research was
conducted will also be noted.
If at any time injury, serious injury, or
mortality of the species for which take
is authorized should occur, or if take of
any kind of any other marine mammal
occurs, and such action may be a result
of the research, PISCO will suspend
research activities and contact NMFS
immediately to determine how best to
proceed to ensure that another injury or
death does not occur and to ensure that
the applicant remains in compliance
with the MMPA.
A draft final report must be submitted
to NMFS Office of Protected Resources
within 60 days after the conclusion of
the 2014–2015 field season or 60 days
prior to the start of the next field season
if a new IHA will be requested. The
report will include a summary of the
information gathered pursuant to the
monitoring requirements set forth in the
IHA. A final report must be submitted
to the Director of the NMFS Office of
Protected Resources and to the NMFS
West Coast Office Regional
Administrator within 30 days after
receiving comments from NMFS on the
draft final report. If no comments are
received from NMFS, the draft final
report will be considered to be the final
report.
Estimated Take by Incidental
Harassment
Except with respect to certain
activities not pertinent here, the MMPA
defines ‘‘harassment’’ as: Any act of
pursuit, torment, or annoyance which (i)
has the potential to injure a marine
mammal or marine mammal stock in the
wild [Level A harassment]; or (ii) has
the potential to disturb a marine
mammal or marine mammal stock in the
wild by causing disruption of behavioral
patterns, including, but not limited to,
migration, breathing, nursing, breeding,
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73051
feeding, or sheltering [Level B
harassment].
All anticipated takes would be by
Level B harassment, involving
temporary changes in behavior. The
mitigation and monitoring measures are
expected to minimize the possibility of
injurious or lethal takes such that take
by injury, serious injury, or mortality is
considered remote. Animals hauled out
close to the actual survey sites may be
disturbed by the presence of biologists
and may alter their behavior or attempt
to move away from the researchers.
As discussed earlier, NMFS considers
an animal to have been harassed if it
moved greater than 1 m (3.3 ft) in
response to the researcher’s presence or
if the animal was already moving and
changed direction and/or speed, or if
the animal flushed into the water.
Animals that became alert without such
movements were not considered
harassed.
For the purpose of this IHA, only
Oregon and California sites that are
frequently sampled and have a marine
mammal presence during sampling were
included in take estimates. Sites where
only Biodiversity Surveys are conducted
were not included due to the
infrequency of sampling and rarity of
occurrences of pinnipeds during
sampling. In addition, Steller sea lions
are not included in take estimates as
they will not be disturbed by
researchers or research activities since
activities will not occur or will be
suspended if Steller sea lions are
present. A small number of harbor seal
and northern elephant seal pup takes
are anticipated as pups may be present
at several sites during spring and
summer sampling.
Takes estimates are based on marine
mammal observations from each site.
Marine mammal observations are done
as part of PISCO site observations,
which include notes on physical and
biological conditions at the site. The
maximum number of marine mammals,
by species, seen at any given time
throughout the sampling day is recorded
at the conclusion of sampling. A marine
mammal is counted if it is seen on
access ways to the site, at the site, or
immediately up-coast or down-coast of
the site. Marine mammals in the water
immediately offshore are also recorded.
Any other relevant information,
including the location of a marine
mammal relevant to the site, any
unusual behavior, and the presence of
pups is also noted.
These observations formed the basis
from which researchers with extensive
knowledge and experience at each site
estimated the actual number of marine
mammals that may be subject to take. In
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most cases the number of takes is based
on the maximum number of marine
mammals that have been observed at a
site throughout the history of the site
(2–3 observation per year for 5–10 years
or more). Section 6 in PISCO’s
application outlines the number of visits
per year for each sampling site and the
potential number of pinnipeds
anticipated to be encountered at each
site. Table 4 in PISCO’s application
outlines the number of potential takes
per site (see ADDRESSES).
Based on this information, NMFS has
authorized the take, by Level B
harassment only, of 55 California sea
lions, 183 harbor seals, and 30 northern
elephant seals. These numbers are
considered to be maximum take
estimates; therefore, actual take may be
slightly less if animals decide to haul
out at a different location for the day or
animals are out foraging at the time of
the survey activities.
Negligible Impact and Small Numbers
Analysis and Determination
NMFS typically includes our
negligible impact and small numbers
analyses and determinations under the
same section heading of our Federal
Register notices. Despite co-locating
these terms, we acknowledge that
negligible impact and small numbers are
distinct standards under the MMPA and
treat them as such. The analyses
presented below do not conflate the two
standards; instead, each standard has
been considered independently, and we
have applied the relevant factors to
inform our negligible impact and small
numbers determinations.
NMFS has defined ‘‘negligible
impact’’ in 50 CFR 216.103 as ‘‘. . . an
impact resulting from the specified
activity that cannot be reasonably
expected to, and is not reasonably likely
to, adversely affect the species or stock
through effects on annual rates of
recruitment or survival.’’ In making a
negligible impact determination, NMFS
considers a variety of factors, including
but not limited to: (1) The number of
anticipated mortalities; (2) the number
and nature of anticipated injuries; (3)
the number, nature, intensity, and
duration of Level B harassment; and (4)
the context in which the take occurs.
No injuries or mortalities are
anticipated to occur as a result of
PISCO’s rocky intertidal monitoring,
and none are authorized. The behavioral
harassments that could occur would be
of limited duration, as researchers only
conduct sampling one to two times per
year at each site for a total of 4–6 hours
per sampling event. Therefore,
disturbance will be limited to a short
duration, allowing pinnipeds to
reoccupy the sites within a short
amount of time.
Some of the pinniped species may use
some of the sites during certain times of
year to conduct pupping and/or
breeding. However, some of these
species prefer to use the offshore islands
for these activities. At the sites where
pups may be present, PISCO will
implement certain mitigation measures,
such as no intentional flushing if
dependent pups are present, which will
avoid mother/pup separation and
trampling of pups.
Of the three marine mammal species
anticipated to occur in the activity
areas, none are listed under the ESA.
Table 1 in this document presents the
abundance of each species or stock, the
authorized take estimates, and the
percentage of the affected populations
or stocks that may be taken by
harassment. Based on these estimates,
PISCO would take less than 1.1% of
each species or stock. Because these are
maximum estimates, actual take
numbers are likely to be lower, as some
animals may select other haulout sites
the day the researchers are present.
Based on the analysis contained
herein of the likely effects of the
specified activity on marine mammals
and their habitat, and taking into
consideration the implementation of the
mitigation and monitoring measures,
NMFS finds that the rocky intertidal
monitoring program will result in the
incidental take of small numbers of
marine mammals, by Level B
harassment only, and that the total
taking from the rocky intertidal
monitoring program will have a
negligible impact on the affected species
or stocks.
TABLE 1—POPULATION ABUNDANCE ESTIMATES, TOTAL AUTHORIZED LEVEL B TAKE, AND PERCENTAGE OF POPULATION
THAT MAY BE TAKEN FOR THE POTENTIALLY AFFECTED SPECIES DURING THE PROPOSED ROCKY INTERTIDAL MONITORING PROGRAM
Species
Abundance *
Harbor Seal ..................................................................................................................................
Total
authorized
level B take
1 30,196
Percentage of
stock or
population
183
0.6–1.1
60
30
0.02
0.03
2 16,165
California Sea Lion ......................................................................................................................
Northern Elephant Seal ...............................................................................................................
296,750
124,000
* Abundance estimates are taken from the 2013 U.S. Pacific Marine Mammal Stock Assessments (Carretta et al., 2014).
1 California stock abundance estimate;
2 Oregon/Washington stock abundance estimate
rljohnson on DSK3VPTVN1PROD with NOTICES
Impact on Availability of Affected
Species or Stock for Taking for
Subsistence Uses
Endangered Species Act (ESA)
There are no relevant subsistence uses
of marine mammals 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.
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None of the marine mammals for
which incidental take is authorized are
listed as threatened or endangered
under the ESA. NMFS’ Permits and
Conservation Division worked with the
NMFS West Coast Regional Office to
ensure that Steller sea lions would be
avoided and incidental take would not
occur. Therefore, NMFS has determined
that issuance of the IHA to PISCO under
section 101(a)(5)(D) of the MMPA will
have no effect on species listed as
threatened or endangered under the
ESA.
National Environmental Policy Act
(NEPA)
In 2012, we prepared an EA analyzing
the potential effects to the human
environment from conducting rocky
intertidal surveys along the California
and Oregon coasts and issued a FONSI
on the issuance of an IHA for PISCO’s
rocky intertidal surveys in accordance
with section 6.01 of the NOAA
Administrative Order 216–6
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(Environmental Review Procedures for
Implementing the National
Environmental Policy Act, May 20,
1999). PISCO’s proposed activities and
impacts for 2013–2014 are within the
scope of our 2012 EA and FONSI. We
have reviewed the 2012 EA and
determined that there are no new direct,
indirect, or cumulative impacts to the
human and natural environment
associated with the IHA requiring
evaluation in a supplemental EA and
we, therefore, reaffirm the 2012 FONSI.
Authorization
As a result of these determinations,
NMFS has authorized the take of marine
mammals incidental to PISCO’s rocky
intertidal monitoring research activities,
provided the previously mentioned
mitigation, monitoring, and reporting
requirements are incorporated.
Dated: December 3, 2014.
Donna S. Wieting,
Director, Office of Protected Resources,
National Marine Fisheries Service.
[FR Doc. 2014–28807 Filed 12–8–14; 8:45 am]
BILLING CODE 3510–22–P
DEPARTMENT OF DEFENSE
Office of the Secretary
[Docket ID: DoD–2014–OS–0157]
Proposed Collection; Comment
Request
Defense Media Activity, DoD.
ACTION: Notice.
AGENCY:
In compliance with the
Paperwork Reduction Act of 1995, the
Defense Media Activity announces a
proposed public information collection
and seeks public comment on the
provisions thereof. Comments are
invited on: (a) Whether the proposed
collection of information is necessary
for the proper performance of the
functions of the agency, including
whether the information shall have
practical utility; (b) the accuracy of the
agency’s estimate of the burden of the
proposed information collection; (c)
ways to enhance the quality, utility, and
clarity of the information to be
collected; and (d) ways to minimize the
burden of the information collection on
respondents, including through the use
of automated collection techniques or
other forms of information technology.
DATES: Consideration will be given to all
comments received by February 9, 2015.
ADDRESSES: You may submit comments,
identified by docket number and title,
by any of the following methods:
rljohnson on DSK3VPTVN1PROD with NOTICES
SUMMARY:
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• Federal eRulemaking Portal: https://
www.regulations.gov. Follow the
instructions for submitting comments.
• Mail: Federal Docket Management
System Office, 4800 Mark Center Drive,
East Tower, Suite 02G09, Alexandria,
VA 22350–3100.
Instructions: All submissions received
must include the agency name, docket
number and title for this Federal
Register document. The general policy
for comments and other submissions
from members of the public is to make
these submissions available for public
viewing on the Internet at https://
www.regulations.gov as they are
received without change, including any
personal identifiers or contact
information.
Any associated form(s) for this
collection may be located within this
same electronic docket and downloaded
for review/testing. Follow the
instructions at https://
www.regulations.gov for submitting
comments. Please submit comments on
any given form identified by docket
number, form number, and title.
FOR FURTHER INFORMATION CONTACT: To
request more information on this
proposed information collection or to
obtain a copy of the proposal and
associated collection instruments,
please write to the Defense Media
Activity, American Forces NetworkBroadcast Center, 23755 Z Street,
Riverside, CA 92518, or call 951–413–
2569.
SUPPLEMENTARY INFORMATION:
Title; Associated Form; and OMB
Number: AFNConnect (AFNC); OMB
Control Number 0704–TBD.
Needs and Uses: The information
collection requirement is necessary to
obtain and audit the eligibility of DoD
Employees, DoD contractors,
Department of State (DoS) employees,
military personnel (including retirees
and active reservists) and their family
members OCONUS to receive restricted
American Forces Radio and Television
Service (AFRTS) programming services
(i.e., radio, television, and web
streaming services). Demographic data
will also be collected to ensure DMA
provides its services in the most
efficient and cost effective manner.
Affected Public: Individuals or
households
Annual Burden Hours: 1,667
Number of Respondents: 10,000
Responses Per Respondent: 1
Average Burden Per Response: 10
minutes
Frequency: On occasion
The American Forces Network (AFN)
is a broadcast service of the Defense
Media Activity (DMA). AFN provides an
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internal information program to provide
U.S. radio and television news,
information, and entertainment
programming to Military Service
members, DoD civilian and contract
employees, and their families overseas,
on board U.S. Navy and Coast Guard
ships at sea, and other authorized users.
This DoD internal information program
(1) provides U.S. military commanders
worldwide with a unique means to
communicate internal information
directly to DoD personnel and their
family members overseas; (2) provides
overseas DoD personnel and their
families the same type of information
and entertainment programming as their
fellow citizens in the United States; (3)
assists in maintaining and enhancing
the morale, readiness, situational
awareness, and well-being of DoD
personnel and their family members
overseas. AFN communicates messages
and themes from senior DoD leaders
(i.e., Secretary of Defense, Secretaries of
the Military Departments, Chairman of
the Joint Chiefs of Staff, Military Service
Chiefs of Staff, Combatant
Commanders), as well as other leaders
in the chain of command, in order to
support and improve quality of life and
morale, promote situational awareness,
provide timely and immediate force
protection information, and sustain
readiness.
Much of the content distributed by
AFN is commercial programming whose
distribution is restricted to targeted
OCONUS audiences. The AFNConnect
system is an automated system which
will allow potential consumers of AFN
content to quickly validate their
location and status, and be
automatically authorized to receive AFN
programming.
Dated: December 3, 2014.
Aaron Siegel,
Alternate OSD Federal Register Liaison
Officer, Department of Defense.
[FR Doc. 2014–28731 Filed 12–8–14; 8:45 am]
BILLING CODE 5001–06–P
DEPARTMENT OF DEFENSE
Office of the Secretary
Renewal of Department of Defense
Federal Advisory Committees
DoD.
Renewal of Federal Advisory
Committee.
AGENCY:
ACTION:
The Department of Defense is
publishing this notice to announce that
it is renewing the charter for the
Department of Defense Military Family
Readiness Council (‘‘the Council’’).
SUMMARY:
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Agencies
[Federal Register Volume 79, Number 236 (Tuesday, December 9, 2014)]
[Notices]
[Pages 73048-73053]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2014-28807]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
RIN 0648-XD531
Takes of Marine Mammals Incidental to Specified Activities;
Taking Marine Mammals Incidental to Rocky Intertidal Monitoring Surveys
Along the Oregon and California Coasts
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Notice; issuance of an incidental harassment authorization.
-----------------------------------------------------------------------
SUMMARY: In accordance with the Marine Mammal Protection Act (MMPA)
regulations, notification is hereby given that NMFS has issued an
Incidental Harassment Authorization (IHA) to the Partnership for
Interdisciplinary Study of Coastal Oceans (PISCO) at the University of
California (UC) Santa Cruz for an Incidental Harassment Authorization
(IHA) to take marine mammals, by harassment, incidental to rocky
intertidal monitoring surveys.
DATES: Effective December 17, 2014, through December 16, 2015.
ADDRESSES: A copy of the authorization, application, and associated
Environmental Assessment (EA) and Finding of No Significant Impact
(FONSI) may be obtained by writing to Jolie Harrison, Chief, Permits
and Conservation Division, Office of Protected Resources, National
Marine Fisheries Service, 1315 East-West Highway, Silver Spring, MD
20910, telephoning the contact listed below (see FOR FURTHER
INFORMATION CONTACT), or visiting the internet at: https://www.nmfs.noaa.gov/pr/permits/incidental.htm. Documents cited in this
notice may also be viewed, by appointment, during regular business
hours, at the aforementioned address.
FOR FURTHER INFORMATION CONTACT: Robert Pauline, Office of Protected
Resources, NMFS, (301) 427-8401.
SUPPLEMENTARY INFORMATION:
Background
Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.)
direct the Secretary of Commerce to allow, upon request, the
incidental, but not intentional, taking of small numbers of marine
mammals by U.S. citizens who engage in a specified activity (other than
commercial fishing) within a specified geographical region if certain
findings are made and either regulations are issued or, if the taking
is limited to harassment, a notice of a proposed authorization is
provided to the public for review.
Authorization for incidental takings shall be granted if NMFS finds
that the taking will have a negligible impact on the species or
stock(s), will not have an unmitigable adverse impact on the
availability of the species or stock(s) for subsistence uses (where
relevant), and if the permissible methods of taking, other means of
effecting the least practicable impact on the species or stock and its
habitat, and requirements pertaining to the mitigation, monitoring and
reporting of such takings are set forth. NMFS has defined ``negligible
impact'' in 50 CFR 216.103 as ``. . . an impact resulting from the
specified activity that cannot be reasonably expected to, and is not
reasonably likely to, adversely affect the species or stock through
effects on annual rates of recruitment or survival.''
Section 101(a)(5)(D) of the MMPA established an expedited process
by which citizens of the United States can apply for an authorization
to incidentally take small numbers of marine mammals by harassment.
Section 101(a)(5)(D) establishes a 45-day time limit for NMFS review of
an application followed by a 30-day public notice and comment period on
any proposed authorizations for the incidental harassment of marine
mammals. Within 45 days of the close of the comment period, NMFS must
either issue or deny the authorization. Except with respect to certain
activities not pertinent here, the MMPA defines ``harassment'' as:
``any act of pursuit, torment, or annoyance which (i) has the potential
to injure a marine mammal or marine mammal stock in the wild [Level A
harassment]; or (ii) has the potential to disturb a marine mammal or
marine mammal stock in the wild by causing disruption of behavioral
patterns, including, but not limited to, migration, breathing, nursing,
breeding, feeding, or sheltering [Level B harassment].''
Summary of Request
On July 30, 2014, NMFS received an application from PISCO for the
taking of marine mammals incidental to rocky intertidal monitoring
surveys along the Oregon and California coasts. NMFS determined that
the application was adequate and complete on August 22, 2014. On
October 8, 2014, we published a notice in the Federal Register of our
proposal to issue an IHA with preliminary determinations and explained
the basis for the proposal and preliminary determinations (78 FR
64918). The notice initiated a 30-day public comment period. Responses
are discussed below. In December 2012, NMFS issued a 1-year IHA to
PISCO to
[[Page 73049]]
take marine mammals incidental to these same proposed activities (77 FR
72327, December 5, 2012). That IHA expired on December 2, 2013. In
December 2013 NMFS issued another 1 year IHA to PISCO to take marine
mammals incidental to continuation of proposed activities which expires
on December 16, 2014 (78 FR 79403, December 30, 2013).
The research group at UC Santa Cruz operates in collaboration with
two large-scale marine research programs: PISCO and the Multi-agency
Rocky Intertidal Network. The research group at UC Santa Cruz (PISCO)
is responsible for many of the ongoing rocky intertidal monitoring
programs along the Pacific coast. Monitoring occurs at rocky intertidal
sites, often large bedrock benches, from the high intertidal to the
water's edge. Long-term monitoring projects include Community Structure
Monitoring, Intertidal Biodiversity Surveys, Marine Protected Area
Baseline Monitoring, Intertidal Recruitment Monitoring, and Ocean
Acidification. Research is conducted throughout the year along the
California and Oregon coasts and will continue indefinitely. Most sites
are sampled one to two times per year over a 4-6 hour period during a
negative low tide series. This IHA is only effective for a 12-month
period. The following specific aspects of the proposed activities are
likely to result in the take of marine mammals: Presence of survey
personnel near pinniped haulout sites and approach of survey personnel
towards hauled out pinnipeds. Take, by Level B harassment only, of
individuals of three species of marine mammals is anticipated to result
from the specified activity.
Description of the Specified Activity and Specified Geographic Region
PISCO focuses on understanding the nearshore ecosystems of the U.S.
west coast through a number of interdisciplinary collaborations. PISCO
integrates long-term monitoring of ecological and oceanographic
processes at dozens of sites with experimental work in the lab and
field. A short description of each project is contained here.
Additional information can be found in PISCO's application (see
ADDRESSES) and the Notice of Proposed IHA (79 FR 60831, October 8,
2014).
Community Structure Monitoring involves the use of permanent
photoplot quadrats which target specific algal and invertebrate
assemblages (e.g. mussels, rockweeds, barnacles). This project provides
managers with insight into the causes and consequences of changes in
species abundance. Each Community Structure site is surveyed over a 1-
day period during a low tide series one to two times a year. Sites,
location, number of times sampled per year, and typical sampling months
for each site are presented in Table 1 in PISCO's application (see
ADDRESSES).
Biodiversity Surveys, which are part of a long-term monitoring
project and are conducted every 3-5 years at established sites, involve
point contact identification along permanent transects, mobile
invertebrate quadrat counts, sea star band counts, and tidal height
topographic measurements. Table 2 in PISCO's application (see
ADDRESSES) lists established biodiversity sites in Oregon and
California.
In September 2007, the state of California began establishing a
network of Marine Protected Areas along the California coast as part of
the Marine Life Protection Act (MLPA). Under baseline monitoring
programs funded by Sea Grant and the Ocean Protection Council, PISCO
established additional intertidal monitoring sites in the Central
Coast, North Central Coast, and South Coast study regions. Six
additional sites will be established and sampled in the North Coast
study region during 2015 (see Table 3 in PISCO's application). Baseline
characterization of newly established areas involves sampling of these
new sites, as well as established sites both within and outside of
marine protected areas. These sites were sampled using existing
Community Structure and Biodiversity protocols for consistency.
Resampling of these sites may take place as part of future marine
protected area evaluation.
Specified Geographic Location and Activity Timeframe
PISCO's research is conducted throughout the year along the
California and Oregon coasts. Most sites are sampled one to two times
per year over a 1-day period (4-6 hours per site) during a negative low
tide series. Due to the large number of research sites, scheduling
constraints, the necessity for negative low tides and favorable
weather/ocean conditions, exact survey dates are variable and difficult
to predict. Some sampling is anticipated to occur in all months, except
for January, August, and September.
The intertidal zones where PISCO conducts intertidal monitoring are
also areas where pinnipeds can be found hauled out on the shore at or
adjacent to some research sites. Accessing portions of the intertidal
habitat may cause incidental Level B (behavioral) harassment of
pinnipeds through some unavoidable approaches if pinnipeds are hauled
out directly in the study plots or while biologists walk from one
location to another. No motorized equipment is involved in conducting
these surveys. The species for which Level B harassment is requested
are: California sea lions (Zalophus californianus californianus);
harbor seals (Phoca vitulina richardii); and northern elephant seals
(Mirounga angustirostris).
Comments and Responses
A Notice of Proposed IHA was published in the Federal Register on
October 8, 2014 (79 FR 60831) for public comment. During the 30-day
public comment period, NMFS received one letter from the Marine Mammal
Commission. No other organizations provided comments on the proposed
issuance of an IHA for this activity. The Marine Mammal Commission
recommended that NMFS issue the IHA, subject to inclusion of the
proposed mitigation and monitoring measures. NMFS has included all of
the mitigation and monitoring measures proposed in the Notice of
Proposed IHA (79 FR 60831, October 8, 2014) in the issued IHA.
Description of Marine Mammals in the Area of the Specified Activity
Several pinniped species can be found along the California and
Oregon coasts. The three that are most likely to occur at some of the
research sites are California sea lion, harbor seal, and northern
elephant seal. On rare occasions, PISCO researchers have seen very
small numbers (i.e., five or fewer) of Steller sea lions at one of the
sampling sites. These sightings are rare. Therefore, encounters are not
expected. However, if Steller sea lions are sighted before approaching
a sampling site, researchers will abandon approach and return at a
later date. For this reason, this species is not considered further in
this IHA notice.
We refer the public to Carretta et al. (2014) for general
information on these species. The publication is available on the
internet at: https://www.nmfs.noaa.gov/pr/sars/pdf/pacific2013_final.pdf. Additional information on the status,
distribution, seasonal distribution, and life history can also be found
in PISCO's application and NMFS' Notice of Proposed IHA (79 FR 60831,
October 8, 2014). The information has not changed and is therefore not
repeated here.
California (southern) sea otters (Enhydra lutris nereis), listed as
threatened under the ESA and categorized as depleted under the MMPA,
usually range in coastal waters
[[Page 73050]]
within 2 km (1.2 mi) of shore. This species is managed by the U.S. Fish
and Wildlife Service and is not considered further in this notice.
Potential Effects of the Specified Activity on Marine Mammals
The appearance of researchers may have the potential to cause Level
B harassment of any pinnipeds hauled out at sampling sites. Although
marine mammals are never deliberately approached by abalone survey
personnel, approach may be unavoidable if pinnipeds are hauled out in
the immediate vicinity of the permanent study plots. Disturbance may
result in reactions ranging from an animal simply becoming alert to the
presence of researchers (e.g., turning the head, assuming a more
upright posture) to flushing from the haul-out site into the water.
NMFS does not consider the lesser reactions to constitute behavioral
harassment, or Level B harassment takes, but rather assumes that
pinnipeds that move greater than 1 m (3.3 ft) or change the speed or
direction of their movement in response to the presence of researchers
are behaviorally harassed, and thus subject to Level B taking. Animals
that respond to the presence of researchers by becoming alert, but do
not move or change the nature of locomotion as described, are not
considered to have been subject to behavioral harassment. NMFS' Notice
of Proposed IHA (79 FR 60831, October 8, 2014) contains information
regarding potential impacts to marine mammals from the specified
activity. The information has not changed and is therefore not repeated
here.
Typically, even those reactions constituting Level B harassment
would result at most in temporary, short-term disturbance. In any given
study season, researchers will visit sites one to two times per year
for a total of 4-6 hours per visit. Therefore, disturbance of pinnipeds
resulting from the presence of researchers lasts only for short periods
of time and is separated by significant amounts of time in which no
disturbance occurs. Because such disturbance is sporadic, rather than
chronic, and of low intensity, individual marine mammals are unlikely
to incur any detrimental impacts to vital rates or ability to forage
and, thus, loss of fitness. Correspondingly, even local populations,
much less the overall stocks of animals, are extremely unlikely to
accrue any significantly detrimental impacts.
NMFS does not anticipate that the activities would result in the
injury, serious injury, or mortality of pinnipeds because pups are only
found at a couple of the sampling locations during certain times of the
year and that many rookeries occur on the offshore islands and not the
mainland areas where the activities would occur. In addition,
researchers will exercise appropriate caution approaching sites,
especially when pups are present and will redirect activities when pups
are present.
Anticipated Effects on Marine Mammal Habitat
The only habitat modification associated with the activity is the
placement of permanent bolts and other sampling equipment in the
intertidal. Bolts are installed during the set-up of a site and, at
existing sites, this has already occurred. In some instances, bolts
will need to be replaced or installed for new plots. Bolts are 7.6 to
12.7 cm (2 to 5 in) long, stainless steel 1 cm (3/8 in) Hex or Carriage
bolts. They are installed by drilling a hole with a battery powered
DeWalt 24 volt rotary hammer drill with a 1 cm (3/8 in) bit. The bolts
protrude 1.3-7.6 cm (0.5-3 in) above the rock surface and are held in
place with marine epoxy. Although the drill does produce noticeable
noise, researchers have never observed an instance where near-by or
offshore marine mammals were disturbed by it. Any marine mammal at the
site would likely be disturbed by the presence of researchers and
retreat to a distance where the noise of the drill would not increase
the disturbance. In most instances, wind and wave noise also drown out
the noise of the drill. The installation of bolts and other sampling
equipment is conducted under the appropriate permits (Monterey Bay
National Marine Sanctuary, California State Parks). Once a particular
study has ended, the respective sampling equipment is removed. No trash
or field gear is left at a site. Thus, the proposed activity is not
expected to have any habitat-related effects, including to marine
mammal prey species, that could cause significant or long-term
consequences for individual marine mammals or their populations.
Mitigation
In order to issue an incidental take authorization (ITA) under
section 101(a)(5)(D) of the MMPA, NMFS must, where applicable, set
forth the permissible methods of taking pursuant to such activity, and
other means of effecting the least practicable impact on such species
or stock and its habitat, paying particular attention to rookeries,
mating grounds, and areas of similar significance, and on the
availability of such species or stock for taking for certain
subsistence uses (where relevant).
PISCO shall implement several mitigation measures to reduce
potential take by Level B (behavioral disturbance) harassment. Measures
include: (1) Approaching study sites cautiously and quietly, such that
any disturbance of pinnipeds is minimized and stampeding is avoided;
(2) avoiding disturbance that may place pinniped pups at risk; (3)
using binoculars to detect pinnipeds before close approach to avoid
being seen by the animals; (4) monitoring the offshore area for
predators (such as killer whales and white sharks) and avoid flushing
of pinnipeds when predators are observed in nearshore waters; (5)
rescheduling work at sites where pups are present, unless other means
to accomplishing the work can be done without causing disturbance to
mothers and dependent pups; (6) only flushing pinnipeds if they are
located in the sampling plots and there are no other means to
accomplish the survey (however, flushing must be done slowly and
quietly so as not to cause a stampede); (7) not intentionally flushing
pups if present at the sampling; and (8) rescheduling sampling if
Steller sea lions are present at the study site.
The methodologies and actions noted in this section will be
utilized and included as mitigation measures in the IHA to ensure that
impacts to marine mammals are mitigated to the lowest level
practicable. The primary method of mitigating the risk of disturbance
to pinnipeds, which will be in use at all times, is the selection of
judicious routes of approach to study sites, avoiding close contact
with pinnipeds hauled out on shore, and the use of extreme caution upon
approach. In no case will marine mammals be deliberately approached by
survey personnel, and in all cases every possible measure will be taken
to select a pathway of approach to study sites that minimizes the
number of marine mammals potentially harassed. In general, researchers
will stay inshore of pinnipeds whenever possible to allow maximum
escape to the ocean. Each visit to a given study site will last for
approximately 4-6 hours, after which the site is vacated and can be re-
occupied by any marine mammals that may have been disturbed by the
presence of researchers. By arriving before low tide, worker presence
will tend to encourage pinnipeds to move to other areas for the day
before they haul out and settle onto rocks at low tide.
PISCO will suspend sampling and monitoring operations immediately
if an injured marine mammal is found in the vicinity of the project
area and the
[[Page 73051]]
monitoring activities could aggravate its condition.
NMFS has carefully evaluated PISCO's mitigation measures and
considered a range of other measures in the context of ensuring that
NMFS prescribes the means of effecting the least practicable impact on
the affected marine mammal species and stocks and their habitat. Our
evaluation of potential measures included consideration of the
following factors in relation to one another:
The manner in which, and the degree to which, the
successful implementation of the measure is expected to minimize
adverse impacts to marine mammals;
The proven or likely efficacy of the specific measure to
minimize adverse impacts as planned; and
The practicability of the measure for applicant
implementation.
Based on our evaluation of the applicant's final measures, NMFS has
determined that the mitigation measures provide the means of effecting
the least practicable impact on marine mammal species or stocks and
their habitat, paying particular attention to rookeries, mating
grounds, and areas of similar significance.
Monitoring and Reporting
In order to issue an ITA for an activity, section 101(a)(5)(D) of
the MMPA states that NMFS must, where applicable, set forth
``requirements pertaining to the monitoring and reporting of such
taking''. The MMPA implementing regulations at 50 CFR 216.104 (a)(13)
indicate that requests for ITAs must include the suggested means of
accomplishing the necessary monitoring and reporting that will result
in increased knowledge of the species and of the level of taking or
impacts on populations of marine mammals that are expected to be
present in the proposed action area.
PISCO can add to the knowledge of pinnipeds in California and
Oregon by noting observations of: (1) Unusual behaviors, numbers, or
distributions of pinnipeds, such that any potential follow-up research
can be conducted by the appropriate personnel; (2) tag-bearing
carcasses of pinnipeds, allowing transmittal of the information to
appropriate agencies and personnel; and (3) rare or unusual species of
marine mammals for agency follow-up.
Monitoring requirements in relation to PISCO's rocky intertidal
monitoring will include observations made by the applicant. Information
recorded will include species counts (with numbers of pups/juveniles
when possible), numbers of observed disturbances, and descriptions of
the disturbance behaviors during the monitoring surveys, including
location, date, and time of the event. In addition, observations
regarding the number and species of any marine mammals observed, either
in the water or hauled out, at or adjacent to the site, will be
recorded as part of field observations during research activities.
Observations of unusual behaviors, numbers, or distributions of
pinnipeds will be reported to NMFS so that any potential follow-up
observations can be conducted by the appropriate personnel. In
addition, observations of tag-bearing pinniped carcasses as well as any
rare or unusual species of marine mammals will be reported to NMFS.
Information regarding physical and biological conditions pertaining to
a site, as well as the date and time that research was conducted will
also be noted.
If at any time injury, serious injury, or mortality of the species
for which take is authorized should occur, or if take of any kind of
any other marine mammal occurs, and such action may be a result of the
research, PISCO will suspend research activities and contact NMFS
immediately to determine how best to proceed to ensure that another
injury or death does not occur and to ensure that the applicant remains
in compliance with the MMPA.
A draft final report must be submitted to NMFS Office of Protected
Resources within 60 days after the conclusion of the 2014-2015 field
season or 60 days prior to the start of the next field season if a new
IHA will be requested. The report will include a summary of the
information gathered pursuant to the monitoring requirements set forth
in the IHA. A final report must be submitted to the Director of the
NMFS Office of Protected Resources and to the NMFS West Coast Office
Regional Administrator within 30 days after receiving comments from
NMFS on the draft final report. If no comments are received from NMFS,
the draft final report will be considered to be the final report.
Estimated Take by Incidental Harassment
Except with respect to certain activities not pertinent here, the
MMPA defines ``harassment'' as: Any act of pursuit, torment, or
annoyance which (i) has the potential to injure a marine mammal or
marine mammal stock in the wild [Level A harassment]; or (ii) has the
potential to disturb a marine mammal or marine mammal stock in the wild
by causing disruption of behavioral patterns, including, but not
limited to, migration, breathing, nursing, breeding, feeding, or
sheltering [Level B harassment].
All anticipated takes would be by Level B harassment, involving
temporary changes in behavior. The mitigation and monitoring measures
are expected to minimize the possibility of injurious or lethal takes
such that take by injury, serious injury, or mortality is considered
remote. Animals hauled out close to the actual survey sites may be
disturbed by the presence of biologists and may alter their behavior or
attempt to move away from the researchers.
As discussed earlier, NMFS considers an animal to have been
harassed if it moved greater than 1 m (3.3 ft) in response to the
researcher's presence or if the animal was already moving and changed
direction and/or speed, or if the animal flushed into the water.
Animals that became alert without such movements were not considered
harassed.
For the purpose of this IHA, only Oregon and California sites that
are frequently sampled and have a marine mammal presence during
sampling were included in take estimates. Sites where only Biodiversity
Surveys are conducted were not included due to the infrequency of
sampling and rarity of occurrences of pinnipeds during sampling. In
addition, Steller sea lions are not included in take estimates as they
will not be disturbed by researchers or research activities since
activities will not occur or will be suspended if Steller sea lions are
present. A small number of harbor seal and northern elephant seal pup
takes are anticipated as pups may be present at several sites during
spring and summer sampling.
Takes estimates are based on marine mammal observations from each
site. Marine mammal observations are done as part of PISCO site
observations, which include notes on physical and biological conditions
at the site. The maximum number of marine mammals, by species, seen at
any given time throughout the sampling day is recorded at the
conclusion of sampling. A marine mammal is counted if it is seen on
access ways to the site, at the site, or immediately up-coast or down-
coast of the site. Marine mammals in the water immediately offshore are
also recorded. Any other relevant information, including the location
of a marine mammal relevant to the site, any unusual behavior, and the
presence of pups is also noted.
These observations formed the basis from which researchers with
extensive knowledge and experience at each site estimated the actual
number of marine mammals that may be subject to take. In
[[Page 73052]]
most cases the number of takes is based on the maximum number of marine
mammals that have been observed at a site throughout the history of the
site (2-3 observation per year for 5-10 years or more). Section 6 in
PISCO's application outlines the number of visits per year for each
sampling site and the potential number of pinnipeds anticipated to be
encountered at each site. Table 4 in PISCO's application outlines the
number of potential takes per site (see ADDRESSES).
Based on this information, NMFS has authorized the take, by Level B
harassment only, of 55 California sea lions, 183 harbor seals, and 30
northern elephant seals. These numbers are considered to be maximum
take estimates; therefore, actual take may be slightly less if animals
decide to haul out at a different location for the day or animals are
out foraging at the time of the survey activities.
Negligible Impact and Small Numbers Analysis and Determination
NMFS typically includes our negligible impact and small numbers
analyses and determinations under the same section heading of our
Federal Register notices. Despite co-locating these terms, we
acknowledge that negligible impact and small numbers are distinct
standards under the MMPA and treat them as such. The analyses presented
below do not conflate the two standards; instead, each standard has
been considered independently, and we have applied the relevant factors
to inform our negligible impact and small numbers determinations.
NMFS has defined ``negligible impact'' in 50 CFR 216.103 as ``. . .
an impact resulting from the specified activity that cannot be
reasonably expected to, and is not reasonably likely to, adversely
affect the species or stock through effects on annual rates of
recruitment or survival.'' In making a negligible impact determination,
NMFS considers a variety of factors, including but not limited to: (1)
The number of anticipated mortalities; (2) the number and nature of
anticipated injuries; (3) the number, nature, intensity, and duration
of Level B harassment; and (4) the context in which the take occurs.
No injuries or mortalities are anticipated to occur as a result of
PISCO's rocky intertidal monitoring, and none are authorized. The
behavioral harassments that could occur would be of limited duration,
as researchers only conduct sampling one to two times per year at each
site for a total of 4-6 hours per sampling event. Therefore,
disturbance will be limited to a short duration, allowing pinnipeds to
reoccupy the sites within a short amount of time.
Some of the pinniped species may use some of the sites during
certain times of year to conduct pupping and/or breeding. However, some
of these species prefer to use the offshore islands for these
activities. At the sites where pups may be present, PISCO will
implement certain mitigation measures, such as no intentional flushing
if dependent pups are present, which will avoid mother/pup separation
and trampling of pups.
Of the three marine mammal species anticipated to occur in the
activity areas, none are listed under the ESA. Table 1 in this document
presents the abundance of each species or stock, the authorized take
estimates, and the percentage of the affected populations or stocks
that may be taken by harassment. Based on these estimates, PISCO would
take less than 1.1% of each species or stock. Because these are maximum
estimates, actual take numbers are likely to be lower, as some animals
may select other haulout sites the day the researchers are present.
Based on the analysis contained herein of the likely effects of the
specified activity on marine mammals and their habitat, and taking into
consideration the implementation of the mitigation and monitoring
measures, NMFS finds that the rocky intertidal monitoring program will
result in the incidental take of small numbers of marine mammals, by
Level B harassment only, and that the total taking from the rocky
intertidal monitoring program will have a negligible impact on the
affected species or stocks.
Table 1--Population Abundance Estimates, Total Authorized Level B Take, And Percentage of Population That May Be
Taken for the Potentially Affected Species During the Proposed Rocky Intertidal Monitoring Program
----------------------------------------------------------------------------------------------------------------
Total Percentage of
Species Abundance * authorized stock or
level B take population
----------------------------------------------------------------------------------------------------------------
Harbor Seal..................................................... \1\ 30,196 183 0.6-1.1
\2\ 16,165
California Sea Lion............................................. 296,750 60 0.02
Northern Elephant Seal.......................................... 124,000 30 0.03
----------------------------------------------------------------------------------------------------------------
* Abundance estimates are taken from the 2013 U.S. Pacific Marine Mammal Stock Assessments (Carretta et al.,
2014).
\1\ California stock abundance estimate;
\2\ Oregon/Washington stock abundance estimate
Impact on Availability of Affected Species or Stock for Taking for
Subsistence Uses
There are no relevant subsistence uses of marine mammals 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)
None of the marine mammals for which incidental take is authorized
are listed as threatened or endangered under the ESA. NMFS' Permits and
Conservation Division worked with the NMFS West Coast Regional Office
to ensure that Steller sea lions would be avoided and incidental take
would not occur. Therefore, NMFS has determined that issuance of the
IHA to PISCO under section 101(a)(5)(D) of the MMPA will have no effect
on species listed as threatened or endangered under the ESA.
National Environmental Policy Act (NEPA)
In 2012, we prepared an EA analyzing the potential effects to the
human environment from conducting rocky intertidal surveys along the
California and Oregon coasts and issued a FONSI on the issuance of an
IHA for PISCO's rocky intertidal surveys in accordance with section
6.01 of the NOAA Administrative Order 216-6
[[Page 73053]]
(Environmental Review Procedures for Implementing the National
Environmental Policy Act, May 20, 1999). PISCO's proposed activities
and impacts for 2013-2014 are within the scope of our 2012 EA and
FONSI. We have reviewed the 2012 EA and determined that there are no
new direct, indirect, or cumulative impacts to the human and natural
environment associated with the IHA requiring evaluation in a
supplemental EA and we, therefore, reaffirm the 2012 FONSI.
Authorization
As a result of these determinations, NMFS has authorized the take
of marine mammals incidental to PISCO's rocky intertidal monitoring
research activities, provided the previously mentioned mitigation,
monitoring, and reporting requirements are incorporated.
Dated: December 3, 2014.
Donna S. Wieting,
Director, Office of Protected Resources, National Marine Fisheries
Service.
[FR Doc. 2014-28807 Filed 12-8-14; 8:45 am]
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