[Federal Register Volume 82, Number 133 (Thursday, July 13, 2017)]
[Notices]
[Pages 32330-32344]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2017-14699]


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DEPARTMENT OF COMMERCE

National Oceanic and Atmospheric Administration

RIN 0648-XF119


Takes of Marine Mammals Incidental to Specified Activities; 
Taking Marine Mammals Incidental to Site Characterization Surveys off 
the Coast of New York

AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and 
Atmospheric Administration (NOAA), Commerce.

ACTION: Notice; issuance of an incidental harassment authorization.

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SUMMARY: 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 
Deepwater Wind, LLC, (DWW) to incidentally harass, by Level B 
harassment only, marine mammals during high-resolution geophysical 
(HRG) and geotechnical survey investigations associated with marine 
site characterization activities off the coast of New York in the area 
of the Commercial Lease of Submerged Lands for Renewable Energy 
Development on the Outer Continental Shelf (OCS-A 0486) (Lease Area) 
and along potential submarine cable routes to a landfall location in 
Easthampton, New York (``Submarine Cable Corridor'') (collectively the 
Lease Area and Submarine Cable Corridor are the Project Area).

DATES: This Authorization is effective from June 16, 2017 through June 
15, 2018.

FOR FURTHER INFORMATION CONTACT: Laura McCue, Office of Protected 
Resources, NMFS, (301) 427-8401. Electronic copies of the applications 
and supporting documents, as well as a list of the references cited in 
this document, may be obtained by visiting the Internet at: 
www.nmfs.noaa.gov/pr/permits/incidental/energy_other.htm. In case of 
problems accessing these documents, please call the contact listed 
above.

SUPPLEMENTARY INFORMATION: 

Background

    Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.) 
direct the Secretary of Commerce to allow, upon request, the 
incidental, but not intentional, taking of small numbers of marine 
mammals by U.S. citizens who engage in a specified activity (other than 
commercial fishing) within a specified geographical region if certain 
findings are made and either regulations are issued or, if the taking 
is limited to harassment, a notice of a proposed authorization is 
provided to the public for review.
    An authorization for incidental takings shall be granted if NMFS 
finds that the taking will have a negligible impact on the species or 
stock(s), will not have an unmitigable adverse impact on the 
availability of the species or stock(s) for subsistence uses (where 
relevant), and if the permissible methods of taking and requirements 
pertaining to the mitigation, monitoring and reporting of such takings 
are set forth.
    NMFS has defined ``negligible impact'' in 50 CFR 216.103 as an 
impact resulting from the specified activity that cannot be reasonably 
expected to, and is not reasonably likely to, we adversely affect the 
species or stock through effects on annual rates of recruitment or 
survival.
    The MMPA states that the term ``take'' means to harass, hunt, 
capture, kill or attempt to harass, hunt, capture, or kill any marine 
mammal.
    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).

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 
incidental harassment authorization) with respect to potential impacts 
on the human environment. Accordingly, NMFS prepared an Environmental 
Assessment (EA) to consider the environmental impacts associated with 
the issuance of the IHA.
    NMFS' EA will be made available at www.nmfs.noaa.gov/pr/permits/incidental/other_energy.htm at the time of the publication of this 
Federal Register notice.

Summary of Request

    On December 1, 2016, NMFS received application request from DWW for 
an IHA to take marine mammals incidental to 2017 geophysical survey 
investigations in the area of the Commercial Lease of Submerged Lands 
for Renewable Energy Development on the Outer Continental Shelf (OCS) 
lease area #OCS-A-0486 Lease Area and along potential submarine cable 
routes to a landfall location in Easthampton, New York (Project Area) 
designated and offered by the U.S. Bureau of Ocean Energy Management 
(BOEM), to support the development of an offshore wind project. DWW's 
request was for take of 18 species of marine mammals by Level B 
harassment of a small number of 18 species and take by Level A 
harassment of 3 species. Neither DWW nor NMFS expects mortality to 
result from this activity; and therefore, an IHA is appropriate. NMFS 
determined that the

[[Page 32331]]

application was adequate and complete on April 27, 2017.

Description of the Specified Activity

Overview

    DWW plans to conduct a geophysical and geotechnical survey in the 
Project Area to support the characterization of the existing seabed and 
subsurface geological conditions in the Project Area. Surveys will 
include the use of the following equipment: Shallow and medium-
penetration sub-bottom profiler (chirper, boomer, and sparker) used 
during the HRG survey, multi-beam depth sounder, side-scan sonar, 
vibracores, and cone penetration tests (CPTs). The planned geophysical 
survey activities would occur for 168 days beginning in June 2017, and 
geotechnical survey activities would take place in June 2017 and last 
for approximately 75 days. Take, by Level B Harassment only of 
individuals of 18 species of marine mammals is anticipated to result 
from the specified activities. No serious injury or mortality is 
expected from DWW's HRG and geotechnical surveys. A detailed 
description of the planned marine site characterization project is 
provided in the Federal Register notice for the proposed IHA (82 FR 
22250; May 12, 2017). Since that time, no changes have been made to the 
planned marine site characterization survey activities. Therefore, a 
detailed description is not provided here. Please refer to that Federal 
Register notice for the description of the specific activity.

Comments and Responses

    A notice of NMFS's proposal to issue an IHA to DWW was published in 
the Federal Register on May 12, 2017 (80 FR 22250). That notice 
described, in detail, DWW's activity, the marine mammal species that 
may be affected by the activity and the anticipated effects on marine 
mammals. During the 30-day public comment period, NMFS received 
comments from the Marine Mammal Commission (Commission) and one private 
citizen. Only the Commission had substantive comments.
    Comment 1: The Commission noted a discrepancy between the source 
levels used in this project and the a recently issued IHA for another 
marine site characterization project (82 FR 20577) to Ocean Wind, LLC 
(Ocean Wind) and recommended that NMFS (1) explain why the sparker 
source levels for the two projects were considerably different, (2) 
encourage applicants to disclose the methods used in measuring and 
calculating source levels of the various sound sources, and (3) ensure 
accuracy and consistency in source levels used by applicants for 
different projects with similar types of HRG equipment.
    Response: NMFS was provided with proprietary information from Ocean 
Wind and was unable to use that data in the analysis for DWW. The 
source levels that were used for this project were described in the 
notice of our proposed IHA (82 FR 22250; May 12, 2017) but included 
source levels from the manufacturer and from measurements taken in situ 
(Crocker and Fratantonio 2016). In the future, we will encourage 
applicants to disclose their data to the public and will continue to 
use all publicly available data to ensure consistency and accuracy for 
similar projects.
    Comment 2: The Commission does not believe that take by Level A 
harassment would likely occur from project activities because of the 
very small Level A zones (e.g. 5.12 m for harbor porpoise and 0.65 m 
for harbor seals and gray seals) and the increased likelihood that take 
by Level A harassment could be avoided with the implementation of the 
minimum 200 meter (m) shutdown zone. The Commission recommends that 
NMFS use a consistent approach for authorizing Level A harassment 
takes, especially in situations when mitigation measure implementation 
very likely would preclude taking in the respective Level A harassment 
zones.
    Response: NMFS agrees with the Commission and believes that all 
modeled take by Level A harassment could be avoided with the 
implementation of the shutdown zones. We have removed the authorization 
for Level A take for harbor porpoise, harbor seals, and gray seals.
    Comment 3: The Commission recommends that, until the behavior 
thresholds are updated, NMFS require applicants to use the 120- rather 
than 160-decibel (dB) re 1 micropascal ([mu]Pa) threshold for acoustic, 
non-impulsive sources (e.g., chirp-type sub-bottom profilers, 
echosounders, and other sonars including side-scan and fish-finding).
    Response: NMFS considers sub-bottom profilers to be impulsive 
sources; therefore, 160 dB threshold will continue to be used. 
Additionally, BOEM listed sparkers as impulsive sources (BOEM 2016). 
The 120-dB threshold is typically associated with continuous sources. 
Continuous sounds are those whose sound pressure level remains above 
that of the ambient sound, with negligibly small fluctuations in level 
(NIOSH, 1998; ANSI, 2005). Intermittent sounds are defined as sounds 
with interrupted levels of low or no sound (NIOSH, 1998). Sub-bottom 
profiler signals are intermittent sounds. Intermittent sounds can 
further be defined as either impulsive or non-impulsive. Impulsive 
sounds have been defined as sounds which are typically transient, brief 
(<1 sec), broadband, and consist of a high peak pressure with rapid 
rise time and rapid decay (ANSI, 1986; NIOSH, 1998). Non-impulsive 
sounds typically have more gradual rise times and longer decays (ANSI, 
1995; NIOSH, 1998). Sub-bottom profiler signals have durations that are 
typically very brief (<1 sec), with temporal characteristics that more 
closely resemble those of impulsive sounds than non-impulsive sounds. 
With regard to behavioral thresholds, we consider the temporal and 
spectral characteristics of sub-bottom profiler signals to more closely 
resemble those of an impulse sound rather than a continuous sound. The 
160-dB threshold is typically associated with impulsive sources. 
Therefore, the 160-dB threshold (typically associated with impulsive 
sources) is more appropriate than the 120-dB threshold (typically 
associated with continuous sources) for estimating takes by behavioral 
harassment incidental to use of such sources.
    Comment 4: The Commission recommends that NMFS require DWW to 
monitor the full extent of the Level B harassment zones for the purpose 
of enumerating Level B harassment takes and documenting any behavioral 
responses observed.
    Response: The Level B zones extend to 3,556 m for vibracore, 893 m 
for sparkers, and 500 m for dynamic positioning (DP) thrusters. It is 
not practicable for the applicant to monitor these zones. Therefore, 
NMFS is clarifying that the monitoring measures include Protected 
Species Observers (PSO)s will monitor all visible waters to the extent 
practicable so as to not undermine effectiveness of shutdown zone. The 
data collection and reporting requirements will include providing an 
estimate of the observable distance recorded at each shift change; and, 
if the entire Level B zone was not able to be monitored, DWW apply a 
correction to the observed marine mammals in the 160 dB zone to 
estimate the number of animals that were likely not detected based on 
the area that was not monitored.

Description of Marine Mammals in the Area of the Specified Activity

    There are 36 species of marine mammals that potentially occur in 
the Northwest Atlantic OCS region (BOEM,

[[Page 32332]]

2014) (Table 1). The majority of these species are pelagic and/or 
northern species, or are so rarely sighted that their presence in the 
Project Area is unlikely. Eighteen of these species are included in the 
take estimate for this project based on seasonal density in the Project 
area. The other 18 species are not included in the take request because 
they have low densities in the Project area, are rarely sighted there, 
and are considered very unlikely to occur in the area.
    Further information on the biology, ecology, abundance, and 
distribution of those species likely to occur in the Project Area can 
be found in section 4 of DWW's application, and the NMFS Marine Mammal 
Stock Assessment Reports (see Waring et al., 2016), which are available 
online at: http://www.nmfs.noaa.gov/pr/species/. A detailed description 
of the of the species likely to be affected by the marine site 
characterization project, including brief introductions to the species 
and relevant stocks as well as available information regarding 
population trends and threats, and information regarding local 
occurrence, were provided in the Federal Register notice for the 
proposed IHA (82 FR 22250; May 12, 2017). Since that time, we are not 
aware of any changes in the status of these species and stocks; 
therefore, detailed descriptions are not provided here. Please refer to 
that Federal Register notice for these descriptions. Please also refer 
to NMFS' Web site (www.nmfs.noaa.gov/pr/species/mammals/) for 
generalized species accounts.

               Table 1--Marine Mammals Known To Occur in the Waters off the Northwest Atlantic OCS
----------------------------------------------------------------------------------------------------------------
                                                   NMFS MMPA and    Stock abundance              Occurrence and
                                                    ESA status;     (CV,Nmin, most               seasonality in
          Common Name                 Stock       strategic (Y/N)  recent abundance   PBR \3\    the NW Atlantic
                                                        \1\           survey) \2\                      OCS
----------------------------------------------------------------------------------------------------------------
                                           Toothed whale (Odontoceti)
----------------------------------------------------------------------------------------------------------------
Atlantic white-sided dolphin    W. North          -; N...........  48,819 (0.61;           304  rare.
 (Lagenorhynchus acutus).        Atlantic.                          30,403; n/a).
Atlantic spotted dolphin        W. North          -; N...........  44,715 (0.43;           316  rare.
 (Stenella frontalis).           Atlantic.                          31,610; n/a).
Bottlenose dolphin (Tursiops    W. North          -; N...........  77,532 (0.40;           561  Common year
 truncatus).                     Atlantic,                          56,053; 2011).               round.
                                 Offshore.
Clymene Dolphin (Stenella       W. North          -; N...........  Unknown (unk;         Undet  rare.
 clymene).                       Atlantic.                          unk; n/a).
Pantropical Spotted Dolphin     W. North          -; N...........  3,333 (0.91;             17  rare.
 (Stenella attenuata).           Atlantic.                          1,733; n/a).
Risso's dolphin (Grampus        W. North          -; N...........  18,250 (0.46;           126  rare.
 griseus).                       Atlantic.                          12,619; n/a).
Short-beaked common dolphin     W. North          -; N...........  70,184 (0.28;           557  Common year
 (Delphinus delphis).            Atlantic.                          55,690; 2011).               round.
Striped dolphin (Stenella       W. North          -; N...........  54,807 (0.3;            428  rare.
 coeruleoalba).                  Atlantic.                          42,804; n/a).
Spinner Dolphin (Stenella       W. North          -; N...........  Unknown (unk;         Undet  rare.
 longirostris).                  Atlantic.                          unk; n/a).
White-beaked dolphin            W. North          -; N...........  2,003 (0.94;             10  rare.
 (Lagenorhynchus albirostris).   Atlantic.                          1,023; n/a).
Harbor porpoise (Phocoena       Gulf of Maine/    -; N...........  79,833 (0.32;           706  Common year
 phocoena).                      Bay of Fundy.                      61,415; 2011).               round.
Killer whale (Orcinus orca)...  W. North          -; N...........  Unknown (unk;         Undet  rare.
                                 Atlantic.                          unk; n/a).
False killer whale (Pseudorca   W. North          -; Y...........  442 (1.06; 212;         2.1  rare.
 crassidens).                    Atlantic.                          n/a).
Long-finned pilot whale         W. North          -; Y...........  5,636 (0.63;             35  rare.
 (Globicephala melas).           Atlantic.                          3,464; n/a).
Short-finned pilot whale        W. North          -; Y...........  21,515 (0.37;           159  rare.
 (Globicephala macrorhynchus).   Atlantic.                          15,913; n/a).
Sperm whale (Physeter           North Atlantic..  E; Y...........  2,288 (0.28;            3.6  Year round in
 macrocephalus).                                                    1,815; n/a).                 continental
                                                                                                 shelf and slope
                                                                                                 waters, occur
                                                                                                 seasonally to
                                                                                                 forage.
Pygmy sperm whale (Kogia        W. North          -; N...........  3,785 b/(0.47;           26  rare.
 breviceps).                     Atlantic.                          2,598; n/a).
Dwarf sperm whale (Kogia sima)  W. North          -; N...........  3,785 b/(0.47;           26  rare.
                                 Atlantic.                          2,598; n/a).
Cuvier's beaked whale (Ziphius  W. North          -; N...........  6,532 (0.32;             50  rare.
 cavirostris).                   Atlantic.                          5,021; n/a).
Blainville's beaked whale       W. North          -; N...........  7,092 c/(0.54;           46  rare.
 (Mesoplodon densirostris).      Atlantic.                          4,632; n/a).
Gervais' beaked whale           W. North          -; N...........  7,092 c/(0.54;           46  rare.
 (Mesoplodon europaeus).         Atlantic.                          4,632; n/a).
True's beaked whale             W. North          -; N...........  7,092 c/(0.54;           46  rare.
 (Mesoplodon mirus).             Atlantic.                          4,632; n/a).
Sowerby's Beaked Whale          W. North          -; N...........  7,092 c/(0.54;           46  rare.
 (Mesoplodon bidens).            Atlantic.                          4,632; n/a).

[[Page 32333]]

 
Melon-headed whale              W. North          -; N...........  Unknown (unk;         Undet  rare.
 (Peponocephala electra).        Atlantic.                          unk; n/a).
----------------------------------------------------------------------------------------------------------------
                                            Baleen whales (Mysticeti)
----------------------------------------------------------------------------------------------------------------
Minke whale (Balaenoptera       Canadian East     -; N...........  2,591 (0.81;            162  Year round in
 acutorostrata).                 Coast.                             1,425; n/a).                 continental
                                                                                                 shelf and slope
                                                                                                 waters, occur
                                                                                                 seasonally to
                                                                                                 forage.
Blue whale (Balaenoptera        W. North          E; Y...........  Unknown (unk;           0.9  Year round in
 musculus).                      Atlantic.                          440; n/a).                   continental
                                                                                                 shelf and slope
                                                                                                 waters, occur
                                                                                                 seasonally to
                                                                                                 forage.
Fin whale (Balaenoptera         W. North          E; Y...........  1,618 (0.33;            2.5  Year round in
 physalus).                      Atlantic.                          1,234; n/a).                 continental
                                                                                                 shelf and slope
                                                                                                 waters, occur
                                                                                                 seasonally to
                                                                                                 forage.
Humpback whale (Megaptera       Gulf of Maine...  -; N...........  823 (0; 823; n/         2.7  Common year
 novaeangliae).                                                     a).                          round.
North Atlantic right whale      W. North          E; Y...........  440 (0; 440; n/           1  Year round in
 (Eubalaena glacialis).          Atlantic.                          a).                          continental
                                                                                                 shelf and slope
                                                                                                 waters, occur
                                                                                                 seasonally to
                                                                                                 forage.
Sei whale (Balaenoptera         Nova Scotia.....  E; Y...........  357 (0.52; 236;         0.5  Year round in
 borealis).                                                         n/a).                        continental
                                                                                                 shelf and slope
                                                                                                 waters, occur
                                                                                                 seasonally to
                                                                                                 forage.
----------------------------------------------------------------------------------------------------------------
                                            Earless seals (Phocidae)
----------------------------------------------------------------------------------------------------------------
Gray seals (Halichoerus         North Atlantic..  -; N...........  505,000 (unk;         Undet  Unlikely.
 grypus).                                                           unk; n/a).
Harbor seals (Phoca vitulina).  W. North          -; N...........  75,834 (0.15;         2,006  Common year
                                 Atlantic.                          66,884; 2012).               round.
Hooded seals (Cystophora        W. North          -; N...........  Unknown (unk;         Undet  rare.
 cristata).                      Atlantic.                          unk; n/a).
Harp seal (Phoca groenlandica)  North Atlantic..  -; N...........  Unknown (unk;         Undet  rare.
                                                                    unk; n/a).
----------------------------------------------------------------------------------------------------------------
\1\ ESA status: Endangered (E), Threatened (T)/MMPA status: Depleted (D). A dash (-) indicates that the species
  is not listed under the ESA or designated as depleted under the MMPA. Under the MMPA, a strategic stock is one
  for which the level of direct human-caused mortality exceeds PBR (see footnote 3) or which is determined to be
  declining and likely to be listed under the ESA within the foreseeable future. Any species or stock listed
  under the ESA is automatically designated under the MMPA as depleted and as a strategic stock.
\2\ CV is coefficient of variation; Nmin is the minimum estimate of stock abundance. In some cases, CV is not
  applicable. For certain stocks, abundance estimates are actual counts of animals and there is no associated
  CV. The most recent abundance survey that is reflected in the abundance estimate is presented; there may be
  more recent surveys that have not yet been incorporated into the estimate. All values presented here are from
  the 2016 draft Atlantic SARs.
\3\ Potential biological removal, defined by the MMPA as the maximum number of animals, not including natural
  mortalities, that may be removed from a marine mammal stock while allowing that stock to reach or maintain its
  optimum sustainable population size (OSP).

Potential Effects of the Specified Activity on Marine Mammals and Their 
Habitat

    The effects of underwater noise from HRG and geotechnical 
activities for the marine site characterization project have the 
potential to result in behavioral harassment of marine mammals in the 
vicinity of the action area. The Federal Register notice for the 
proposed IHA (82 FR 22250; May 12, 2017) included a discussion of the 
effects of anthropogenic noise on marine mammals. That information is 
not repeated here. Please refer to that Federal Register notice for 
that information.

Estimated Take by Incidental Harassment

    This section provides the number of incidental takes authorized 
through this IHA, which informed both NMFS' consideration of whether 
the number of takes is ``small'' and the negligible impact 
determination.
    Harassment is the only type of take expected to result from these 
activities. 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).
    Authorized takes would be by Level B harassment, in the form of 
disruption of behavioral patterns resulting from exposure to HRG and 
geotechnical surveys. The proposed mitigation and monitoring measures 
(when considered in combination with the operational parameters and 
characteristics of the

[[Page 32334]]

sound sources) are expected to alleviate the potential for Level A take 
of all species. In addition, as described previously, no mortality is 
anticipated or proposed to be authorized for this activity. Below we 
describe how the take is estimated.
    In summary, we estimate take by considering: (1) Acoustic 
thresholds above which NMFS believes the best available science 
indicates marine mammals will be behaviorally harassed or incur some 
degree of permanent hearing impairment; (2) The area or volume of water 
that will be ensonified above these levels in a day; (3) The density or 
occurrence of marine mammals within these ensonified areas; and, (4) 
the number of days of activities. Below, we describe these components 
in more detail and present the proposed take estimate.

Acoustic Thresholds

    Using the best available science, NMFS has developed acoustic 
thresholds that identify the received level of underwater sound above 
which exposed marine mammals would be reasonably expected to be 
behaviorally harassed (equated to Level B harassment) or to incur 
permanent threshold shift (PTS) of some degree (equated to Level A 
harassment).
    Level B Harassment for non-explosive sources--Though significantly 
driven by received level, the onset of behavioral disturbance from 
anthropogenic noise exposure is also informed to varying degrees by 
other factors related to the source (e.g., frequency, predictability, 
duty cycle), the environment (e.g., bathymetry), and the receiving 
animals (hearing, motivation, experience, demography, behavioral 
context) and can be difficult to predict (Southall et al., 2007, 
Ellison et al., 2011). Based on what the available science indicates 
and the practical need to use a threshold based on a factor that is 
both predictable and measurable for most activities, NMFS uses a 
generalized acoustic threshold based on received level to estimate the 
onset of behavioral harassment. NMFS predicts that marine mammals are 
likely to be behaviorally harassed in a manner we consider Level B 
harassment when exposed to underwater anthropogenic noise above 
received levels of 120 dB re 1 [mu]Pa ((root mean square (rms)) for 
continuous (e.g. vibratory pile-driving, drilling) and above 160 dB re 
1 [mu]Pa (rms) for non-explosive impulsive (e.g., seismic airguns) or 
intermittent (e.g., scientific sonar) sources.
    DWW's planned activity includes the use of continuous (vibracore 
and DP thruster) and impulsive (e.g. sparkers) sources; and therefore, 
the 120 and 160 dB re 1 [mu]Pa (rms) are applicable.
    Level A harassment for non-explosive sources--NMFS' Technical 
Guidance for Assessing the Effects of Anthropogenic Sound on Marine 
Mammal Hearing (Technical Guidance, 2016) identifies dual criteria to 
assess auditory injury (Level A harassment) to five different marine 
mammal groups (based on hearing sensitivity) as a result of exposure to 
noise from two different types of sources (impulsive or non-impulsive). 
DWW's marine site characterization activities include the use of 
impulsive (sparkers) and non-impulsive (vibracore and DP thruster) 
sources.
    These thresholds were developed by compiling and synthesizing the 
best available science and soliciting input multiple times from both 
the public and peer reviewers to inform the final product, and are 
provided in Table 2 below. The references, analysis, and methodology 
used in the development of the thresholds are described in NMFS 2016 
Technical Guidance, which may be accessed at: http://www.nmfs.noaa.gov/pr/acoustics/guidelines.htm.

          Table 2--Summary of PTS Onset Acoustic Thresholds \1\
------------------------------------------------------------------------
                                     PTS onset acoustic thresholds *
                                            (received level)
         Hearing Group         -----------------------------------------
                                       Impulsive          Non-impulsive
------------------------------------------------------------------------
Low-frequency cetaceans.......  Cell 1--Lpk,flat: 219   Cell 2--
                                 dB, LE,LF,24h: 183 dB.  LE,LF,24h: 199
                                                         dB.
Mid-frequency cetaceans.......  Cell 3--Lpk,flat: 230   Cell 4--
                                 dB, LE,MF,24h: 185 dB.  LE,MF,24h: 198
                                                         dB.
High-frequency cetaceans......  Cell 5--Lpk,flat: 202   Cell 6--
                                 dB, LE,HF,24h: 155      LE,HF,24h: 173
                                 dB..                    dB.
Phocid Pinnipeds (underwaters)  Cell 7--Lpk,flat: 218   Cell 8--
                                 dB, LE,PW,24h: 185 dB.  LE,PW,24h: 201
                                                         dB.
Otariid Pinnipeds (underwater)  Cell 9--Lpk,flat: 232   Cell 10--
                                 dB, LE,OW,24h: 203 dB.  LE,OW,24h: 219
                                                         dB.
------------------------------------------------------------------------
\1\ NMFS 2016.
* Dual metric acoustic thresholds for impulsive sounds: Use whichever
  results in the largest isopleth for calculating PTS onset. If a non-
  impulsive sound has the potential of exceeding the peak sound pressure
  level thresholds associated with impulsive sounds, these thresholds
  should also be considered.

Ensonified Area

    Here, we describe operational and environmental parameters of the 
activity that will feed into identifying the area ensonified above the 
acoustic thresholds.
    DWW took into consideration sound sources using the potential 
operational parameters, bathymetry, geoacoustic properties of the 
Project Area, time of year, and marine mammal hearing ranges. Results 
of a sound source verification study in a nearby location showed that 
estimated maximum distance to the 160 dB re 1 [mu]Pa (rms) MMPA 
threshold for all water depths for the HRG survey sub-bottom profilers 
(the HRG survey equipment with the greatest potential for effect on 
marine mammal) was approximately 447 m from the source, which equated 
to a propagation loss coefficient of 20logR (equivalent to spherical 
spreading). The estimated maximum critical distance to the 120 dB re 1 
[mu]Pa (rms) MMPA threshold for all water depths for the vibracore was 
approximately 1,778 from the source using spherical spreading. For 
sparkers and vibracore, we doubled these distances to conservatively 
account for the uncertainty in predicting propagation loss in a similar 
but different location. The estimated maximum critical distance to the 
120 dB re 1 [mu]Pa (rms) MMPA threshold for all water depths for the 
drill ship DP thruster was approximately 500 m from the source based on 
hydroacoustic modeling results (Subacoustech 2016). DWW and NMFS 
believe that these estimates represent a conservative scenario and that 
the actual distances to the Level B harassment threshold may be 
shorter, as the calculated distance was doubled for the sparker system 
and vibracore, the SL for the sparker system was conservatively based 
on a source that was louder than the equipment planned for use in this 
project, and there are some sound measurements taken in the Northeast 
that suggest a

[[Page 32335]]

higher spreading coefficient (which would result in a shorter distance) 
may be applicable.
    The Zone of influence (ZOI) is the extent of the ensonified zone in 
a given day. The ZOI was calculated using the following equations:

 Stationary source (e.g. DP thruster and vibracore): [pi]r\2\
 Mobile source (e.g. sparkers): (distance/day * 2r) + [pi]r\2\

    Where distance is the maximum survey trackline per day (110 
kilometer (km)) and r is the distance to the 160 dB (for impulsive 
sources) and 120 dB (for non-impulsive sources) isopleths. The 
isopleths for sparkers and vibracores were calculated using 20logR, and 
the resulting isopleths were doubled as a conservative mechanism to 
allow for any uncertainty in propagation loss. The isopleths for the DP 
thruster was calculated using a transmission loss coefficient of 11.12, 
which was based on field verification study results (Subacoustech 
2016).

                                         Table 3--User Spreadsheet Input
----------------------------------------------------------------------------------------------------------------
                                          Vibracore             DP thruster                  Sparker
----------------------------------------------------------------------------------------------------------------
Spreadsheet Tab Used..............  (A) Non-impulsive-     (A) Non-impulsive-    (F) Impulsive-Mobile.
                                     Stat-Cont.             Stat-Cont.
Source Level......................  185 dB RMS...........  150 dB RMS..........  186 dB SEL.
Weighting Factor Adjustment.......  1.7, 6.2, 20.........  1.75, 5.............  2.75, 1.2.
Activity Duration (hours) within    1....................  1, 3................  n/a.
 24-h period.
Propogation (xLogR)...............  20...................  11.12...............  n/a.
Distance of source level            1....................  1...................  n/a.
 measurement (meters).
Source velocity (meters/second)...  n/a..................  n/a.................  1.93.
1/Repetition rate (seconds).......  n/a..................  n/a.................  2.48.
----------------------------------------------------------------------------------------------------------------

    DWW used the user spreadsheet to calculate the isopleth for the 
loudest sources (sparker, vibracore, DP thruster). The sparker was 
calculated with the following conditions: source level of 186 dB SEL, 
source velocity of 1.93 meters per second (m/s), repetition rate of 
2.48, and a weighting factor adjustment of 1.2 and 2.75 based on the 
appropriate broadband source. Isopleths were less than 1 m for all 
hearing groups (Table 4) except high-frequency cetaceans, which was 
5.12 m. Take by Level A harassment can be avoided with the 
implementation of the shutdowns during all planned activities. Shutdown 
zones exceed the Level A zones for sparkers. The vibracore used the 
following parameters: source level of 185 rms, distance of source level 
measurement at 1 m, duration of 1 hour, propagation loss of 20, and 
weighting factor adjustment of 1.7, 6.2, and 20 based on the 
spectrograms for this equipment. Isopleths are summarized in Table 4 
and no Level A takes are requested during the use of the vibracore. The 
DP thruster was defined as non-impulsive static continuous source with 
a source level of 150 dB rms, Propagation loss of 11.12 based on the 
spectrograms for this equipment (Subacoustech 2016), an activity 
duration of 1 and 3 hours and weighting factor adjustment of 1.7 and 5. 
Isopleths were less than 3 m for all hearing groups (Table 4); 
therefore, no Level A takes were requested for this source.

                                                 Table 4--Maximum Worst-Case Distance (m) and Area (km\2\) to the Level A and Level B Thresholds
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
 
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
         Hearing group            SELcum       Equipment           Vibracore Operations: HPC or Rossfelder Corer
                                threshold
                                   (dB)
                                         DP Thruster            800 Joule Geo      Sparker System
                                                                   Resources
                                                                    Sparker
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
                                               Source PLS                            185 dB RMS
                                         150 dB RMS               186 dB SEL        186 dB SEL,
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
                                                                                             Level A
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
                                Threshold      WFA* (kHz)            1.7                6.2                 20                1.7                 5                 2.75               1.2
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
Low-Frequency Cetaceans.......        199  PTS Isopleth to    11.97 m, 0 km\2\.  .................  .................  0.06 m, 0 km\2\..  .................  1.29 m, 0.283      1.30 m, 0.287
                                            threshold                                                                                                         km\2\.             km\2\.
                                            (meters).
Mid-Frequency Cetaceans.......        198  .................  .................  .................  12.96 m, 0.001 km  .................  0.03 m, 0 km\2\..  0.02 m, 0.005      ................
                                                                                                     \2\.                                                     km\2\.
High-Frequency Cetaceans......        173  .................  .................  .................  207.58 m, 0.135    .................  2.17 m, 0 km\2\..  5.12 m, 1.127      ................
                                                                                                     km\2\.                                                   km\2\.
Phocid Pinnipeds..............        201  .................  .................  9.51 m, 0 km\2\..  .................  .................  0.11 m, 0 km\2\..  0.65 m, 0.144      ................
                                                                                                                                                              km\2\.
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
                                                                                             Level B
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
                                Threshold      Source PLS                            185 dBRMS
                                          150 dBRMS               213 dBRMS          213 dBRMS,
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
All Marine Mammals............        120  Level B                              3,556 m, 39.74 km\2\
                                            Harassment
                                            Distance.
                                      499 m, 0.78 km\2\                          .................
                                      160
                                                              893 m, 199.0481    893 m, 199.0481
                                                               km\2\.             km\2\..
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
* Weighting Factor Adjustment.


[[Page 32336]]

Marine Mammal Occurrence

    In this section we provide the information about the presence, 
density, or group dynamics of marine mammals that will inform the take 
calculations.
    DWW estimated species densities within the planned project area in 
order to estimate the number of marine mammal exposures to sound levels 
above the 120 dB Level B harassment threshold for continuous noise 
(i.e., DP thrusters and vibracore) and the 160 dB Level B harassment 
threshold for intermittent, impulsive noise (i.e., sparkers). Research 
indicates that marine mammals generally have extremely fine auditory 
temporal resolution and can detect each signal separately (e.g., Au et 
al., 1988; Dolphin et al., 1995; Supin and Popov 1995; Mooney et al., 
2009b), especially for species with echolocation capabilities. 
Therefore, it is likely that marine mammals would perceive the acoustic 
signals associated with the HRG survey equipment as being intermittent 
rather than continuous, and we base our takes from these sources on 
exposures to the 160 dB threshold.
    The data used as the basis for estimating cetacean density (``D'') 
for the Lease Area are sightings per unit effort (SPUE) derived by Duke 
University (Roberts et al., 2016). For pinnipeds, the only available 
comprehensive data for seal abundance is the Northeast Navy Operations 
Area (OPAREA) Density Estimates (DoN 2007). SPUE (or, the relative 
abundance of species) is derived by using a measure of survey effort 
and number of individual cetaceans sighted. SPUE allows for comparison 
between discrete units of time (i.e. seasons) and space within a 
project area (Shoop and Kenney 1992). The Duke University (Roberts et 
al., 2016) cetacean density data represent models derived from 
aggregating line-transect surveys conducted over 23 years by 5 
institutions (NMFS Northeast Fisheries Science Center (NEFSC), New 
Jersey Department of Environmental Protection (NJDEP), NMFS Southeast 
Fisheries Science Center (SEFSC), University of North Carolina 
Wilmington (UNCW), Virginia Aquarium & Marine Science Center (VAMSC)), 
the results of which are freely available online at the Ocean 
Biogeographic Information System Spatial Ecological Analysis of 
Megavertebrate Populations (OBIS-SEAMAP) repository. The datasets for 
each species were downloaded from OBIS-SEAMAP and were modeled as 
estimated mean year-round abundance (number of individual animals) per 
grid cell (100 km by 100 km) for most species. For certain species, the 
model predicted monthly mean abundance rather than mean year-round 
abundance, for which the annual mean abundance was calculated using 
Spatial Analyst tools in ArcGIS. Based on the annual mean abundance 
datasets, the mean density (animals/km\2\) was calculated in ArcGIS by 
averaging the abundance of animals within the Project Area and dividing 
by 100 to get animals/km\2\. The OPAREA Density Estimates (DoN 2007) 
used for pinniped densities were based on data collected through NMFS 
NWFSC aerial surveys conducted between 1998 and 2005.

Take Calculation and Estimation

    Here we describe how the information provided above is brought 
together to produce a quantitative take estimate.
    Estimated takes were calculated by multiplying the species density 
(animals per km\2\) by the appropriate ZOI, multiplied by the number of 
appropriate days (e.g. 168 for HRG activities or 53 days for 
vibracoring or 22 days for DP thruster during CPT) of the specified 
activity. A detailed description of the acoustic modeling used to 
calculate zones of influence is provided in DWW's IHA application (also 
see the discussion in the Mitigation Measures section below).
    DWW used a distance to the 160 dB Level B threshold of 447 m, which 
was doubled to be conservative for any uncertainty in propagation loss, 
for a maximum distance of 894 m for the sparker system. The ZOI of 
199.048 km\2\ for the sparker system and the survey period of a 
conservative 168 days, which includes estimated weather downtime, was 
used to estimate take from use of the HRG survey equipment during 
geophysical survey activities. The ZOI is based on the worst case 
(since it assumes the higher powered Dura-Spark 240 System sparker will 
be operating all the time) and a maximum survey trackline of 110 km (68 
mi) per day. The resulting take estimates (rounded to the nearest whole 
number) are presented in Table 5.
    DWW used a maximum distance to the 120 dB Level B threshold of 499 
m for DP thrusters. The ZOI of 0.782 km\2\ and the maximum DP thruster 
use period of 22 days were used to estimate take from use of the DP 
thruster during geotechnical survey activities.
    DWW used a distance to the 120 dB Level B zone of 1,778 m, which 
was doubled to be conservative, for a maximum distance of 3,556 m for 
vibracore. The ZOI of 39.738 km\2\ and a maximum vibracore use period 
of 53 days were used to estimate take from use of the vibracore during 
geotechnical survey activities. The resulting take estimates (rounded 
to the nearest whole number) based upon these conservative assumptions 
are presented in Table 5.
    DWW's requested take numbers are provided in Table 5 and are also 
the number of takes NMFS is authorizing. DWW's calculations do not take 
into account whether a single animal is harassed multiple times or 
whether each exposure is a different animal. Therefore, the numbers in 
Tables 5 are the maximum number of animals that may be harassed during 
the HRG and geotechnical surveys (i.e., DWW assumes that each exposure 
event is a different animal). These estimates do not account for 
prescribed mitigation measures that DWW would implement during the 
specified activities and the fact that shutdown/powerdown procedures 
shall be implemented if an animal enters within 200 m of the vessel 
during any activity and within 400 m when the sparkers are operating, 
further reducing the potential for any takes to occur during these 
activities. The take numbers in Table 5 were reduced from the proposed 
IHA due to a change in the number of days of operation of the vibracore 
and CPT. In the proposed IHA, we conservatively estimated the maximum 
number of days of geotechnical activities (75) for each type of 
activity. Here we have reduced the total number of days for each source 
(53 days for vibracore and 22 days of DP thruster use during CPT) since 
they will not be running on the same day.
    When NMFS Technical Guidance (2016) was published, in recognition 
of the fact that ensonified area/volume could be more technically 
challenging to predict because of the duration component in the new 
thresholds, we developed a User Spreadsheet that includes tools to help 
predict a simple isopleth that can be used in conjunction with marine 
mammal density or occurrence to help predict takes. We note that 
because of some of the assumptions included in the methods used for 
these tools, we anticipate that isopleths produced are typically going 
to be overestimates of some degree, which will result in some degree of 
overestimate of Level A take. However, these tools offer the best way 
to predict appropriate isopleths when more sophisticated 3D modeling 
methods are not available, and NMFS continues to develop ways to 
quantitatively refine these tools, and will qualitatively address the 
output where appropriate. For mobile sources, the User Spreadsheet 
predicts the closest distance at which a stationary animal would not 
incur PTS if the sound source traveled by the animal in a straight line

[[Page 32337]]

at a constant speed. Inputs used in the User Spreadsheet, and the 
resulting isopleths are reported in Tables 3 and 4.
[GRAPHIC] [TIFF OMITTED] TN13JY17.003

Mitigation 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 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 (latter not applicable for this action). NMFS

[[Page 32338]]

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 such 
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.
    With NMFS' input during the application process, and as per the 
BOEM Lease, DWW will implement the following mitigation measures during 
site characterization surveys utilizing HRG survey equipment and use of 
the DP thruster and vibracore. The mitigation measures outlined in this 
section are based on protocols and procedures that have been 
successfully implemented and resulted in no observed take of marine 
mammals for similar offshore projects and previously approved by NMFS 
(ESS 2013; Dominion 2013 and 2014).

Marine Mammal Exclusion Zones

    PSOs will monitor the following exclusion/monitoring zones for the 
presence of marine mammals:
     A 200-m exclusion zone during all geophysical and 
geotechnical operations.
     A 400-m exclusion zone during the use of sparkers.
    These exclusion zones are exclusion zone specified in stipulations 
of the OCS-A 0486 Lease Agreement.
     A 208-m exclusion zone for harbor porpoise only, during 
vibracore activities, only.

Visual Monitoring

    Visual monitoring of the established exclusion zone(s) s will be 
performed by qualified and NMFS-approved PSOs, the resumes of whom will 
be provided to NMFS for review and approval prior to the start of 
survey activities. Observer qualifications will include direct field 
experience on a marine mammal observation vessel and/or aerial surveys 
in the Atlantic Ocean/Gulf of Mexico. An observer team comprising a 
minimum of four NMFS-approved PSOs and two certified Passive Acoustic 
Monitoring (PAM) operators (PAM operators will not function as PSOs), 
operating in shifts, will be stationed aboard the survey vessel. PSOs 
and PAM operators will work in shifts such that no one monitor will 
work more than 4 consecutive hours without a 2-hour break or longer 
than 12 hours during any 24-hour period. Each PSO will monitor 360 
degrees of all visible waters to the extent practicable so as to not 
undermine effectiveness of shutdown zone monitoring..
    PSOs will be responsible for visually monitoring and identifying 
marine mammals approaching or within the established exclusion zone(s) 
during survey activities. It will be the responsibility of the Lead PSO 
on duty to communicate the presence of marine mammals as well as to 
communicate and enforce the action(s) that are necessary to ensure 
mitigation and monitoring requirements are implemented as appropriate. 
PAM operators will communicate detected vocalizations to the Lead PSO 
on duty, who will then be responsible for implementing the necessary 
mitigation procedures.
    PSOs will be equipped with binoculars and have the ability to 
estimate distances to marine mammals located in proximity to the vessel 
and/or exclusion zone using range finders. Reticulated binoculars will 
also be available to PSOs for use as appropriate based on conditions 
and visibility to support the siting and monitoring of marine species. 
During night operations, PAM (see Passive Acoustic Monitoring 
requirements below) and night-vision equipment in combination with 
infrared technology will be used. Position data will be recorded using 
hand-held or vessel global positioning system (GPS) units for each 
sighting.
    The PSOs will begin observation of all zone(s) at least 60 minutes 
prior to ramp-up of HRG survey equipment. Use of noise-producing 
equipment will not begin until the exclusion zone is clear of all 
marine mammals for at least 60 minutes, as per the requirements of the 
BOEM Lease.
    If a marine mammal is detected approaching or entering the 200-m or 
400-m exclusion zones, the vessel operator would adhere to the shutdown 
(during HRG survey) or powerdown (during DP thruster use) procedures 
described below to minimize noise impacts on the animals.
    At all times, the vessel operator will maintain a separation 
distance of 500 m from any sighted North Atlantic right whale as 
stipulated in the Vessel Strike Avoidance procedures described below. 
These stated requirements will be included in the site-specific 
training to be provided to the survey team.

Passive Acoustic Monitoring

    As per the BOEM Lease, alternative monitoring technologies (e.g., 
active or passive acoustic monitoring) are required if a Lessee intends 
to conduct geophysical surveys at night or when visual observation is 
otherwise impaired. To support 24-hour HRG survey operations, DWW will 
include PAM as part of the project monitoring during nighttime 
operations to provide for optimal acquisition of species detections at 
night.
    Given the range of species that could occur in the Project Area, 
the PAM system will consist of an array of hydrophones with both 
broadband (sampling mid-range frequencies of 2 kilohertz (kHz) to 200 
kHz) and at least one low-frequency hydrophone (sampling range 
frequencies of 75 Hertz (Hz) to 30 kHz). The PAM operator(s) will 
monitor the hydrophone signals for detection of marine mammals in real 
time both aurally (using headphones) and visually (via the monitor 
screen displays). PAM operators will communicate detections to the Lead 
PSO on duty who will ensure the implementation of the appropriate 
mitigation measure.

Vessel Strike Avoidance

    DWW will ensure that vessel operators and crew maintain a vigilant 
watch for cetaceans and pinnipeds and slow down or stop their vessels 
to avoid striking these species. Survey vessel crew members responsible 
for navigation duties will receive site-specific training on marine 
mammal sighting/reporting and vessel strike avoidance measures. Vessel 
strike avoidance measures will include the following, except under 
extraordinary circumstances when complying with these requirements 
would put the safety of the vessel or crew at risk:

[[Page 32339]]

     All vessel operators will comply with 10 knots (<18.5 km 
per hour [km/h]) speed restrictions in any Dynamic Management Area 
(DMA).
     All survey vessels will maintain a separation distance of 
500 m or greater from any sighted North Atlantic right whale.
     If underway, vessels must steer a course away from any 
sited North Atlantic right whale at 10 knots (<18.5 km/h) or less until 
the 500 m minimum separation distance has been established. If a North 
Atlantic right whale is sited in a vessel's path, or within 100 m to an 
underway vessel, the underway vessel must reduce speed and shift the 
engine to neutral. Engines will not be engaged until the North Atlantic 
right whale has moved outside of the vessel's path and beyond 100 m. If 
stationary, the vessel must not engage engines until the North Atlantic 
right whale has moved beyond 100 m.
     All vessels will maintain a separation distance of 100 m 
or greater from any sighted non-delphinoid (i.e., mysticetes and sperm 
whales) cetaceans. If sighted, the vessel underway must reduce speed 
and shift the engine to neutral and must not engage the engines until 
the non-delphinoid cetacean has moved outside of the vessel's path and 
beyond 100 m. If a survey vessel is stationary, the vessel will not 
engage engines until the non-delphinoid cetacean has moved out of the 
vessel's path and beyond 100 m.
     All vessels will maintain a separation distance of 50 m or 
greater from any sighted delphinoid cetacean. Any vessel underway will 
remain parallel to a sighted delphinoid cetacean's course whenever 
possible and avoid excessive speed or abrupt changes in direction. Any 
vessel underway reduces vessel speed to 10 knots or less when pods 
(including mother/calf pairs) or large assemblages of delphinoid 
cetaceans are observed. Vessels may not adjust course and speed until 
the delphinoid cetaceans have moved beyond 50 m and/or abeam (i.e., 
moving away and at a right angle to the centerline of the vessel) of 
the underway vessel.
     All vessels will maintain a separation distance of 50 m or 
greater from any sighted pinniped.
    The training program will be provided to NMFS for review and 
approval prior to the start of surveys. Confirmation of the training 
and understanding of the requirements will be documented on a training 
course log sheet. Signing the log sheet will certify that the crew 
members understand and will comply with the necessary requirements 
throughout the survey event.

Seasonal Operating Requirements

    Between watch shifts, members of the monitoring team will consult 
the NMFS North Atlantic right whale reporting systems for the presence 
of North Atlantic right whales throughout survey operations. The 
planned survey activities will, however, occur outside of the seasonal 
management area (SMA) located off the coasts of Delaware and New 
Jersey. The planned survey activities will also occur in June/July and 
September, which is outside of the seasonal mandatory speed restriction 
period for this SMA (November 1 through April 30).
    Throughout all survey operations, DWW will monitor the NMFS North 
Atlantic right whale reporting systems for the establishment of a DMA. 
If NMFS should establish a DMA in the Lease Area under survey, within 
24 hours of the establishment of the DMA, DWW will work with NMFS to 
shut down and/or alter the survey activities to avoid the DMA.

Ramp-Up

    As per the BOEM Lease, a ramp-up procedure will be used for HRG 
survey equipment capable of adjusting energy levels at the start or re-
start of HRG survey activities. A ramp-up procedure will be used at the 
beginning of HRG survey activities in order to provide additional 
protection to marine mammals near the Project Area by allowing them to 
vacate the area prior to the commencement of survey equipment use. The 
ramp-up procedure will not be initiated during daytime, nighttime, or 
periods of inclement weather if the exclusion zone cannot be adequately 
monitored by the PSOs using the appropriate visual technology (e.g., 
reticulated binoculars, night vision equipment) and/or PAM for a 60-
minute period. A ramp-up would begin with the power of the smallest 
acoustic HRG equipment at its lowest practical power output appropriate 
for the survey. The power would then be gradually turned up and other 
acoustic sources added such that the source level would increase in 
steps not exceeding 6 dB per 5-minute period. If marine mammals are 
detected within the HRG survey exclusion zone prior to or during the 
ramp-up, activities will be delayed until the animal(s) has moved 
outside the monitoring zone and no marine mammals are detected for a 
period of 60 minutes.
    The DP vessel thrusters will be engaged from the time the vessel 
leaves the dock to support the safe operation of the vessel and crew 
while conducting geotechnical survey activities and require use as 
necessary. Therefore, there is no opportunity to engage in a ramp-up 
procedure.

Shutdown and Powerdown

    HRG Survey--The exclusion zone(s) around the noise-producing 
activities (HRG and geotechnical survey equipment) will be monitored, 
as previously described, by PSOs and at night by PAM operators for the 
presence of marine mammals before, during, and after any noise-
producing activity. The vessel operator must comply immediately with 
any call for shutdown by the Lead PSO. Any disagreement should be 
discussed only after shutdown.
    As per the BOEM Lease, if a non-delphinoid (i.e., mysticetes and 
sperm whales) cetacean is detected at or within the established 
exclusion zone (200-m exclusion zone during HRG surveys; 400-m 
exclusion zone during the operation of the sparker), an immediate 
shutdown of the survey equipment is required. Subsequent restart of the 
survey equipment must use the ramp-up procedures described above and 
may only occur following clearance of the exclusion zone for 60 
minutes.
    As per the BOEM Lease, if a delphinoid cetacean or pinniped is 
detected at or within the exclusion zone, the HRG survey equipment 
(including the sub-bottom profiler) must be powered down to the lowest 
power output that is technically feasible. Subsequent power up of the 
survey equipment must use the ramp-up procedures described above and 
may occur after (1) the exclusion zone is clear of a delphinoid 
cetacean and/or pinniped for 60 minutes or (2) a determination by the 
PSO after a minimum of 10 minutes of observation that the delphinoid 
cetacean or pinniped is approaching the vessel or towed equipment at a 
speed and vector that indicates voluntary approach to bow-ride or chase 
towed equipment.
    If the HRG sound source (including the sub-bottom profiler) shuts 
down for reasons other than encroachment into the exclusion zone by a 
marine mammal including but not limited to a mechanical or electronic 
failure, resulting in in the cessation of sound source for a period 
greater than 20 minutes, a restart for the HRG survey equipment 
(including the sub-bottom profiler) is required using the full ramp-up 
procedures and clearance of the exclusion zone of all cetaceans and 
pinnipeds for 60 minutes. If the pause is less than 20 minutes, the 
equipment may be restarted as soon as practicable at its operational 
level as long as visual surveys were continued diligently

[[Page 32340]]

throughout the silent period and the exclusion zone remained clear of 
cetaceans and pinnipeds. If the visual surveys were not continued 
diligently during the pause of 20 minutes or less, a restart of the HRG 
survey equipment (including the sub-bottom profiler) is required using 
the full ramp-up procedures and clearance of the exclusion zone for all 
cetaceans and pinnipeds for 60 minutes.
    Geotechnical Survey (DP Thrusters)--During geotechnical survey 
activities, a constant position over the drill, coring, or CPT site 
must be maintained to ensure the integrity of the survey equipment. 
During DP vessel operations if marine mammals enter or approach the 
established exclusion zone, DWW plans to reduce DP thruster to the 
maximum extent possible, except under circumstances when ceasing DP 
thruster use would compromise safety (both human health and 
environmental) and/or the integrity of the Project. Reducing thruster 
energy will effectively reduce the potential for exposure of marine 
mammals to sound energy. Normal use may resume when PSOs report that 
the monitoring zone has remained clear of marine mammals for a minimum 
of 60 minutes since last the sighting.
    Based on our evaluation of the applicant's planned measures, as 
well as other measures considered by NMFS, NMFS has determined that the 
planned mitigation measures provide the means of effecting the least 
practicable impact on the affected 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 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 
incidental take authorizations (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 action area. Effective reporting is critical both to 
compliance as well as ensuring that the most value is obtained from the 
required monitoring.
    Monitoring measures prescribed by NMFS should contribute to 
improved understanding of one or more of the following general goals:
     Occurrence of marine mammal species or stocks in the 
action area (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).
     Mitigation and monitoring effectiveness.
    DWW submitted marine mammal monitoring and reporting measures as 
part of the IHA application.
    Visual Monitoring--Visual monitoring all visible waters during all 
HRG and geotechnical surveys will be performed by qualified and NMFS-
approved PSOs (see discussion of PSO qualifications and requirements in 
Marine Mammal Exclusion Zones above).
    The PSOs will begin observation of the monitoring zone during all 
HRG survey activities and all geotechnical operations where DP 
thrusters are employed. Observations of the monitoring zone will 
continue throughout the survey activity and/or while DP thrusters are 
in use. PSOs will be responsible for visually monitoring and 
identifying marine mammals approaching or entering the established 
monitoring zone during survey activities.
    Observations will take place from the highest available vantage 
point on the survey vessel. General 360-degree scanning will occur 
during the monitoring periods, and target scanning by the PSO will 
occur when alerted of a marine mammal presence.
    Data on all PSO observations will be recorded based on standard PSO 
collection requirements. This will include dates and locations of 
construction operations; time of observation, location and weather; 
details of the sightings (e.g., species, age classification (if known), 
numbers, behavior); an estimate of the observable distance recorded at 
each shift change, and details of any observed ``taking'' (behavioral 
disturbances or injury/mortality). If the entire zone was not 
observable, DWW will provide an adjusted total take number based on the 
number of animals observed, and the area that was not observed. The 
data sheet will be provided to both NMFS and BOEM for review and 
approval prior to the start of survey activities. In addition, prior to 
initiation of survey work, all crew members will undergo environmental 
training, a component of which will focus on the procedures for 
sighting and protection of marine mammals. A briefing will also be 
conducted between the survey supervisors and crews, the PSOs, and DWW. 
The purpose of the briefing will be to establish responsibilities of 
each party, define the chains of command, discuss communication 
procedures, provide an overview of monitoring purposes, and review 
operational procedures.
    Acoustic Field Verification--As per the requirements of the BOEM 
Lease, field verification of the exclusion/monitoring zones will be 
conducted to determine whether the zones correspond accurately to the 
relevant isopleths and are adequate to minimize impacts to marine 
mammals. The details of the field verification strategy will be 
provided in a Field Verification Plan no later than 45 days prior to 
the commencement of field verification activities.
    DWW must conduct field verification of the exclusion zone (the 160 
dB isopleth) for HRG survey equipment and the exclusion zone (the 120 
dB isopleth) for DP thruster use for all equipment operating below 200 
kHz. DWW must take acoustic measurements at a minimum of two reference 
locations and in a manner that is sufficient to establish source level 
(peak at 1 meter) and distance to the 160 dB isopleths (the B 
harassment zones for HRG surveys) and 120 dB isopleth (the Level B 
harassment zone) for DP thruster use. Sound measurements must be taken 
at the reference locations at two depths (i.e., a depth at mid-water 
and a depth at approximately 1 meter (3.28 ft) above the seafloor).
    DWW may use the results from its field-verification efforts to 
request modification of the exclusion/monitoring zones for the HRG or 
geotechnical surveys. Any new exclusion/monitoring zone radius

[[Page 32341]]

proposed by DWW must be based on the most conservative measurements 
(i.e., the largest safety zone configuration) of the target Level A or 
Level B harassment acoustic threshold zones. The modified zone must be 
used for all subsequent use of field-verified equipment. DWW must 
obtain approval from NMFS and BOEM of any new exclusion/monitoring zone 
before it may be implemented, and the IHA shall be modified 
accordingly.

Reporting Measures

    DWW will provide the following reports as necessary during survey 
activities:
     The Applicant will contact NMFS and BOEM within 24 hours 
of the commencement of survey activities and again within 24 hours of 
the completion of the activity.
     As per the BOEM Lease: Any observed significant behavioral 
reactions (e.g., animals departing the area) or injury or mortality to 
any marine mammals must be reported to NMFS and BOEM within 24 hours of 
observation. Dead or injured protected species are reported to the NMFS 
Greater Atlantic Regional Fisheries Office (GARFO) Stranding Hotline 
(800-900-3622) within 24 hours of sighting, regardless of whether the 
injury is caused by a vessel. In addition, if the injury of death was 
caused by a collision with a project related vessel, DWW must ensure 
that NMFS and BOEM are notified of the strike within 24 hours. DWW must 
use the form included as Appendix A to Addendum C of the Lease to 
report the sighting or incident. Additional reporting requirements for 
injured or dead animals are described below (Notification of Injured or 
Dead Marine Mammals).
     Notification of Injured or Dead Marine Mammals--In the 
unanticipated event that the specified HRG and geotechnical activities 
lead to an injury of a marine mammal (Level A harassment) or mortality 
(e.g., ship-strike, gear interaction, and/or entanglement), DWW would 
immediately cease the specified activities and report the incident to 
the Chief of the Permits and Conservation Division, Office of Protected 
Resources and the NOAA GARFO Stranding Coordinator. The report would 
include the following information:
     Time, date, and location (latitude/longitude) of the 
incident;
     Name and type of vessel involved;
     Vessel's speed during and leading up to the incident;
     Description of the incident;
     Status of all sound source use in the 24 hours preceding 
the incident;
     Water depth;
     Environmental conditions (e.g., wind speed and direction, 
Beaufort sea state, cloud cover, and visibility);
     Description of all marine mammal observations in the 24 
hours preceding the incident;
     Species identification or description of the animal(s) 
involved;
     Fate of the animal(s); and
     Photographs or video footage of the animal(s) (if 
equipment is available).
    Activities would not resume until NMFS is able to review the 
circumstances of the event. NMFS would work with DWW to minimize 
reoccurrence of such an event in the future. DWW would not resume 
activities until notified by NMFS.
    In the event that DWW discovers an injured or dead marine mammal 
and determines that the cause of the injury or death is unknown and the 
death is relatively recent (i.e., in less than a moderate state of 
decomposition), DWW would immediately report the incident to the Chief 
of the Permits and Conservation Division, Office of Protected Resources 
and the GARFO Stranding Coordinator. The report would include the same 
information identified in the paragraph above. Activities would be able 
to continue while NMFS reviews the circumstances of the incident. NMFS 
would work with DWW to determine if modifications in the activities are 
appropriate.
    In the event that DWW discovers an injured or dead marine mammal 
and determines that the injury or death is not associated with or 
related to the activities authorized in the IHA (e.g., previously 
wounded animal, carcass with moderate to advanced decomposition, or 
scavenger damage), DWW would report the incident to the Chief of the 
Permits and Conservation Division, Office of Protected Resources, and 
the GARFO Regional Stranding Coordinator, within 24 hours of the 
discovery. DWW would provide photographs or video footage (if 
available) or other documentation of the stranded animal sighting to 
NMFS. DWW can continue its operations under such a case.
     Within 90 days after completion of the marine site 
characterization survey activities, a technical report will be provided 
to NMFS and BOEM that fully documents the methods and monitoring 
protocols, summarizes the data recorded during monitoring, estimates 
the number of marine mammals that may have been taken during survey 
activities, and provides an interpretation of the results and 
effectiveness of all monitoring tasks. Any recommendations made by NMFS 
must be addressed in the final report prior to acceptance by NMFS.
     In addition to the Applicant's reporting requirements 
outlined above, DWW will provide an assessment report of the 
effectiveness of the various mitigation techniques, i.e. visual 
observations during day and night, compared to the PAM detections/
operations. This will be submitted as a draft to NMFS and BOEM 30 days 
after the completion of the HRG and geotechnical surveys and as a final 
version 60 days after completion of the surveys.

Negligible Impact Analysis and Determinations

    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. 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 the 
authorized 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, etc.), as 
well as effects on habitat, the status of the affected stocks, 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 the NMFS implementing regulations (54 FR 40338; September 
29, 1989), the impacts from other past and ongoing anthropogenic 
activities are incorporated into these analyses 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).
    As discussed in the Potential Effects section, PTS, masking, non-
auditory physical effects, and vessel strike are not expected to occur. 
Further, once an area has been surveyed, it is not likely that it will 
be surveyed again, thereby reducing the likelihood of repeated impacts 
within the project area.
    Potential impacts to marine mammal habitat were discussed 
previously in

[[Page 32342]]

this document (see the Potential Effects of the Specified Activity on 
Marine Mammals and their Habitat section). Marine mammal habitat may be 
impacted by elevated sound levels and some sediment disturbance, but 
these impacts would be temporary. Also, feeding behavior is less likely 
to be impacted than other behavioral patterns, as marine mammals appear 
to be less likely to exhibit behavioral reactions or avoidance 
responses while engaged in feeding activities (Richardson et al., 
1995). Additionally, prey species are mobile and are broadly 
distributed throughout the Project Area; therefore, marine mammals that 
may be temporarily displaced during survey activities are expected to 
be able to resume foraging once they have moved away from areas with 
disturbing levels of underwater noise. Because of the temporary nature 
of the disturbance, and the availability of similar habitat and 
resources in the surrounding area, the impacts to marine mammals and 
the food sources that they utilize are not expected to cause 
significant or long-term consequences for individual marine mammals or 
their populations. Furthermore, there are no rookeries or mating 
grounds known to be biologically important to marine mammals within the 
project area. A biologically important feeding area for fin whales East 
of Montauk Point (from March to October) and a biologically important 
migratory route effective March-April and November-December for North 
Atlantic right whale, occur near the Project Area (LaBrecque, et al., 
2015). However, there is only a small temporal overlap between the 
migratory biologically important area (BIA) and the planned survey 
activities in November and December.
    ESA-listed species for which takes are authorized are North 
Atlantic right, sperm, sei and fin whales. Recent estimates of 
abundance indicate a potential declining right whale population; 
however, this may also be due to low sighting rates in areas where 
right whales were present in previous years, due to a shift in habitat 
use patterns (Waring et al., 2016). While we are concerned about 
declining right whale populations, and we are authorizing take of 105 
individuals, as described elsewhere in this section the anticipated 
impacts are expected to be in the form of shorter-term lower level 
disturbance in areas that are not of particular known importance for 
right whales, and not expected to have any impacts on health or 
fitness. There are currently insufficient data to determine population 
trends for fin whale, sei whale, and sperm whale (Waring et al., 2015). 
There is no designated critical habitat for any ESA-listed marine 
mammals within the Project Area, and most of the stocks for non-listed 
species authorized to be taken are not considered depleted or strategic 
by NMFS under the MMPA. Of the two non-listed species that are 
considered strategic for which take is requested (false killer whale 
and long-finned pilot whale), take is less than one percent of the 
entire populations. Therefore, the planned site characterization 
surveys will not have population-level effects, and we do not expect 
them to impact annual rates of recruitment or survival.
    The mitigation measures are expected to reduce the number and/or 
severity of takes by (1) giving animals the opportunity to move away 
from the sound source before HRG survey equipment reaches full energy; 
(2) reducing the intensity of exposure within a certain distance by 
reducing the DP thruster power; and (3) preventing animals from being 
exposed to sound levels that may cause injury. Additional vessel strike 
avoidance requirements will further mitigate potential impacts to 
marine mammals during vessel transit to and within the Study Area.
    DWW did not request, and NMFS is not authorizing, take of marine 
mammals by serious injury or mortality. NMFS expects that most takes 
would be in the form of a very small number of short-term Level B 
behavioral harassment in the form of brief startling reaction and/or 
temporary avoidance of the area or decreased foraging (if such activity 
were occurring)--reactions that are considered to be of low severity 
and with no lasting biological consequences (e.g., Southall et al., 
2007). This is largely due to the short time scale of the planned 
activities, the low source levels and intermittent nature of many of 
the technologies planned to be used, as well as the required 
mitigation.
    NMFS concludes that exposures to marine mammal species and stocks 
due to DWW's HRG and geotechnical survey activities would result in 
only short-term and relatively infrequent effects to individuals 
exposed and not of the type or severity that would be expected to be 
additive for the small portion of the stocks and species likely to be 
exposed. NMFS does not anticipate the authorized takes to impact annual 
rates of recruitment or survival, because although animals may 
temporarily avoid the immediate area, they are not expected to 
permanently abandon the area. Additionally, major shifts in habitat 
use, distribution, or foraging success, are not expected.
    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 monitoring and mitigation 
measures, NMFS finds that the total marine mammal take from the planned 
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 Section 101(a)(5)(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 the relevant species or stock size in our 
determination of whether an authorization is limited to small numbers 
of marine mammals. Additionally, other qualitative factors may be 
considered in the analysis, such as the temporal or spatial scale of 
the activities.
    The takes authorized for the HRG and geotechnical surveys represent 
less than 1 percent for 11 stocks (sei whale, minke whale, sperm whale, 
false killer whale, Cuvier's beaked whale, long-finned pilot whale, 
white-beaked dolphin, Atlantic spotted dolphin, striped dolphin, 
bottlenose dolphin, and gray seal); 1.05 percent for Atlantic white-
sided dolphin; 1.48 percent for harbor porpoise; 2.04 percent for 
short-beaked common dolphin; 4.51 percent for fin whale; 6.43 percent 
for humpback whale; and 14.68 percent for harbor seal (Table 6). Just 
under 24 percent of the North Atlantic right whale stock has take 
authorized; however, this is for the entire duration of the project 
activities (mid-June through December), and while this stock of right 
whales may be present in very low numbers in the winter months 
(November and December) in this area, most animals have moved off the 
feeding grounds and have moved to the breeding grounds during this 
time. We do not expect a large number of right whales to be in the area 
for nearly one third of the project duration. Only repeated takes of 
some individuals are likely and this is an overestimate of the number 
of individual right whales that may actually be impacted by project 
activities. However, we analyzed the potential for take of 23.86 
percent of the individual right whales in the context of the 
anticipated effects described previously.

[[Page 32343]]

    These take estimates represent the percentage of each species or 
stock that could be taken by Level B harassment and are small numbers 
relative to the affected species or stock sizes. Further, the take 
numbers represent the instances of take and are the maximum numbers of 
individual animals that are expected to be harassed during the project; 
it is possible that some exposures may occur to the same individual.
    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.

                    Table 6--Summary of Marine Mammal Takes and Percentage of Stocks Affected
----------------------------------------------------------------------------------------------------------------
                                                    Authorized      Authorized         Stock
                     Species                       Level B take    Level A take      abundance     Percentage of
                                                       (No.)           (No.)         estimate     stock affected
----------------------------------------------------------------------------------------------------------------
North Atlantic right whale......................             105               0             440           23.86
(Eubalaena glacialis)...........................
Fin Whale.......................................              73               0           1,618            4.51
(Balaenoptera physalus).........................
Sei whale.......................................               3               0             357            0.84
(Balaenoptera borealis).........................
Humpback whale..................................              53               0             823            6.43
(Megaptera novaeangliae)........................
Minke whale.....................................              16               0           2,591            0.62
(Balaenoptera acutorostrata)....................
Sperm whale.....................................               3               0           2,288            0.13
(Physeter macrocephalus)........................
False killer whale..............................               3               0             442            0.68
(Pseudorca crassidens)..........................
Cuvier's beaked whale...........................               6               0           6,532            0.09
(Ziphius cavirostris)...........................
Long-finned pilot whale.........................              53               0           5,636            0.94
(Globicephala melas)............................
Atlantic white-sided dolphin....................             513               0          48,819            1.05
(Lagenorhynchus acutus).........................
White-beaked dolphin............................               3               0           2,003            0.15
(Lagenorhynhcus albirostris)....................
Short beaked common Dolphin.....................           1,433               0          70,184            2.04
(Delphinus delphis).............................
Atlantic spotted dolphin........................               2               0          44,715          0.0045
(Stenella frontalis)............................
Striped dolphin.................................               1               0          54,807          0.0018
(Stenella coruleoalba)..........................
Bottlenose Dolphin..............................             411               0          77,532            0.53
(Tursiops truncatus)............................
Harbor Porpoise.................................            1188               0          79,883            1.48
(Phocoena phocoena).............................
Harbor Seal\1\..................................          11,137               0          75,834           14.68
(Phoca vitulina)................................
Gray seal.......................................            1293               0         505,000            0.25
(Halichoerus grypus)............................
----------------------------------------------------------------------------------------------------------------

Unmitigable Adverse Impact Analysis and Determination

    There are no relevant subsistence uses of the affected marine 
mammal stocks 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

    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, in this case with the Greater Atlantic 
Regional Fisheries Office (GARFO) Protected Resources Division, 
whenever we propose to authorize take for endangered or threatened 
species.
    NMFS is proposing to authorize take of three listed species, which 
are listed under the ESA: fin, humpback, and North Atlantic right 
whale. Under section 7 of the ESA, BOEM consulted with NMFS on 
commercial wind lease issuance and site assessment activities on the 
Atlantic Outer Continental Shelf in Massachusetts, Rhode Island, New 
York and New Jersey Wind Energy Areas. NOAA's GARFO issued a Biological 
Opinion concluding that these activities may adversely affect but are 
not likely to jeopardize the continued existence of fin whale, humpback 
whale, or North Atlantic right whale. The Biological Opinion can be 
found online at http://www.nmfs.noaa.gov/pr/permits/incidental/energy_other.htm. NMFS is also consulting internally on the issuance of 
an IHA under section 101(a)(5)(D) of the MMPA for this activity. 
Following issuance of the DWW's IHA, the Biological Opinion may be 
amended to include an incidental take exemption for these marine mammal 
species, as appropriate.

[[Page 32344]]

National Environmental Policy Act (NEPA)

    NMFS prepared an Environmental Assessment (EA) in accordance with 
the National Environmental Policy Act (NEPA). A Finding of No 
Significant Impact (FONSI) was signed in June 2017. A copy of the EA 
and FONSI are posted at http://www.nmfs.noaa.gov/pr/permits/incidental/energy_other.htm.

Authorization

    NMFS has issued an IHA to Deepwater Wind for the potential 
harassment of small numbers of 18 marine mammal species incidental to 
high-resolution geophysical (HRG) and geotechnical survey 
investigations associated with marine site characterization activities 
off the coast of New York in the Project Area, provided the previously 
mentioned mitigation, monitoring and reporting.

    Dated: July 10, 2017.
Donna S. Wieting,
Director, Office of Protected Resources, National Marine Fisheries 
Service.
[FR Doc. 2017-14699 Filed 7-12-17; 8:45 am]
 BILLING CODE 3510-22-P