Takes of Marine Mammals Incidental to Specified Activities; Taking Marine Mammals Incidental to Offshore Wind Construction Activities Off of Virginia, 30930-30948 [2020-10982]

Agencies

• DEPARTMENT OF COMMERCE
• National Oceanic and Atmospheric Administration

[Federal Register Volume 85, Number 99 (Thursday, May 21, 2020)]
[Notices]
[Pages 30930-30948]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2020-10982]


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DEPARTMENT OF COMMERCE

National Oceanic and Atmospheric Administration

[RTID 0648-XR075]


Takes of Marine Mammals Incidental to Specified Activities; 
Taking Marine Mammals Incidental to Offshore Wind Construction 
Activities Off of Virginia

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 
Virginia Electric and Power Company, d/b/a Dominion Energy Virginia 
(Dominion), to incidentally harass, by Level B harassment only, marine 
mammals during construction activities off the coast of Virginia in the 
area of Research Lease of Submerged Lands for Renewable Energy 
Activities on the Outer Continental Shelf (OCS) Offshore Virginia 
(Lease No. OCS-A-0497), in support of the Coastal Virginia Offshore 
Wind (CVOW) Project.

DATES: This authorization is valid for one year from the date of 
issuance.

FOR FURTHER INFORMATION CONTACT: Jordan Carduner, 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.fisheries.noaa.gov/national/marine-mammal-protection/incidental-take-authorizations-other-energy-activities-renewable. In case of 
problems accessing these documents, please call the contact listed 
above.

SUPPLEMENTARY INFORMATION: 

Background

    The MMPA prohibits the ``take'' of marine mammals, with certain 
exceptions. Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 
et seq.) direct the Secretary of Commerce (as delegated to NMFS) to 
allow, upon request, the incidental, but not intentional, taking of 
small numbers of marine mammals by United States citizens who engage in 
a specified activity (other than commercial fishing) within a specified 
geographical region if certain findings are made and either regulations 
are issued or, if the taking is limited to harassment, a notice of a 
proposed incidental take authorization may be provided to the public 
for review.
    Authorization for incidental takings shall be granted if NMFS finds 
that the taking will have a negligible impact on the species or 
stock(s) and will not have an unmitigable adverse impact on the 
availability of the species or stock(s) for taking for subsistence uses 
(where relevant). Further, NMFS must prescribe the permissible methods 
of taking and other ``means of effecting the least practicable adverse 
impact'' on the affected species or stocks and their habitat, paying 
particular attention to rookeries, mating grounds, and areas of similar 
significance, and on the availability of such species or stocks for 
taking for certain subsistence uses (referred to in shorthand as 
``mitigation''); and requirements pertaining to the mitigation, 
monitoring and reporting of such takings are set forth.
    The definitions of all applicable MMPA statutory terms cited above 
are included in the relevant sections below.

Summary of Request

    On September 13, 2019, NMFS received a request from Dominion for an 
IHA to take marine mammals incidental to construction activities off 
the coast of Virginia in the area of Research Lease of Submerged Lands 
for Renewable Energy Activities on the Outer Continental Shelf (OCS) 
Offshore Virginia (Lease No. OCS-A-0497) in support of the CVOW 
project. A revised application was received on January 21, 2020. NMFS 
deemed that request to be adequate and complete. Dominion's request is 
for the take of seven marine mammal species by Level B harassment that 
would occur over the course of two days of in-water construction. 
Neither Dominion nor NMFS expects serious injury or mortality to result 
from this activity and the activity is expected to last no more than 
one year, therefore, an IHA is appropriate.

Description of Activity

Overview

    The CVOW Project (the Project) calls for development of two 6-
megawatt wind turbines on a site leased by the Virginia Department of 
Mines Minerals and Energy (DMME). Dominion has an agreement with DMME 
to build and operate the two turbines within the 2,135-acre site, which 
lies 27 miles (mi) off the coast of Virginia Beach, Virginia. Dominion 
has contracted with [Oslash]rsted for construction of the two turbines. 
The goals of the Project are to provide electricity to Virginia and to 
inform plans for a future large-scale commercial offshore wind 
development in the adjacent Virginia Wind Energy Area that is also 
leased by Dominion.
    Dominion proposes to conduct in-water construction activities in 
the area of Research Lease of Submerged Lands for Renewable Energy 
Activities on the OCS Offshore Virginia (Lease No. OCS-A-0497) (the 
Lease Area; see Figure 1-1 in the IHA application), as well as cable-
lay and marine site characterization surveys along a 27-mile (mi) 
submarine cable corridor to a landfall location in Virginia, in support 
of the Project. The objective of the construction activities is to 
support installation of the wind turbine generator (WTG) foundations.
    Construction activities are expected to occur during two days and 
could occur any time between May and October, 2020. Cable-lay and site 
characterization survey activities could occur for up to three months 
between May and October, 2020. Dominion's activities would occur in the 
Northwest Atlantic Ocean within Federal and state waters. Construction 
activities would occur within the Lease Area approximately 27 miles 
offshore Virginia (see Figure 1-1 in the IHA application) while cable-
lay and site characterization survey activities would occur between the 
Lease Area and a landfall location in Virginia. As described in the 
notice of proposed IHA (85 FR 14901; March 16, 2020) NMFS has 
determined the likelihood of cable lay activities and HRG surveys 
associated with the construction of the project resulting in harassment 
of marine mammals to be so low as to be discountable; therefore, cable 
lay activities and HRG surveys associated with the construction of the 
project are not analyzed further in this document.
    In-water construction activities would entail pile driving to 
support installation of two WTG foundations. The monopiles would have a 
7.8 meter (m) (26 feet (ft)) diameter at the seafloor and 6 m (20 ft) 
diameter flange. The two monopiles would be 63 and 64 m (207 and 210 
ft) in length. One monopile would be driven at a time and a maximum of 
one pile would be driven per day. As described in the notice of 
proposed IHA (85 FR 14901; March 16, 2020) NMFS has determined that 
pile driving associated with construction of

[[Page 30931]]

the WTG foundations has the potential to result in the take of marine 
mammals by Level B harassment.
    A detailed description of Dominion's planned activities is provided 
in the notice of proposed IHA (85 FR 14901; March 16, 2020). Since that 
time, no changes have been made to the activities. Therefore, a 
detailed description is not provided here. Please refer to that notice 
for the detailed description of the specified activity. Mitigation, 
monitoring, and reporting measures are described in detail later in 
this document (please see Mitigation and Monitoring and Reporting 
below).

Comments and Responses

    A notice of proposed IHA was published in the Federal Register on 
March 16, 2020 (85 FR 14901). During the 30-day public comment period, 
NMFS received a comment letter from the Marine Mammal Commission 
(Commission) and a group of non-governmental organizations (NGOs) 
including Southern Environmental Law Center, Natural Resources Defense 
Council, National Wildlife Federation, Conservation Law Foundation, 
Defenders of Wildlife, Whale and Dolphin Conservation, Surfrider 
Foundation, Sierra Club Virginia Chapter, Assateague Coastal Trust, 
NY4WHALES, Inland Ocean Coalition, and Ocean Conservation Research. 
NMFS has posted the comments online at www.fisheries.noaa.gov/national/marine-mammal-protection/incidental-take-authorizations-other-energy-activities-renewable. Please see those letters for full detail 
regarding the commenters' recommendations and underlying rationale.
    Comment 1. The NGOs asserted that the proposed mitigation measures 
for noise attenuation are insufficient and do not comply with the 
MMPA's requirement to achieve the ``least practicable adverse impact'' 
to affected marine mammal populations, and that NMFS should require 
further mitigation of pile driving noise including noise attenuation at 
the pile itself, such as through pile casings or dampers.
    Response: NMFS disagrees with the assertion that the proposed 
mitigation measures do not comply with the MMPA's requirement to 
achieve the least practicable adverse impact to affected marine mammal 
populations. The commenter's position is based on an assumption that 
the only way to achieve the least practicable adverse impact on 
affected marine mammal populations through this IHA is to require noise 
attenuation on both piles planned for installation by Dominion. NMFS 
does not agree with this assumption. We note that the proposal to drive 
one pile with an active noise attenuation system (i.e. a double bubble 
curtain) and to drive the second pile with no attenuation was proposed 
by Dominion with the goal of improving the overall understanding of the 
effectiveness of double bubble curtains in attenuation of pile driving 
noise. Data on the effectiveness of the attenuation method will be 
gathered via acoustic monitoring during the driving of both piles (one 
with the active double bubble curtain and the other with no 
attenuation) and this data will then be made available to both NMFS and 
the Bureau of Ocean Energy Management (BOEM) as well as the public. 
Thus, the driving of one pile without attenuation, and the acoustic 
measurements of the driving of both piles, are fundamental components 
of the applicant's proposed action. To prevent Dominion from 
undertaking this study would therefore be impracticable for Dominion, 
as it would preclude them from accomplishing one of the purposes of the 
project, and would therefore not result in the least practicable 
impact.
    We note that differences in modeled marine mammal exposure numbers 
between one pile driven with 6 dB attenuation (assumed to be the 
effective attenuation level achieved from the double bubble curtain) 
compared with modeled exposure numbers for one pile driven with no 
attenuation are minimal (Table 6); therefore, the potential 
conservation benefit from precluding Dominion from undertaking this 
study would be minimal. Thus, a requirement to apply noise attenuation 
to both piles would result in a very minor potential benefit to marine 
mammals, but would prevent the applicant from collecting very valuable 
information regarding the effectiveness of bubble curtains, and is 
therefore impracticable.
    The data gathered through this study also has the potential to 
minimize overall impacts on marine mammal populations through improved 
mitigation and monitoring measures. There is still much to be learned 
regarding the effectiveness of bubble curtains, especially in offshore 
environments off the Atlantic coast in the U.S. where virtually none of 
this type of pile driving has occurred thus far. The acoustic 
monitoring of both piles, as required in this IHA, will provide NMFS 
with data that will inform mitigation measures in numerous future 
authorizations for activities that are expected to be much more 
impactful to marine mammals than the activity considered here 
(including a planned commercial-scale project by Dominion in the same 
geographic area as this IHA that would entail up to 200 planned wind 
turbine generators). We expect the data gathered from this project will 
lead to more effective mitigation. More effective mitigation will 
likely result in lesser overall impacts from expected offshore wind 
construction. Thus, the data to be collected by Dominion is indeed very 
valuable, and that information cannot be collected if both piles are 
treated with bubble curtains as the commenters proposed.
    Regarding the commenters recommendation that NMFS require the use 
of additional noise attenuation devices such as pile casings or 
dampers, while NMFS is supportive of the use of these attenuation 
devices, a requirement for additional attenuation devices is not 
necessary in this particular case as the applicant has demonstrated 
that the targeted level of attenuation can be achieved through 
deployment of the proposed double bubble curtain (see the IHA 
application under Section 2.3 ``Pile Driving''). The application of a 
double bubble curtain on one pile, in concert with the other mitigation 
measures required during pile driving including PSOs, pre-clearance, 
and delay and shutdown upon observation of marine mammals, will ensure 
the least practicable adverse impact on marine mammal species or stocks 
and their habitat.
    Comment 2. The NGOs commented that NMFS should reassess its 
acoustic thresholds and criticized NMFS's use of the 160-dB rms Level B 
harassment threshold, stating that the threshold is based on outdated 
information and that current research shows that behavioral impacts can 
occur at levels below the threshold.
    Response: NMFS acknowledges that the 160-dB rms step-function 
approach is simplistic, and that an approach reflecting a more complex 
probabilistic function may more effectively represent the known 
variation in responses at different levels due to differences in the 
receivers, the context of the exposure, and other factors. The 
commenters suggested that our use of the 160-dB threshold implies that 
we do not recognize the science indicating that animals may react in 
ways constituting behavioral harassment when exposed to lower received 
levels. However, we do recognize the potential for Level B harassment 
at exposures to received levels below 160 dB rms, in addition to the 
potential that animals exposed to received levels above 160 dB rms will 
not respond in ways constituting behavioral harassment. These comments 
appear to evidence a misconception regarding the concept of the 160-dB

[[Page 30932]]

threshold. While it is correct that in practice it works as a step-
function, i.e., animals exposed to received levels above the threshold 
are considered to be ``taken'' and those exposed to levels below the 
threshold are not, it is in fact intended as a sort of mid-point of 
likely behavioral responses (which are extremely complex depending on 
many factors including species, noise source, individual experience, 
and behavioral context). What this means is that, conceptually, the 
function recognizes that some animals exposed to levels below the 
threshold will in fact react in ways that are appropriately considered 
take, while others that are exposed to levels above the threshold will 
not. Use of the 160-dB threshold allows for a simplistic quantitative 
estimate of take, while we can qualitatively address the variation in 
responses across different received levels in our discussion and 
analysis.
    As behavioral responses to sound depend on the context in which an 
animal receives the sound, including the animal's behavioral mode when 
it hears sounds, prior experience, additional biological factors, and 
other contextual factors, defining sound levels that disrupt behavioral 
patterns is extremely difficult. Even experts have not previously been 
able to suggest specific new criteria due to these difficulties (e.g., 
Southall et al. 2007; Gomez et al., 2016).
    Comment 3. The NGOs commented that NMFS should consider data from 
state monitoring efforts, passive acoustic monitoring data, 
opportunistic marine mammal sightings, and other data sources in 
modeling marine mammal exposure estimates.
    Response: NMFS has used the best available scientific information--
in this case the marine mammal density models developed by the Duke 
University Marine Geospatial Ecology Lab (MGEL) (Roberts et al., 2016, 
2017, 2018)--to inform our determinations. The commenters cite four 
alternate sources and recommend that NMFS incorporate information from 
these sources in modeling marine mammal exposure estimates, stating 
``the density maps produced by the Roberts et al. model do not fully 
reflect the abundance, distribution, and density of marine mammals for 
the U.S. East Coast.'' The first source cited by the commenters is a 
report by the Virginia Aquarium & Marine Science Center that summarizes 
aerial survey data in the Virginia Wind Energy Area from 2012-2015 
(Mallette et al, 2016). However, a review of the most recent report on 
updates to the Duke MGEL density models (Roberts et al, 2018) shows 
that the aerial sightings data from the Virginia Aquarium & Marine 
Science Center report have in fact been incorporated into the Duke MGEL 
density models used to model exposures in this IHA. The second and 
third sources cited by the commenters summarize North Atlantic right 
whale passive acoustic monitoring (PAM) data in Virginia and elsewhere 
along the Atlantic coast. While NMFS agrees that these papers provide 
valuable information on right whale presence and habitat use in and 
near the project area, they do not provide density data that can 
readily be incorporated into exposure models and the commenters do not 
provide any recommendations as to how this PAM data would be 
incorporated into exposure estimates. The fourth source cited by the 
commenters is an article in the popular press about fishermen 
disentangling a North Atlantic right whale 50 miles offshore Virginia 
in 2013; the commenters do not provide a recommendation as to how an 
anecdotal report of a single right whale off Virginia in 2013 would be 
incorporated into marine mammal exposure estimates.
    The commenters also incorrectly state that, for large whales, NMFS 
``entirely dismiss[ed] the possibility of take based on a purported 
lack of presence'' for large whales. In fact, as described in the 
notice of proposed IHA, the potential for take of large whales to occur 
as a result of the project was ruled out because of very low densities 
in the project area. The potential for large whale take was analyzed in 
the same manner as all marine mammal species that may occur in the 
project area; that is, the proposed authorized take numbers were based 
on marine mammal exposure modeling, which incorporated the best 
available density data, followed by additional qualitative evaluation. 
This density data includes all marine mammal species that may be 
present in the project area, including blue, fin, sei, humpback, minke, 
sperm and North Atlantic right whales (Roberts et al., 2016, 2017, 
2018). The exposure modeling that incorporated the density data for 
these species resulted in estimates of zero takes for all large whale 
species. This was the first step in the analysis, which indicated that 
take of these species is unlikely. The addition of required mitigation 
and monitoring measures further reduces the likelihood of take. We 
therefore determined, based on the best available information, that 
take of these species was not expected to occur.
    Comment 4. The NGOs commented that NMFS should acknowledge the 
potential for take that may occur incidental to HRG surveys, cable 
laying, and vessel collisions. The NGOs also recommended that NMFS 
authorize take by Level A harassment of harbor porpoises because the 
agency has authorized Level A harassment for this species in some 
previous authorizations for HRG surveys.
    Response: NMFS acknowledged the general potential for HRG surveys, 
cable laying, and vessel collisions to result in the take of marine 
mammals in the notice of proposed IHA (85 FR 14901; March 16, 2020) but 
explained why the take of marine mammals is not anticipated as a result 
of these activities. Rather than repeating those explanations here, we 
refer the reader to the notice of proposed IHA under Detailed 
Description of the Specified Activities. Regarding the commenters' 
recommendation that take by Level A harassment be authorized for harbor 
porpoises, the reasoning behind our authorization of Level A harassment 
take for harbor porpoises in certain previous IHAs for HRG survey 
activities was based on the fact that modeling results for those 
previous authorizations resulted in Level A harassment numbers that 
exceeded 0. In this instance, exposure modeling resulted in an estimate 
of 0 Level A harassment takes for harbor porpoises (and all marine 
mammal species) thus we do not expect Level A harassment to occur and 
we do not authorize the take by Level A harassment of harbor porpoises 
as recommended by the commenters.
    We further note that the commenters have incorrectly stated that 
NMFS based its zero take conclusion for HRG surveys ``in part on 
mitigation measures that are under-protective--and in some cases 
nonexistent.'' However, the notice of proposed IHA (85 FR 14901; March 
16, 2020) clearly stated that NMFS determined the HRG surveys proposed 
by Dominion are not likely to result in take not because of proposed 
mitigation measures but because of the frequencies and modeled acoustic 
propagation of the HRG equipment planned for use by Dominion. Rather 
than repeating the reasoning behind this determination here, we refer 
the reader to the notice of proposed IHA under Detailed Description of 
the Specified Activities.
    Comment 5. The NGOs asserted that the required mitigation and 
monitoring protocols are insufficient in protecting marine mammals and 
do not comply with the MMPA and recommended that NMFS require 
additional mitigation measures, including the following, which we 
respond to in turn:
     For HRG surveys: Surveys should commence during daylight 
hours only; at least one observer or two observers if

[[Page 30933]]

feasible to monitor clearance zones for HRG surveys; a 500 m clearance 
zone for NARW, and, to the extent feasible, a 1,000 m clearance zone 
for NARW, including a delay or shut down if a right whale is observed 
within 1,000 meters from the source.
    Response: Regarding the commenters suggestion that HRG surveys 
should commence during daylight hours only, NMFS acknowledges the 
limitations inherent in detection of marine mammals at night. However, 
in this case no harassment (either Level A or Level B) is expected to 
result from the planned HRG surveys even in the absence of mitigation, 
given the very small estimated Level A and Level B harassment zones. 
Restricting surveys in the manner suggested by the commenters would not 
result in any significant reduction in either intensity or duration of 
noise exposure. Incorporating this measure would also have the 
unintended result of extending the overall duration of HRG surveys, 
thereby resulting in vessels being on the water for an extended period 
of time. Thus the commenters have not demonstrated that such a 
requirement would result in a net benefit. In consideration of 
potential effectiveness of the recommended measure and its 
practicability for the applicant, NMFS has determined that restricting 
survey start-ups to daylight hours is not warranted or practicable in 
this case.
    Regarding the commenters recommendation for a 500 m or 1,000 m 
clearance zone for NARW and a requirement for a delay or shut down if a 
right whale is observed within 1,000 m, NMFS does not expect take to 
result from the HRG surveys as proposed by Dominion even in the absence 
of mitigation measures. The HRG equipment planned for use during 
Dominion's surveys that operates below 180 kHz would be limited to a 
Ultra Short Baseline (USBL), which has a modeled Level B harassment 
zone of less than 25 m, would only be operated when the survey vessel 
moves at a maximum of 1.5 knots, and which has a beam that is pointed 
directly downward toward the seabed with a 90 degree beam. Therefore we 
have determined that the potential conservation benefit from a 500 m or 
1,000 m exclusion zone on these activities would be minimal and 
therefore a requirement for a 500 m or 1,000 m exclusion zone is not 
warranted. The commenters do not provide any meaningful rationale for 
the recommendation.
    Regarding the commenters recommendation for a required PSO or PSOs 
during HRG surveys, as described above, NMFS does not expect take to 
result from the HRG surveys as proposed by Dominion even in the absence 
of mitigation measures, and the HRG equipment planned for use during 
Dominion's surveys that operates below 180 kHz would be limited to a 
USBL, which has a modeled Level B harassment zone of less than 25 m, 
would be operated only when the survey vessel moves at a maximum of 1.5 
knots, and has a beam that is pointed directly downward toward the 
seabed with a 90 degree beam. When balancing the potential conservation 
benefit from a requirement for a PSO (or PSOs) with the costs and 
logistical challenges associated with a requirement to deploy PSOs on 
the survey vessel, especially during the current public health crisis 
associated with the COVID-19 pandemic, we have determined a requirement 
for PSOs during HRG surveys is not warranted.
     A pre-clearance observation period of 60 minutes (versus 
30 minutes as proposed in the notice of proposed IHA) prior to 
beginning or resuming pile driving.
    Response: NMFS agrees with the commenters that a pre-clearance 
observation period of 60 minutes is warranted in this particular 
situation and is practicable for Dominion to implement and we have 
incorporated this requirement in the final IHA.
     All activities, including cable-lay and HRG survey 
activities, should be completed between May and October 2020 due to 
increased presence of NARW from November 1 through April 30.
    Response: NMFS does not expect take to result from the HRG surveys 
or cable-lay activities as proposed by Dominion even in the absence of 
mitigation measures, therefore we have determined that the potential 
conservation benefit from a seasonal restriction on these activities 
would be minimal and do not agree that a requirement for a seasonal 
restriction on these activities is warranted. The commenters do not 
provide adequate support for assertions of potential harm from these 
activities.
     PAM should be required during pile-driving activity and 
HRG surveys.
    Response: While NMFS agrees that PAM can be a useful tool for 
augmenting detection capabilities under certain circumstances, there 
are costs and logistical challenges associated with PAM deployment. 
Thus, the decision as to whether or not to require PAM as a monitoring 
or mitigation measure requires a consideration of the potential 
benefits of PAM specific to the activity and the expected impacts of 
the activity on marine mammals.
    In the case of Dominion's planned pile driving activity, the 
potential impacts to marine mammals are relatively minor: The total 
duration of pile driving is very brief (i.e. an expected total duration 
of approximately four hours of pile driving for the entire project). In 
addition, expected marine mammal exposures would be by Level B 
harassment only, and authorized takes by Level B harassment are very 
low for all species (Table 7). PAM is only capable of detecting marine 
mammals that are actively vocalizing, while many marine mammal species 
vocalize infrequently or only during certain activities, which means 
that only a subset of the animals within the range of the PAM system 
would be detected. Additionally, localization and range detection can 
be challenging depending on the species, configuration of the PAM 
system, and the expertise of the PAM observer. For example, odontocetes 
are fast moving and often travel in large or dispersed groups which 
makes localization difficult. Taking the above factors into 
consideration, and weighing the potential conservation benefits of a 
requirement for PAM against the costs and logistical challenges 
associated with PAM deployment, we have determined that the 
requirements for visual monitoring as proposed in the notice of 
proposed IHA (85 FR 14901; March 16, 2020) are sufficient to ensure the 
least practicable adverse impact on the affected species or stocks and 
their habitat and a requirement for PAM is not warranted for Dominion's 
planned pile driving activities.
    Regarding the commenters recommendation for a PAM requirement 
during HRG surveys, the potential impacts to marine mammals associated 
with Dominion's planned HRG surveys are minor: the area expected to be 
ensonified above the Level B harassment threshold is extremely small 
(less than 25 m to the Level B harassment threshold for the dominant 
source in terms of acoustic propagation), and no takes by Level B 
harassment associated with HRG surveys are expected or authorized. The 
limitations of PAM during HRG surveys include those described above, 
though the logistical challenges associated with localization of marine 
mammals is even greater as the vessel (and the PAM system) are mobile. 
In addition, the ability of PAM to detect baleen whale vocalizations is 
further limited during HRG surveys due to being deployed from the stern 
of a vessel, which puts the PAM hydrophones in proximity to propeller 
noise and low frequency

[[Page 30934]]

engine noise which can mask the low frequency sounds emitted by baleen 
whales, including right whales. Taking the above factors into 
consideration, and weighing the potential conservation benefits of a 
requirement for PAM against the costs and logistical challenges 
associated with PAM deployment, we have determined that the current 
requirements for visual monitoring as proposed in the notice of 
proposed IHA (85 FR 14901; March 16, 2020) are sufficient to ensure the 
least practicable adverse impact on the affected species or stocks and 
their habitat and a requirement for PAM is not warranted for Dominion's 
planned HRG survey activities.
     All project vessels operating within the Project Area, 
including survey and support vessels, should maintain a speed of 10 
knots or less during the entire period covered by the IHA.
    Response: NMFS has analyzed the potential for vessel strike 
resulting from Dominion's activity and has determined that the 
mitigation measures specific to vessel strike avoidance are sufficient 
to avoid the potential for vessel strike. These include the following 
requirements: All vessels must comply with 10 knot or less speed 
restrictions in any Seasonal Management Area (SMA) or Dynamic 
Management Area (DMA); all vessels must reduce vessel speed to 10 knots 
or less when any large whale, any mother/calf pairs, pods, or large 
assemblages of non-delphinoid cetaceans are observed within 100-m of an 
underway vessel; all vessels must 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 sighted North 
Atlantic right whale at 10 knots or less until the 500-m minimum 
separation distance has been established; and, if a North Atlantic 
right whale is sighted in a vessel's path, or within 500-m of an 
underway vessel, the underway vessel must reduce speed and shift the 
engine to neutral. These measures and additional vessel strike 
avoidance measures are described in greater detail below under 
Mitigation. We have determined that these vessel strike avoidance 
measures are sufficient to ensure the least practicable adverse impact 
on species or stocks and their habitat.
     NMFS should ``examine'' noise attenuation at the pile 
itself. While a bubble curtain addresses one pathway of acoustic 
propagation from the monopile, noise attenuation that addresses direct 
entry into the water column, such as through pile casings or dampers, 
should also be examined in the ``least practicable adverse impact'' 
analysis.
    Response: Our response to Comment 1 addresses the use of pile 
casings and dampers. NMFS must prescribe the ``means of effecting the 
least practicable adverse impact'' on the affected species or stocks 
and their habitat, paying particular attention to rookeries, mating 
grounds, and areas of similar significance. In evaluating how 
mitigation may or may not be appropriate to ensure the least 
practicable adverse impact on species or stocks and their habitat 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) and 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 
and impact on operations. In this case, we carefully evaluated 
Dominion's proposed mitigation measures and considered a range of other 
measures, and determined that the measures specific to noise 
attenuation represented the means of effecting the least practicable 
adverse impact on the affected marine mammal species and stocks and 
their habitat.
    We have determined that the suite of mitigation measures required 
in this IHA represent the means of effecting the least practicable 
adverse impact on the affected marine mammal species and stocks and 
their habitat. For more details on the required mitigation measures, 
please see the Mitigation section below.
    Comment 6. The NGOs objected to NMFS' process to consider extending 
any one-year IHA with a truncated 15-day comment period as contrary to 
the MMPA.
    Response: NMFS' IHA Renewal process meets all statutory 
requirements. All IHAs issued, whether an initial IHA or a Renewal IHA, 
are valid for a period of not more than one year. And the public has at 
least 30 days to comment on all proposed IHAs, with a cumulative total 
of 45 days for IHA Renewals. As noted above, the Request for Public 
Comments section made clear that the agency was seeking comment on both 
the initial proposed IHA and the potential issuance of a Renewal for 
this project. Because any Renewal (as explained in the Request for 
Public Comments section) is limited to another year of identical or 
nearly identical activities in the same location (as described in the 
Description of Proposed Activity section) or the same activities that 
were not completed within the one-year period of the initial IHA, 
reviewers have the information needed to effectively comment on both 
the immediate proposed IHA and a possible one-year Renewal, should the 
IHA holder choose to request one in the coming months.
    While additional documents would be required should any such 
Renewal request be submitted, for a qualifying Renewal these will be 
limited to documentation that NMFS will make available and use to 
verify that the activities are identical to those in the initial IHA, 
are nearly identical such that the changes would have either no effect 
on impacts to marine mammals or decrease those impacts, or are a subset 
of activities already analyzed and authorized but not completed under 
the initial IHA. NMFS will also confirm, among other things, that the 
activities will occur in the same location; involve the same species 
and stocks; provide for continuation of the same mitigation, 
monitoring, and reporting requirements; and that no new information has 
been received that would alter the prior analysis. The Renewal request 
will also contain a preliminary monitoring report, specifically to 
verify that effects from the activities do not indicate impacts of a 
scale or nature not previously analyzed. The additional 15-day public 
comment period provides the public an opportunity to review these few 
documents, provide any additional pertinent information and comment on 
whether they think the criteria for a Renewal have been met. Between 
the initial 30-day comment period on these same activities and the 
additional 15 days, the total comment period for a Renewal is 45 days.
    In addition to the IHA Renewal process being consistent with all 
requirements under section 101(a)(5)(D), it is also consistent with 
Congress' intent for issuance of IHAs to the extent reflected in 
statements in the legislative history of the MMPA. Through the 
provision for Renewals in the regulations, description of the process 
and express invitation to comment on specific potential Renewals in the 
Request for Public Comments section of each proposed IHA, the 
description of the process on NMFS' website, further elaboration on the 
process through responses to comments such as these,

[[Page 30935]]

posting of substantive documents on the agency's website, and provision 
of 30 or 45 days for public review and comment on all proposed initial 
IHAs and Renewals respectively, NMFS has ensured that the public ``is 
invited and encouraged to participate fully in the agency decision-
making process.''
    Comment 7. The Commission recommended that NMFS authorize at least 
one take of humpback whales by Level A harassment for each of the two 
days of pile-driving activities (i.e., two Level A harassment takes) 
based on sighting and stranding records for the species in the Mid-
Atlantic.
    Response: Despite exposure modeling that indicated zero takes of 
humpback whales would be expected, NMFS agrees with the Commission that 
based on sightings and stranding records that indicate the potential 
for humpback whales to occur in the project area during pile driving 
activities, authorization of take of humpback whales is warranted. We 
do not, however, agree that take by Level A harassment is likely and we 
have therefore authorized take by Level B harassment only. We have 
authorized two takes by Level B harassment based on the potential for 
one group of humpback whales to be taken during the project. Please see 
the Estimated Take section below for further information.
    Comment 8. The Commission recommended that NMFS increase the Level 
B harassment takes of common dolphins from 39 to 78 based on the 
potential for a group to be taken on both days of the project. The 
Commission also recommended that NMFS increase the Level B harassment 
takes of bottlenose dolphins from 34 to 200 based on visual 
observations of groups of up to 100 animals in previous monitoring 
reports (Milne, 2018) and the potential for a group to be taken on both 
days of the project.
    Response: NMFS has already increased the take estimate for common 
dolphins from the modeled number to mean group size. We do not agree 
with the Commission's assertion that the authorized take number should 
be based on an assumption that one group of common dolphins will be 
encountered on each day of the project; we therefore do not adopt the 
Commission's recommendation to increase take of common dolphins from 39 
to 78. Regarding bottlenose dolphins, we agree that the Level B 
harassment number should be adjusted based on visual observations of 
groups of up to approximately 100 animals in previous monitoring 
reports associated with the Dominion CVOW project (Milne, 2018). 
However, we do not agree with the Commission's recommendation that the 
authorized take number should be increased to 200 based on an 
assumption that one group of bottlenose dolphins will be encountered on 
each day of the project; we therefore authorize 100 incidents of take 
for bottlenose dolphins.
    Comment 9. The Commission expressed concern that some of the 
modeled Level A harassment zones (based on SELcum) exceed modeled Level 
B harassment zones, and recommended that NMFS continue to make this 
issue a priority to resolve in the near future.
    Response: NMFS concurs with the Commission's recommendation and has 
made this issue a priority.
    Comment 10. The Commission recommends that NMFS specify in section 
4(l) of the final authorization that a double bubble curtain must be 
used on the pile that is driven with attenuation.
    Response: NMFS agrees with this recommendation and we have included 
this requirement in the final IHA.
    Comment 11. The Commission recommended that NMFS revise the 
exclusion zones in Table 2 of the final authorization to reflect the 
modeled distances to the Level A harassment thresholds based on SELcum 
for LF and MF cetaceans during unattenuated and attenuated pile driving 
and for HF cetaceans during unattenuated pile driving, as specified in 
Table 4 of the Federal Register notice.
    Response: The Commission recommends that exclusion zones be 
expanded to correspond with the modeled isopleth distances for Level A 
harassment based on the SELcum metric. However, such a requirement 
assumes that a marine mammal observed momentarily within such a zone is 
automatically assumed to be taken by Level A harassment. This 
assumption ignores the fact that the SELcum metric is by definition 
based on accumulation time, i.e. the animal would need to remain within 
that particular zone for whatever accumulation time was incorporated in 
the modeling in order for auditory injury, and thereby take by Level A 
harassment, to occur. While the incorporation of accumulation time via 
the SELcum metric represents a valuable theoretical tool for modeling 
marine mammal exposures, NMFS does not agree that a marine mammal 
observed momentarily within a Level A harassment zone modeled based on 
the SELcum metric is automatically considered to be taken by Level A 
harassment. Therefore, NMFS has determined in this circumstance that an 
exclusion zone that far exceeds the Level A harassment zone based on 
the peak SPL metric (i.e., the zone within which instantaneous exposure 
is assumed to equate to auditory injury) is sufficient to avoid takes 
by Level A harassment. We note that, in the case of this IHA, the 
1,750-m EZ is significantly larger than modeled isopleth distances 
corresponding to Level A harassment (based on peak SPL) for all marine 
mammal functional hearing groups (Table 4). We also note that the EZ 
for North Atlantic right whales would effectively extend beyond 1,750-m 
to as far as PSOs are able to see, i.e., a North Atlantic right whale 
observed at any distance from the pile, regardless of the whale's 
distance from the pile, would trigger further mitigation action (either 
delay or shutdown).
    Comment 12. The Commission recommended that NMFS include in Table 2 
of the final authorization the monitoring zone associated with 
unattenuated pile driving, as specified in Table 4 of the Federal 
Register notice.
    Response: The Commission recommends that the monitoring zone be 
expanded to correspond with the modeled isopleth distance for pile 
driving with no attenuation, for the pile that is ultimately driven 
with no bubble curtains activated. NMFS agrees with the recommendation. 
We have also determined that the monitoring zones should coincide with 
the greatest potential impact distances, which in this case are 
associated with Level A harassment zones modeled based on SELcum (Table 
4). We have therefore revised the monitoring zones for both the one 
pile driven with attenuation and the one pile driven without 
attenuation (Table 8) and we have included the revised monitoring zones 
in Table 2 of the IHA.
    Comment 13. The Commission recommended that NMFS (1) include in 
section 5(c) of the final authorization that hydroacoustic monitoring 
must be conducted and (2) require Dominion's hydroacoustic monitoring 
report to include, along with the information specified in section 5(c) 
of the final authorization, the spatial configuration of the first and 
second bubble curtains relative to the pile, whether and when the 
double bubble curtain is active, and the extents of the Level A and B 
harassment zones for both unattenuated and attenuated pile driving.
    Response: NMFS agrees with this recommendation and we have included 
this requirement in the IHA.
    Comment 14. The Commission recommended that NMFS, in the final 
authorization (1) require Dominion to

[[Page 30936]]

initiate pile driving early enough in the day to ensure that pile 
driving is completed before sunset and (2) remove measure 4(i) that 
allows for pile driving to continue into nighttime hours.
    Response: Regarding the recommendation to require Dominion to 
initiate pile driving early enough in the day to ensure that pile 
driving is completed before sunset, NMFS agrees with this 
recommendation; as a pile driving event is expected to last no more 
than two hours per day, we have included a requirement in the IHA that 
pile driving must not be initiated less than four hours prior to 
sunset. Regarding the recommendation to remove the measure that allows 
for pile driving to continue into nighttime hours, we do not agree with 
the recommendation as it may not be practicable for Dominion to 
implement. Pile driving may continue after dark only when the 
installation of the same pile began during daylight when the Exclusion 
Zone was fully visible for at least four hours, and only in 
extraordinary circumstances when it must proceed for human safety or 
installation feasibility reasons as determined by the lead engineer.
    Comment 15. The Commission recommended that NMFS ensure Dominion 
keeps a running tally of the total takes, based on observed and 
extrapolated takes, for Level A and B harassment.
    Response: NMFS agrees that Dominion is responsible for ensuring 
they do not exceed authorized take numbers. As is typical, we have 
included a requirement in the IHA that activities must cease if 
authorized take numbers are exceeded. However, NMFS does not agree that 
a requirement for PSOs to extrapolate takes based on observed takes as 
pile driving activities are ongoing is practicable as such a 
requirement may result in PSOs' attention being diverted from their 
primary task of observing and documenting marine mammal sightings. NMFS 
is not responsible for ensuring that Dominion does not operate in 
violation of an issued IHA.
    Comment 16. The Commission recommended that NMFS include in all 
draft and final incidental harassment authorizations the explicit 
requirements to cease activities if a marine mammal is injured or 
killed, both during the proposed activities and in the event of a 
vessel strike, until NMFS reviews the circumstances involving any 
injury or death that is likely attributable to the activities and 
determines what additional measures are necessary to minimize 
additional injuries or deaths.
    Response: NMFS does not expect that the proposed activities, 
including HRG surveys, cable-lay activities and offshore pile driving 
activities, have the potential to result in injury or mortality to 
marine mammals and therefore does not agree that a blanket requirement 
for project activities to cease would be warranted. While injury or 
mortality to marine mammals is possible due to vessel strike, NMFS does 
not agree that a requirement for a vessel that is operating on the open 
water to suddenly stop operating is practicable, and it is unclear what 
mitigation benefit would result from such a requirement in relation to 
vessel strike. The Commission does not suggest what measures other than 
those prescribed in this IHA would potentially prove more effective in 
reducing the risk of strike. Therefore, we have not included this 
requirement in the authorization. NMFS retains authority to modify the 
IHA and cease all activities immediately based on a vessel strike and 
will exercise that authority if warranted.
    With respect to the Commission's recommendation that NMFS include 
these requirements in all proposed and final IHAs, NMFS determines the 
requirements for mitigation measures in each authorization based on 
numerous case-specific factors, including 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. As NMFS must 
make these determinations on a case by case basis, we therefore do not 
agree with this recommendation.
    Comment 17. The Commission recommended that NMFS refrain from 
issuing renewals for any authorization and instead use its abbreviated 
Federal Register notice process, which is similarly expeditious and 
fulfills NMFS's intent to maximize efficiencies. If NMFS continues to 
propose to issue renewals, the Commission recommends that it (1) 
stipulate that a renewal is a one-time opportunity (a) in all Federal 
Register notices requesting comments on the possibility of a renewal, 
(b) on its web page detailing the renewal process, and (c) in all draft 
and final authorizations that include a term and condition for a 
renewal and, (2) if NMFS refuses to stipulate a renewal being a one-
time opportunity, explain why it will not do so in its Federal Register 
notices, on its web page, and in all draft and final authorizations.
    Response: NMFS does not agree with the Commission and, therefore, 
does not adopt the Commission's recommendation. NMFS will provide a 
detailed explanation of its decision within 120 days, as required by 
section 202(d) of the MMPA. We addressed why renewals are appropriate 
in certain situations in our Response to Comment 6.

Changes From the Proposed IHA to Final IHA

    As described above, the following revisions has been made to 
authorized take numbers:
     Authorized take by Level B harassment of humpback whales 
has been increased from zero to two; and
     Authorized take by Level B harassment of bottlenose 
dolphins has been increased from 34 to 100.
    Also as described above, the following revisions have been made to 
mitigation and monitoring measures:
     The duration for monitoring for marine mammals prior to 
initiation of pile driving has been increased from 30 minutes to 60 
minutes;
     The minimum amount of time before sunset that pile driving 
must start has been increased from 30 minutes to four hours; and
     The monitoring zones have been revised to coincide with 
modeled Level A harassment zones based on SELcum (Table 8).

Description of Marine Mammals in the Area of Specified Activity

    Sections 4 and 5 of the IHA application summarize available 
information regarding status and trends, distribution and habitat 
preferences, and behavior and life history, of the potentially affected 
species. Additional information regarding population trends and threats 
may be found in NMFS' Stock Assessment Reports (SARs; 
www.fisheries.noaa.gov/national/marine-mammal-protection/marine-mammal-stock-assessments) and more general information about these species 
(e.g., physical and behavioral descriptions) may be found on NMFS' 
website (www.fisheries.noaa.gov/find-species).
    All species that could potentially occur in the project area are 
included in Table 4-1 of the IHA application. However, the temporal 
and/or spatial occurrence of several species listed in Table 4-1 of the 
IHA application is such that take of these species is not expected to 
occur either because they have very low densities in the project area 
and/or are extralimital to the project area. These are: The blue whale 
(Balaenoptera musculus), fin whale (Balaenoptera physalus), sei whale 
(Balaenoptera borealis), North Atlantic

[[Page 30937]]

right whale (Eubalaena glacialis), minke whale (Balaenoptera 
acutorostrata), Bryde's whale (Balaenoptera edeni), sperm whale 
(Physeter macrocephalus), long-finned and short-finned pilot whale 
(Globicephala spp.), Cuvier's beaked whale (Ziphius cavirostris), four 
species of Mesoplodont beaked whale (Mesoplodon spp.), dwarf and pygmy 
sperm whale (Kogia sima and Kogia breviceps), northern bottlenose whale 
(Hyperoodon ampullatus), pygmy killer whale (Feresa attenuata), false 
killer whale (Pseudorca crassidens), melon-headed whale (Peponocephala 
electra), harbor porpoise (Phocoena phocoena), Risso's dolphin (Grampus 
griseus), striped dolphin (Stenella coeruleoalba), white-beaked dolphin 
(Lagenorhynchus albirostris), pantropical spotted dolphin (Stenella 
attenuata), Fraser's dolphin (Lagenodelphis hosei), rough-toothed 
dolphin (Steno bredanensis), Clymene dolphin (Stenella clymene), 
spinner dolphin (Stenella longirostris), hooded seal (Cystophora 
cristata), and harp seal (Pagophilus groenlandicus). As take of these 
species is not anticipated as a result of the planned activities, these 
species are not analyzed further in this document.
    Table 1 summarizes information related to the population or stock, 
including regulatory status under the MMPA and ESA and potential 
biological removal (PBR), where known. For taxonomy, we follow 
Committee on Taxonomy (2019). PBR is 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 (as described in NMFS' 
SARs). While no mortality is anticipated or authorized here, PBR is 
included here as a gross indicator of the status of the species and 
other threats.
    Marine mammal abundance estimates presented in this document 
represent the total number of individuals that make up a given stock or 
the total number estimated within a particular study or survey area. 
NMFS' stock abundance estimates for most species represent the total 
estimate of individuals within the geographic area, if known, that 
comprises that stock. For some species, this geographic area may extend 
beyond U.S. waters. All managed stocks in this region are assessed in 
NMFS' U.S. Atlantic SARs. All values presented in Table 1 are the most 
recent available at the time of publication and are available in the 
2019 draft Atlantic SARs (Hayes et al., 2019), available online at: 
www.fisheries.noaa.gov/national/marine-mammal-protection/marine-mammal-stock-assessment-reports-region.

                         Table 1--Marine Mammals Known To Occur in the Project Area That May Be Affected by Dominion's Activity
--------------------------------------------------------------------------------------------------------------------------------------------------------
                                                        MMPA and ESA     Stock abundance
                                                           status;       (CV, Nmin, most         Predicted                 Annual  M/    Occurrence in
  Common name (scientific name)          Stock          strategic (Y/    recent abundance   abundance (CV) \3\   PBR \4\     SI \4\      project area
                                                           N) \1\          survey) \2\
--------------------------------------------------------------------------------------------------------------------------------------------------------
                                                               Toothed whales (Odontoceti)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Atlantic white-sided dolphin      W. North Atlantic..  --; N           93,233 (0.71;        37,180 (0.07).....        544         26  Common.
 (Lagenorhynchus acutus).                                               54,443; n/a).
Common dolphin (Delphinus         W. North Atlantic..  --; N           172,825 (0.21;       86,098 (0.12).....      1,452        419  Common.
 delphis).                                                              145,216; 2011).
Atlantic spotted dolphin          W. North Atlantic..  --; N           39,921 (0.27;        55,436 (0.32).....        320          0  Common.
 (Stenella frontalis).                                                  32,032; 2012).
Bottlenose dolphin (Tursiops      W. North Atlantic,   --; N           62,851 (0.23;        97,476 (0.06) \5\.         23         28  Common offshore.
 truncatus).                       Offshore.           --; N            51,914; 2011).                                        0-14.3  Common nearshore
                                  W. North Atlantic,                   3,751 (0.06; 2,353;                                             in summer.
                                   Southern Migratory                   n/a).
                                   Coastal.
Harbor porpoise (Phocoena         Gulf of Maine/Bay    --; N           79,833 (0.32;        45,089 (0.12).....        706        255  Common.
 phocoena).                        of Fundy.                            61,415; 2011).
--------------------------------------------------------------------------------------------------------------------------------------------------------
                                                                Baleen whales (Mysticeti)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Humpback whale (Megaptera         Gulf of Maine......  --; N           1,396 (0; 1,380; n/  1,637 (0.07) *....         22      12.15  Common.
 novaeangliae).                                                         a).
--------------------------------------------------------------------------------------------------------------------------------------------------------
                                                                Earless seals (Phocidae)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Gray seal \6\ (Halichoerus        W. North Atlantic..  --; N           27,131 (0.19;        ..................      1,389      5,410  Common.
 grypus).                                                               23,158; n/a).
Harbor seal (Phoca vitulina)....  W. North Atlantic..  --; N           75,834 (0.15;        ..................      2,006        350  Common.
                                                                        66,884; 2012).
--------------------------------------------------------------------------------------------------------------------------------------------------------
\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\ Stock abundance as reported in NMFS marine mammal stock assessment reports (SAR) except where otherwise noted. SARs available online at:
  www.fisheries.noaa.gov/national/marine-mammal-protection/marine-mammal-stock-assessments. 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 2019 draft Atlantic SARs (Hayes et al., 2019).
\3\ This information represents species- or guild-specific abundance predicted by recent habitat-based cetacean density models (Roberts et al., 2016,
  2017, 2018). These models provide the best available scientific information regarding predicted density patterns of cetaceans in the U.S. Atlantic
  Ocean, and we provide the corresponding abundance predictions as a point of reference. Total abundance estimates were produced by computing the mean
  density of all pixels in the modeled area and multiplying by its area. For those species marked with an asterisk, the available information supported
  development of either two or four seasonal models; each model has an associated abundance prediction. Here, we report the maximum predicted abundance.
\4\ 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). Annual M/SI, found in NMFS' SARs,
  represent annual levels of human-caused mortality plus serious injury from all sources combined (e.g., commercial fisheries, subsistence hunting, ship
  strike). Annual M/SI values often cannot be determined precisely and is in some cases presented as a minimum value. All M/SI values are as presented
  in the draft 2019 SARs (Hayes et al., 2019).

[[Page 30938]]

 
\5\ Abundance estimates are in some cases reported for a guild or group of species when those species are difficult to differentiate at sea. Similarly,
  the habitat-based cetacean density models produced by Roberts et al. (2016, 2017, 2018) are based in part on available observational data which, in
  some cases, is limited to genus or guild in terms of taxonomic definition. Roberts et al. (2016, 2017, 2018) produced a density model for bottlenose
  dolphins that does not differentiate between offshore and coastal stocks.
\6\ NMFS stock abundance estimate applies to U.S. population only, actual stock abundance is approximately 505,000.

    A detailed description of the species likely to be affected by 
Dominion's activities, 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 notice of proposed IHA (85 FR 14901; March 16, 2020). 
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 notice for these descriptions. Please also 
refer to NMFS' website (www.fisheries.noaa.gov/find-species) for 
generalized species accounts.

Potential Effects of Specified Activities on Marine Mammals and Their 
Habitat

    The effects of underwater noise from Dominion's construction 
activities have the potential to result in behavioral harassment of 
marine mammals in the vicinity of the project area. The notice of 
proposed IHA (85 FR 14901; March 16, 2020) included a discussion of the 
effects of anthropogenic noise on marine mammals and the potential 
effects of underwater noise from Dominion's construction activities on 
marine mammals and their habitat. That information and analysis is 
incorporated by reference into this final IHA determination and is not 
repeated here; please refer to the notice of proposed IHA (85 FR 14901; 
March 16, 2020).

Estimated Take

    This section provides an estimate of the number of incidental takes 
authorized through the IHA, which will inform both NMFS' consideration 
of ``small numbers'' 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, section 3(18) of 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, as noise from pile 
driving has the potential to result in disruption of behavioral 
patterns for individual marine mammals. Impact pile driving has source 
characteristics (short, sharp pulses with higher peak levels and 
sharper rise time to reach those peaks) that are potentially injurious 
or more likely to produce severe behavioral reactions. However, 
modeling indicates there is limited potential for auditory injury even 
in the absence of the proposed mitigation measures, with no species 
predicted to experience Level A harassment. In addition, the already 
limited potential for injury is expected to be minimized through 
implementation of the proposed mitigation measures including soft start 
and the implementation of EZs that would facilitate a delay of pile 
driving if marine mammals were observed approaching or within areas 
that could be ensonified above sound levels that could result in 
auditory injury. Given sufficient notice through use of soft start, 
marine mammals are expected to move away from a sound source that is 
annoying prior to its becoming potentially injurious or resulting in 
more severe behavioral reactions. No Level A harassment of any marine 
mammal stocks are anticipated or authorized.
    As described previously, no mortality is anticipated or authorized 
for this activity. Below we describe how the take is estimated.
    Generally speaking, 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) 
and the number of days of activities. We note that while these basic 
factors can contribute to a basic calculation to provide an initial 
prediction of takes, additional information that can qualitatively 
inform take estimates is also sometimes available (e.g., previous 
monitoring results or average group size). Below, we describe the 
factors considered here in more detail and present the 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 PTS 
of some degree (equated to Level A harassment).
    Level B Harassment--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., 2012). 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 160 dB re 1 [mu]Pa (rms) 
for impulsive and/or intermittent sources (e.g., impact pile driving) 
and 120 dB rms for continuous sources (e.g., vibratory driving). 
Dominion's planned activity includes the use of impulsive sources 
(i.e., impact pile driving equipment) therefore use of the 160 dB re 1 
[mu]Pa (rms) threshold is applicable.
    Level A harassment--NMFS' Technical Guidance for Assessing the 
Effects of Anthropogenic Sound on Marine Mammal Hearing (Version 2.0) 
(Technical Guidance, 2018) 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). The 
components of Dominion's planned activity that may result in the take 
of marine mammals include the use of impulsive sources.
    These thresholds are provided in Table 2 below. The references, 
analysis, and methodology used in the development of the thresholds are

[[Page 30939]]

described in NMFS 2018 Technical Guidance, which may be accessed at: 
www.fisheries.noaa.gov/national/marine-mammal-protection/marine-mammal-acoustic-technical-guidance.

                     Table 2--Thresholds Identifying the Onset of Permanent Threshold Shift
----------------------------------------------------------------------------------------------------------------
                                                     PTS onset acoustic thresholds * (received level)
             Hearing group              ------------------------------------------------------------------------
                                                  Impulsive                         Non-impulsive
----------------------------------------------------------------------------------------------------------------
Low-Frequency (LF) Cetaceans...........  Cell 1: Lpk,flat: 219 dB;   Cell 2: LE,LF,24h: 199 dB.
                                          LE,LF,24h: 183 dB.
Mid-Frequency (MF) Cetaceans...........  Cell 3: Lpk,flat: 230 dB;   Cell 4: LE,MF,24h: 198 dB.
                                          LE,MF,24h: 185 dB.
High-Frequency (HF) Cetaceans..........  Cell 5: Lpk,flat: 202 dB;   Cell 6: LE,HF,24h: 173 dB.
                                          LE,HF,24h: 155 dB.
Phocid Pinnipeds (PW) (Underwater).....  Cell 7: Lpk,flat: 218 dB;   Cell 8: LE,PW,24h: 201 dB.
                                          LE,PW,24h: 185 dB.
Otariid Pinnipeds (OW) (Underwater)....  Cell 9: Lpk,flat: 232 dB;   Cell 10: LE,OW,24h: 219 dB.
                                          LE,OW,24h: 203 dB.
----------------------------------------------------------------------------------------------------------------
* 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.
Note: Peak sound pressure (Lpk) has a reference value of 1 [micro]Pa, and cumulative sound exposure level (LE)
  has a reference value of 1[micro]Pa\2\s. In this Table, thresholds are abbreviated to reflect American
  National Standards Institute standards (ANSI 2013). However, peak sound pressure is defined by ANSI as
  incorporating frequency weighting, which is not the intent for this Technical Guidance. Hence, the subscript
  ``flat'' is being included to indicate peak sound pressure should be flat weighted or unweighted within the
  generalized hearing range. The subscript associated with cumulative sound exposure level thresholds indicates
  the designated marine mammal auditory weighting function (LF, MF, and HF cetaceans, and PW and OW pinnipeds)
  and that the recommended accumulation period is 24 hours. The cumulative sound exposure level thresholds could
  be exceeded in a multitude of ways (i.e., varying exposure levels and durations, duty cycle). When possible,
  it is valuable for action proponents to indicate the conditions under which these acoustic thresholds will be
  exceeded.

Ensonified Area

    Here, we describe operational and environmental parameters of the 
activity that will feed into identifying the area ensonified above the 
acoustic thresholds, which include source levels and transmission loss 
coefficient.
    As described above, Dominion proposes to install two WTGs on 
monopile foundations. The WTG monopile foundations would each be 7.8-m 
in diameter. The expected hammer energy required to drive the two 
monopiles is 600 kJ, though a maximum potential hammer energy of 1,000 
kJ may be required. Bubble curtains would also be deployed to attenuate 
pile driving noise on at least one of the piles. Dominion performed 
acoustic modeling based on scenarios including 600 kJ and 1,000 kJ 
hammer energy, and on attenuation levels of 15 dB, 10 dB, 6 dB and 0 dB 
achieved from the deployment of the bubble curtains.
    Modeling was performed using the software dBSea, a 3D model 
developed by Marshall Day Acoustics that is built by importing 
bathymetry data and placing noise sources in the environment. The dBSea 
model allows for the incorporation of several site-specific properties 
including sound speed profile, temperature, salinity, and current. 
Noise levels are calculated throughout the project area and displayed 
in 3D. The model also allows for the incorporation of several 
``solvers''. Two such ``solvers'' were incorporated in the modeling:
     dBSeaPE (Parabolic Equation Method): The dBSeaPE solver 
makes use of the parabolic equation method, a versatile and robust 
method of marching the sound field out in range from the sound source; 
and
     dBSeaRay (Ray Tracing Method): The dBSeaRay solver forms a 
solution by tracing rays from the source to the receiver. Many rays 
leave the source covering a range of angles, and the sound level at 
each point in the receiving field is calculated by coherently summing 
the components from each ray.
    The number of strikes per pile incorporated in the model were 3,419 
blows for the first foundation and 4,819 blows for the second 
foundation at a rate of 40 blows per minute (the difference in the 
number of anticipated blows is due to different soil conditions at the 
two WTG locations). These estimates of the number of blows required are 
considered conservative; the actual number of blows anticipated for the 
first and second foundations may ultimately be less. Source levels 
incorporated in the model were derived from data recorded at the Walney 
Extension Offshore Wind Farm located off the coast of England (NIRAS 
Consulting Ltd, 2017). Data from the Walney Extension project 
represents a suitable proxy for the planned project as the piles at the 
Walney Extension project were the same diameter as those planned for 
use in the CVOW project (i.e., 7.8-m) and water depth at the Walney 
Extension project was very similar to that at the CVOW project site (a 
depth of 28-m at the Walney Extention project compared to a depth of 
25-m at the CVOW project site). Source levels derived from the Walney 
Extension project and used in the modeling are shown in Table 3.

Table 3--Source Levels Used in Modeling Pile Driving Noise From the CVOW
                                 Project
------------------------------------------------------------------------
         Hammer energy  scenario             Source level  at 1 meter
------------------------------------------------------------------------
600 kJ Hammer Energy....................  222 dBrms90.
                                          213 SEL.
                                          235 Peak.
1,000 kJ Hammer Energy..................  224 dBrms90.
                                          215 SEL.
                                          237 Peak.
------------------------------------------------------------------------

    Acoustic modeling was performed for scenarios including 600 kJ and 
1,000 kJ hammer energy. To be conservative, it was assumed for purposes 
of the exposure estimate that 1,000 kJ hammer energy would be required 
at all times during the driving of both piles. This represents a 
conservative assumption, as less energy may ultimately be required. 
Modeling scenarios included potential attenuation levels of 15 dB, 10 
dB, 6 dB and 0 dB achieved from the deployment of the attenuation 
system. Table 4 shows modeled isopleth distances to Level A and Level B 
harassment thresholds based on 1,000 kJ hammer energy and potential 
attenuation levels of 15 dB, 10 dB, 6 dB and 0 dB. Level A harassment 
isopleths vary based on marine mammal functional hearing groups. The 
updated acoustic thresholds for impulsive sounds (such as pile driving) 
contained in the Technical Guidance (NMFS, 2018) were presented as dual 
metric acoustic thresholds using both cumulative sound exposure level

[[Page 30940]]

(SELcum) and peak sound pressure level metrics. As dual 
metrics, NMFS considers onset of PTS (Level A harassment) to have 
occurred when either one of the two metrics is exceeded (i.e., the 
metric resulting in the largest isopleth). The SELcum metric 
considers both level and duration of exposure, as well as auditory 
weighting functions by marine mammal hearing group.

    Table 4--Modeled Radial Distances to Thresholds Corresponding to Level A and Level B Harassment From Pile Driving Based on 1,000 kJ Hammer Energy
--------------------------------------------------------------------------------------------------------------------------------------------------------
                                                           Radial distance to Level A harassment threshold (m) *                        Radial distance
                                     -------------------------------------------------------------------------------------------------     to Level B
                                                                                                                                           harassment
        Attenuation scenario               High frequency           Low frequency           Mid frequency         Phocid pinnipeds       threshold (m)
                                       cetaceans (peak SPL /    cetaceans (peak SPL /   cetaceans (peak SPL/   (underwater) (peak SPL/------------------
                                              SELcum)                  SELcum)                 SELcum)                 SELcum)             All marine
                                                                                                                                            mammals
--------------------------------------------------------------------------------------------------------------------------------------------------------
No attenuation......................  325/2,670..............  282/5,930.............  182/397...............  N/A/1,722.............              5,175
6 dB Reduction......................  80/1,277...............  N/A/3,830.............  N/A/252...............  N/A/567...............              3,580
10 dB Reduction.....................  N/A/314................  N/A/2,217.............  N/A/229...............  N/A/317...............              2,520
15 dB Reduction.....................  N/A/233................  N/A/1,277.............  N/A/124...............  N/A/236...............              1,370
--------------------------------------------------------------------------------------------------------------------------------------------------------
* N/A indicates the distance to the threshold is so low it was undetectable in the modeling results.

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.
    The habitat-based density models produced by the Duke University 
Marine Geospatial Ecology Laboratory (Roberts et al., 2016, 2017, 2018) 
represent the best available information regarding marine mammal 
densities in the project area. The density data presented by Roberts et 
al. (2016, 2017, 2018) incorporates aerial and shipboard line-transect 
survey data from NMFS and other organizations and incorporates data 
from 8 physiographic and 16 dynamic oceanographic and biological 
covariates, and controls for the influence of sea state, group size, 
availability bias, and perception bias on the probability of making a 
sighting. These density models were originally developed for all 
cetacean taxa in the U.S. Atlantic (Roberts et al., 2016). In 
subsequent years, certain models have been updated on the basis of 
additional data as well as certain methodological improvements. The 
updated models incorporate additional sighting data, including 
sightings from the NOAA Atlantic Marine Assessment Program for 
Protected Species (AMAPPS) surveys from 2010-2014 (NEFSC & SEFSC, 2011, 
2012, 2014a, 2014b, 2015, 2016). More information, including the 
initial model results and supplementary information for each model, is 
available online at seamap.env.duke.edu/models/Duke-EC-GOM-2015/.
    Marine mammal density estimates in the project area (animals/km\2\) 
were obtained using the model results from Roberts et al. (2016, 2017, 
2018). While pile driving activities are planned for May, these 
activities could potentially occur any time between May and October. 
Average seasonal marine mammal densities were developed for each 
species and for each season when pile driving activities may occur 
using maximum monthly densities for each species, as reported by 
Roberts et al. (2016; 2017; 2018) (Densities from March through May 
were averaged for spring; June through August densities were averaged 
for summer; and September through November densities were averaged for 
fall). To be conservative, the highest average seasonal density for 
each species was then carried forward in the analysis (i.e., whichever 
of the three seasonal average densities was highest for each species 
was applied to the exposure estimate). The maximum seasonal density 
values used in the exposure estimates are shown in Table 7 below.

Take Calculation and Estimates

    Here we describe how the information provided above is brought 
together to produce a quantitative take estimate. In order to estimate 
the number of marine mammals predicted to be exposed to sound levels 
that would result in harassment, radial distances to predicted 
isopleths corresponding to harassment thresholds were calculated, as 
described above. The radial distances modeled based on scenarios of 
1,000 kJ hammer energy and 6 dB attenuation, 10 dB attenuation, 15 dB 
attenuation, and no attenuation (Table 4) were then used to calculate 
the areas around the pile predicted to be ensonified to sound levels 
that exceed relevant harassment thresholds.
    Marine mammal density values were overlaid on the ensonified zones 
to relevant thresholds within a geographic information system (GIS). 
The density values were multiplied by these zones, resulting in daily 
Level A and Level B harassment exposure estimates. These estimates were 
then multiplied by the number of days of pile driving activity (i.e., 
two) in order to estimate the number of marine mammals that would be 
exposed to pile driving noise above relevant thresholds for the entire 
project. The exposure numbers were rounded to the nearest whole 
individual.
    The following formula describes these steps:

Estimated Take = D x Z x (d)

Where:

D = average highest species density
ZOI = maximum ensonified area to relevant thresholds
d = number of days

    Dominion provided exposure estimates based on two days of pile 
driving for each scenario (i.e., no attenuation, 6 dB attenuation, 10 
dB attenuation and 15 dB attenuation). However, as Dominion has 
proposed driving one pile with the attenuation system activated and the 
other pile without the attenuation system activated (described further 
under Mitigation, below), we assumed for the exposure estimate that one 
pile would be driven with no attenuation and the other pile would be 
driven with an attenuation system that would achieve an overall 6 dB 
reduction in pile driving sound. Thus we halved the exposure estimates 
provided for the 0 dB attenuation and 6 dB attenuation scenarios to 
come up with exposure estimates for one day of pile driving for each 
scenario (i.e., one pile driven with no attenuation, and the other pile 
driven with 6 dB attenuation). We then combined these to come up with 
exposure estimates for the two piles. We note that an estimate of an 
overall 6 dB reduction from the attenuation system

[[Page 30941]]

represents a conservative assumption, as the attenuation system planned 
for use is a double bubble curtain which may ultimately result in a 
greater level of attenuation than the assumed 6 dB (the attenuation 
system proposed for use is described further under Mitigation, below).
    Table 5 shows modeled exposures above the Level A harassment 
threshold for each of the two piles and both piles combined. Note that 
modeling resulted in no takes by Level A harassment for any species, 
thus we do not authorize any takes by Level A harassment and outputs in 
Table 5 are for illustrative purposes only. Table 6 shows modeled 
exposures above the Level B harassment threshold for each of the two 
piles and both piles combined. Table 7 shows maximum seasonal densities 
used in the take estimate, the number of takes authorized, and the 
total takes as a percentage of population.

  Table 5--Modeled Exposures Above the Level A Harassment Threshold Estimated for Each Pile and for Both Piles
                                                    Combined
----------------------------------------------------------------------------------------------------------------
                                                                                   One pile with
                             Species                               One pile with       6 dB         Both piles
                                                                  no attenuation    attenuation      combined
----------------------------------------------------------------------------------------------------------------
Atlantic-spotted Dolphin........................................          0.0025           0.001          0.0035
White-sided Dolphin.............................................           0.005           0.002           0.007
Bottlenose Dolphin (W.N.A. Offshore)............................           0.118          0.0475          0.1655
Bottlenose Dolphin (W. N. A. Southern Coastal Migratory)........           0.118          0.0475          0.1655
Risso's Dolphin.................................................               0               0               0
Common Dolphin..................................................           0.008           0.003           0.011
Pilot Whales....................................................               0               0               0
Sperm Whale.....................................................               0               0               0
Fin Whale.......................................................           0.256          0.1065          0.3625
Harbor Porpoise.................................................            0.17           0.039           0.209
Humpback Whale..................................................            0.11           0.046           0.156
Minke Whale.....................................................          0.1065          0.0445           0.151
North Atlantic Right Whale......................................          0.0845          0.0355            0.12
Sei Whale.......................................................           0.002          0.0005          0.0025
Harbor Seal.....................................................           0.086          0.0095          0.0955
Gray Seal.......................................................           0.086          0.0095          0.0955
----------------------------------------------------------------------------------------------------------------


  Table 6--Modeled Exposures Above the Level B Harassment Threshold Estimated for Each Pile and for Both Piles
                                                    Combined
----------------------------------------------------------------------------------------------------------------
                                                                                   One pile with    Both piles
                            Species *                              One pile with       6 dB          combined
                                                                  no attenuation    attenuation      (rounded)
----------------------------------------------------------------------------------------------------------------
Common dolphin..................................................            1.34            0.45               2
Atlantic-spotted dolphin........................................            0.43            0.14               1
Atlantic white-sided dolphin....................................            0.86            0.29               1
Bottlenose dolphin (W. N. A. Offshore)..........................           20.08            6.75              27
Bottlenose dolphin (W. N. A. Southern Coastal Migratory)........           20.08            6.75              27
Harbor porpoise.................................................            0.64            0.22               1
Harbor seal.....................................................            0.78            0.26               1
Gray seal.......................................................            0.78            0.26               1
----------------------------------------------------------------------------------------------------------------
* All species potentially occurring in the project area were modeled; only species with at least one exposure
  above the Level B harassment threshold that were carried forward in the take analysis are shown.


Table 7--Marine Mammal Densities, Numbers of Potential Incidental Take of Marine Mammals Authorized and Takes as
                                           a Percentage of Population
----------------------------------------------------------------------------------------------------------------
                                                                                                       Total
                                                                     Estimated         Total        authorized
                                                      Density     takes by Level    authorized      takes as a
                     Species                       (animals/ 100  B harassment 1  takes by Level   percentage of
                                                       km2)                        B harassment    population 2
 
----------------------------------------------------------------------------------------------------------------
Humpback whale..................................           0.099               0               2             0.1
Common dolphin 3................................           1.591               2              39             0.0
Atlantic white-sided dolphin 3..................           1.018               1              40             0.1
Bottlenose dolphin (W. N. Atlantic Coastal                23.861              27             100             2.7
 Migratory) 4 5.................................
Bottlenose dolphin (W. N. Atlantic Offshore) 4 5          23.861              27             100             0.2
Atlantic spotted dolphin 3......................           0.508               1             100             0.3
Harbor porpoise 3...............................           0.760               1               4             0.0
Gray seal 4.....................................           0.925               1               1             0.0
Harbor seal 4...................................           0.925               1               1             0.0
----------------------------------------------------------------------------------------------------------------
1 Estimated takes based on a scenario of 1,000 kJ hammer energy and one pile driven with 6 dB attenuation and
  the other pile driven with no attenuation.
2 Calculations of percentage of stock taken are based on the best available abundance estimate as shown in Table
  1. In most cases the best available abundance estimate is provided by Roberts et al. (2016, 2017, 2018), when
  available, to maintain consistency with density estimates derived from Roberts et al. (2016, 2017, 2018).

[[Page 30942]]

 
3 Number of authorized takes (Level B harassment only) for these species has been increased from the modeled
  take number to mean group size. Sources for group size estimates are as follows: Atlantic white-sided dolphin:
  Cipriano (2018); common dolphin: Palka et al. (2015); harbor porpoise: Palka et al. (2015); Atlantic spotted
  dolphin: Herzing and Perrin (2018); humpback whale: NOAA Fisheries Northeast and Southeast Fisheries Science
  Centers (2019, 2018, 2017, 2016, 2015, 2014, 2013, 2012, 2011).
4 Roberts et al. (2016, 2017, 2018) produced a single density model for all bottlenose dolphins and did not
  differentiate by bottlenose dolphin stocks, and produced a single density model for all seals and did not
  differentiate between seal species. Hence, the density value is the same for both stocks of bottlenose dolphin
  stocks that may be present and for both seal species.
5 Number of authorized takes (Level B harassment only) has been increased from the modeled take number to a
  group size estimate based on sighting records from previously-submitted Dominion monitoring reports.

    Modeling results predicted no takes by Level A harassment for any 
marine mammal species (based on both SELcum and peak SPL) 
(See Table 5). NMFS has therefore determined that the likelihood of 
take of marine mammals in the form of Level A harassment occurring as a 
result of the planned activity is so low as to be discountable, and we 
do not authorize the take by Level A harassment of any marine mammals.
    Using the take methodology approach described above, the resulting 
take estimates for humpback whale, Atlantic white-sided dolphin, common 
dolphin, spotted dolphin and harbor porpoise were less than the average 
group sizes estimated for these species. However, information on the 
life histories of these species indicates they are likely to be 
encountered in groups, therefore it is reasonable to conservatively 
assume that one group of each of these species will be taken during the 
planned activities. We therefore authorize the take of the average 
group size for these species to account for the possibility that a 
group of any of these species or stocks is taken by the planned 
activities (Table 7). We note that for humpback whales zero takes by 
Level B harassment were modeled, however as described above we have 
authorized the take of the mean group size of humpback whales (i.e., 
two) based on a recommendation from the Marine Mammal Commission that 
authorized takes of humpback whales are warranted based on stranding 
and sighting records.
    Roberts et al. (2016, 2017, 2018) produced a single density model 
for all bottlenose dolphins and did not differentiate by bottlenose 
dolphin stocks. The Western North Atlantic southern migratory coastal 
stock occurs in coastal waters from the shoreline to approximately the 
20-m isobath (Hayes et al. 2019). The water depth at the WTG 
installation location is 25 m. As 20-m represents an approximate depth 
limit for the coastal stock, both stocks have the potential to occur in 
the project area. Therefore we authorize take for both stocks. The take 
calculation methodology described above resulted in an estimate of 27 
bottlenose dolphin Level B harassment takes. However, the number of 
authorized Level B harassment takes of bottlenose dolphins has been 
increased from the modeled number to 100 based on an observation of a 
group of approximately 100 bottlenose dolphins in a previous monitoring 
report associated with Dominion offshore wind activity near the project 
area (Milne et al, 2018). We have concluded that since either stock may 
be present it is possible that all estimated takes may accrue to either 
of the stocks and we therefore authorize 100 takes from both stocks 
that may be present.
    Similar to bottlenose dolphins, Roberts et al. (2018) produced 
density models for all seals and did not differentiate by seal species. 
Because the seasonality of, and habitat use by, gray seals roughly 
overlaps with that of harbor seals in the project area, it is possible 
that modeled seal takes could occur to either species. The take 
calculation methodology described above resulted in an estimate of one 
seal take. As the one modeled seal take may accrue to either seal 
species we therefore authorize one take from both seal species that may 
be present. We are therefore authorizing twice the amount of takes that 
the exposure modeling predicts for seal species.

Mitigation

    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 
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.
    The mitigation measures described below are consistent with those 
required and successfully implemented under previous incidental take 
authorizations issued in association with in-water construction 
activities. Modeling was performed to estimate zones of influence (ZOI; 
see ``Estimated Take''); these ZOI values were used to inform 
mitigation measures for pile driving activities to eliminate Level A 
harassment and minimize Level B harassment, while providing estimates 
of the areas within which Level B harassment might occur.
    In addition to the specific measures described below, Dominion 
would conduct briefings for construction supervisors and crews, the 
marine mammal monitoring teams, and Dominion staff prior to the start 
of all pile driving activity, and when new personnel join the work, in 
order to explain responsibilities, communication procedures, the marine 
mammal monitoring protocol, and operational procedures.

Seasonal Restriction on Pile Driving

    No pile driving activities may occur from November 1 through April 
30. This

[[Page 30943]]

seasonal restriction has been established to minimize the potential for 
North Atlantic right whales to be exposed to pile driving noise. Based 
on the best available information (Roberts et al., 2017), the highest 
densities of right whales in the project area are expected during the 
months of November 1 through April when right whales are migrating. 
This restriction will greatly reduce the potential for right whale 
exposure to pile driving noise associated with the project.

Pre-Clearance, Exclusion and Monitoring Zones

    Dominion will use PSOs to establish a 1,750-m exclusion zone (EZ) 
around the pile driving equipment to ensure this zone is clear of 
marine mammals prior to the start of pile driving. The purpose of 
``clearance'' of a particular zone is to prevent potential instances of 
auditory injury and potential instances of more severe behavioral 
disturbance as a result of exposure to pile driving noise (serious 
injury or death are unlikely outcomes even in the absence of mitigation 
measures) by delaying the activity before it begins if marine mammals 
are detected within certain pre-defined distances of the pile driving 
equipment. The primary goal in this case is to prevent auditory injury 
(Level A harassment), and while we acknowledge that porpoises or seals 
may not be detected at this distance, the 1,750-m EZ is significantly 
larger than modeled distances to isopleth distances corresponding to 
Level A harassment (based on peak SPL) for all marine mammal functional 
hearing groups (Table 4). The EZ for North Atlantic right whales would 
effectively extend beyond 1,750-m to as far as PSOs are able to see 
(i.e., a North Atlantic right whale observed at any distance from the 
pile, regardless of the whale's distance from the pile, would trigger 
further mitigation action (either delay or shutdown)).
    In addition to the EZ, PSOs must observe a monitoring zone that 
corresponds with the greatest potential impact zone which in this case 
is associated with the modeled distance to the Level A harassment 
isopleth (based on SELcum) for low-frequency cetaceans (Table 4) during 
pile driving activities. PSOs must record information on marine mammals 
observed within the monitoring zone, including species, observed 
behavior, and estimates of number of marine mammals exposed to pile 
driving noise within the Level B harassment zone. Marine mammals 
observed within the monitoring zone but outside the EZs would not 
trigger any mitigation action. All distances are the radius from the 
center of the pile.

                 Table 8--Exclusion and Monitoring Zones
------------------------------------------------------------------------
                                            Monitoring zone (pile driven
              Exclusion zone                with /without active  bubble
                                                      curtains)
------------------------------------------------------------------------
1,750 m *.................................  3,830 m/5,930 m.
------------------------------------------------------------------------
* A North Atlantic right whale observed at any distance from the pile
  would trigger delay or shutdown of pile driving.

    If a marine mammal is observed approaching or entering the relevant 
EZ prior to the start of pile driving operations, pile driving activity 
must be delayed until either the marine mammal has voluntarily left the 
respective EZ and been visually confirmed beyond that zone, or, 15 
minutes have elapsed without re-detection of the animal in the case of 
delphinids and pinnipeds or 30 minutes have elapsed without re-
detection of the animal in the case of all other marine mammals.
    Prior to the start of pile driving activity, the EZs must be 
monitored for 60 minutes to ensure that they are clear of marine 
mammals. Pile driving may only commence once PSOs have declared the 
respective zones clear of marine mammals. Marine mammals observed 
within a EZ must be allowed to remain in the clearance zone (i.e., must 
leave of their own volition), and their behavior must be monitored and 
documented. The EZs may only be declared clear, and pile driving 
started, when the entire clearance zones are visible (i.e., when not 
obscured by dark, rain, fog, etc.) for a full 30 minutes prior to pile 
driving.

Soft Start

    The use of a soft start procedure is believed to provide additional 
protection to marine mammals by warning marine mammals or providing 
them with a chance to leave the area prior to the hammer operating at 
full capacity, and typically involves a requirement to initiate sound 
from the hammer at reduced energy followed by a waiting period. 
Dominion must utilize soft start techniques for impact pile driving by 
performing an initial set of three strikes from the impact hammer at a 
reduced energy level followed by a 30 second waiting period. The soft 
start process must be conducted a total of three times prior to driving 
each pile (e.g., three strikes followed by a 30 second delay, then 
three additional single strikes followed by a 30 second delay, then a 
final set of three strikes followed by an additional 30 second delay). 
Soft start is required at the beginning of each day's impact pile 
driving work and at any time following a cessation of impact pile 
driving of thirty minutes or longer.

Shutdown

    The purpose of a shutdown is to prevent some undesirable outcome, 
such as auditory injury or behavioral disturbance of sensitive species, 
by halting the activity. If a marine mammal is observed entering or 
within the EZs after pile driving has begun, PSOs must request a 
temporary cessation of pile driving. When called for by a PSO, shutdown 
of pile driving would be implemented when practicable; however, there 
may be instances where a shutdown is not practicable, as any 
significant stoppage of pile driving progress can allow for displaced 
sediments along the piling surface areas to consolidate and bind, 
potentially resulting in a situation where a piling is permanently 
bound in a partially driven position. If a shutdown is called for 
before a pile has been driven to a sufficient depth to allow for pile 
stability, then for safety reasons the pile would need to be driven to 
a sufficient depth to allow for stability and a shutdown would not be 
practicable until after that depth was reached. Therefore we require 
that shutdown be implemented when practicable.
    If shutdown is called for by a PSO, and Dominion determines a 
shutdown to be technically practicable, pile driving must be halted 
immediately. After shutdown, pile driving may be initiated once all EZs 
are clear of marine mammals for the minimum species-specific time 
periods, or, if required to maintain installation feasibility. For 
North Atlantic right whales, shutdown would occur when a right whale is 
observed by PSOs at any distance, and a shutdown zone of 1,750 m would 
be implemented for all other species (Table 8).

Noise Attenuation System

    The Project must utilize an attenuation system in order to reduce 
underwater noise from pile driving during the driving of at least one 
pile. Bubble curtains are used to reduce acoustic energy emissions from 
high-amplitude sources and are generated by releasing air through 
multiple small holes drilled in a hose or manifold deployed on the 
seabed near the source. The resulting curtain of air bubbles in the 
water attenuates sound waves propagating through the curtain. The sound 
attenuating effect of the noise mitigation system bubble curtain or air 
bubbles in water is caused by: (i) Sound

[[Page 30944]]

scattering on air bubbles (resonance effect) and (ii) (specular) 
reflection at the transition between water layer with and without 
bubbles (air water mixture; impedance leap). Use of a ``double bubble 
curtain'' entails two concentric rings of bubbles around the pile and 
can achieve greater levels of attenuation than the use of a single 
bubble curtain. A double bubble curtain would be deployed to reduce 
sound during pile driving activities during the driving of at least one 
pile.
    Dominion has proposed driving one pile with the double bubble 
curtain activated and the other pile without the double bubble curtain 
activated with the goal of gathering in situ data on the effectiveness 
of the double bubble curtain via hydroacoustic monitoring during the 
driving of both piles. This effort would be supported by the Bureau of 
Ocean Energy Management (BOEM) Real-time Opportunity for Development 
Environmental Observations (RODEO) program, which aims to collect real-
time measurements of the construction and operation activities from the 
first offshore wind facilities in the United States to allow for more 
accurate assessments of actual environmental effects and to inform 
development of appropriate mitigation measures. Dominion would activate 
the double bubble curtain on the pile that is expected to require more 
blows to complete.
    The bubble curtains would distribute air bubbles around 100 percent 
of the piling perimeter for the full depth of the water column. The 
lowest bubble ring would be in contact with the mudline for the full 
circumference of the ring, and the weights attached to the bottom ring 
would ensure 100 percent mudline contact. No parts of the ring or other 
objects would prevent full mudline contact. Air flow to the bubblers 
would be balanced around the circumference of the pile.

Visibility Requirements

    All pile driving must be initiated during daylight hours, no 
earlier than 30 minutes after sunrise and no later than four hours 
before sunset. Pile driving must not be initiated at night, or, when 
the full extent of the 1,750 m EZ cannot be confirmed to be clear of 
marine mammals, as determined by the lead PSO on duty. The EZ may only 
be declared clear, and pile driving initiated, when the full extent of 
the 1,750 m EZ is visible (i.e., when not obscured by dark, rain, fog, 
etc.) for a full 30 minutes prior to pile driving. Dominion must 
attempt to complete all pile driving in daylight; pile driving may 
continue after dark only when the installation of the same pile began 
during daylight at least four hours prior to sunset when the EZ was 
fully visible for at least 30 minutes, and only in extraordinary 
circumstances when it must proceed for human safety or installation 
feasibility reasons as determined by the lead engineer.

Monitoring Protocols

    Monitoring must be conducted before, during, and after pile driving 
activities. In addition, PSOs must record all incidents of marine 
mammal occurrence, regardless of distance from the construction 
activity, and PSOs must document any behavioral reactions in concert 
with distance from piles being driven. Observations made outside the EZ 
will not result in delay of pile driving; that pile segment may be 
completed without cessation, unless the marine mammal approaches or 
enters the EZ, at which point pile driving activities must be halted 
when practicable, as described above. Pile driving activities include 
the time to install a single pile, as long as the time elapsed between 
uses of the pile driving equipment is no more than 30 minutes.
    The following additional measures apply to visual monitoring:
    (1) A minimum of two PSOs must be on duty at all times during pile 
driving;
    (2) Monitoring must be conducted by qualified, trained PSOs. PSOs 
must be stationed at the highest practical vantage point on the pile 
installation vessel;
    (3) PSOs may not exceed four consecutive watch hours; must have a 
minimum two-hour break between watches; and may not exceed a combined 
watch schedule of more than 12 hours in a 24-hour period;
    (4) Monitoring must be conducted from 30 minutes prior to 
commencement of pile driving, throughout the time required to drive a 
pile, and for 30 minutes following the conclusion of pile driving;
    (5) PSOs must have no other construction-related tasks while 
conducting monitoring; and
    (6) PSOs must have the following minimum qualifications:
     Visual acuity in both eyes (correction is permissible) 
sufficient for discernment of moving targets at the water's surface 
with ability to estimate target size and distance; use of binoculars 
may be necessary to correctly identify the target;
     Ability to conduct field observations and collect data 
according to assigned protocols;
     Experience or training in the field identification of 
marine mammals, including the identification of behaviors;
     Sufficient training, orientation, or experience with the 
construction operation to provide for personal safety during 
observations;
     Writing skills sufficient to document observations 
including, but not limited to: The number and species of marine mammals 
observed; dates and times when in-water construction activities were 
conducted; dates and times when in-water construction activities were 
suspended to avoid potential incidental injury of marine mammals from 
construction noise within a defined shutdown zone; and marine mammal 
behavior; and
     Ability to communicate orally, by radio or in person, with 
project personnel to provide real-time information on marine mammals 
observed in the area as necessary.
    PSOs employed by Dominion in satisfaction of the mitigation and 
monitoring requirements described herein must meet the following 
additional requirements:
     Independent observers (i.e., not construction personnel) 
are required;
     At least one observer must have prior experience working 
as an observer;
     Other observers may substitute education (degree in 
biological science or related field) or training for experience;
     One observer will be designated as lead observer or 
monitoring coordinator. The lead observer must have prior experience 
working as an observer; and
     NMFS will require submission and approval of observer CVs.

Vessel Strike Avoidance

    Vessel strike avoidance measures include, but are not limited to, 
the following, except under circumstances when complying with these 
measures would put the safety of the vessel or crew at risk:
     All vessel operators and crew must maintain vigilant watch 
for cetaceans and pinnipeds, and slow down or stop their vessel to 
avoid striking these protected species;
     All vessels must travel at 10 knots (18.5 km/hr) or less 
within any designated Dynamic Management Area (DMA) or Seasonal 
Management Area for North Atlantic right whales;
     All vessel operators must reduce vessel speed to 10 knots 
(18.5 km/hr) or less when any large whale, any mother/calf pairs, pods, 
or large assemblages of non-delphinoid cetaceans are observed near 
(within 100 m (330 ft)) an underway vessel;
     All vessels must maintain a separation distance of 500 m 
(1640 ft) or

[[Page 30945]]

greater from any sighted North Atlantic right whale;
     If underway, vessels must steer a course away from any 
sighted North Atlantic right whale at 10 knots (18.5 km/hr) or less 
until the 500 m (1640 ft) minimum separation distance has been 
established. If a North Atlantic right whale is sighted in a vessel's 
path, or within 500 m (330 ft) to an underway vessel, the underway 
vessel must reduce speed and shift the engine to neutral. Engines will 
not be engaged until the right whale has moved outside of the vessel's 
path and beyond 500 m. If stationary, the vessel must not engage 
engines until the North Atlantic right whale has moved beyond 500 m;
     All vessels must maintain a separation distance of 100 m 
(330 ft) or greater from any sighted non-delphinoid cetacean. 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 
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 must maintain a separation distance of 50 m 
(164 ft) or greater from any sighted delphinoid cetacean, with the 
exception of delphinoid cetaceans that voluntarily approach the vessel 
(i.e., bow ride). Any vessel underway must remain parallel to a sighted 
delphinoid cetacean's course whenever possible, and avoid excessive 
speed or abrupt changes in direction. Any vessel underway must reduce 
vessel speed to 10 knots (18.5 km/hr) 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 the abeam of the underway 
vessel;
     All vessels must maintain a separation distance of 50 m 
(164 ft) or greater from any sighted pinniped; and
     All vessels underway must not divert or alter course in 
order to approach any whale, delphinoid cetacean, or pinniped. Any 
vessel underway will avoid excessive speed or abrupt changes in 
direction to avoid injury to the sighted cetacean or pinniped.
    Dominion must ensure that vessel operators and crew maintain a 
vigilant watch for marine mammals by slowing down or stopping the 
vessel to avoid striking marine mammals. Project-specific training must 
be conducted for all vessel crew prior to the start of the construction 
activities. Confirmation of the training and understanding of the 
requirements will be documented on a training course log sheet.
    The mitigation measures are designed to avoid the already low 
potential for injury in addition to some instances of Level B 
harassment, and to minimize the potential for vessel strikes. Further, 
we believe the mitigation measures are practicable for Dominion to 
implement. There are no known marine mammal rookeries or mating or 
calving grounds in the project area that would otherwise potentially 
warrant increased mitigation measures for marine mammals or their 
habitat (or both).
    Based on our evaluation of the required measures, as well as other 
measures considered by NMFS, NMFS has determined that the mitigation 
measures provide the means 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 
authorizations must include the suggested means of accomplishing the 
necessary monitoring and reporting that will result in increased 
knowledge of the species and of the level of taking or impacts on 
populations of marine mammals that are expected to be present in the 
proposed action area. Effective reporting is critical both to 
compliance as well as ensuring that the most value is obtained from the 
required monitoring.
    Monitoring and reporting requirements prescribed by NMFS should 
contribute to improved understanding of one or more of the following:
     Occurrence of marine mammal species or stocks in the area 
in which take is anticipated (e.g., presence, abundance, distribution, 
density);
     Nature, scope, or context of likely marine mammal exposure 
to potential stressors/impacts (individual or cumulative, acute or 
chronic), through better understanding of: (1) Action or environment 
(e.g., source characterization, propagation, ambient noise); (2) 
affected species (e.g., life history, dive patterns); (3) co-occurrence 
of marine mammal species with the action; or (4) biological or 
behavioral context of exposure (e.g., age, calving or feeding areas);
     Individual marine mammal responses (behavioral or 
physiological) to acoustic stressors (acute, chronic, or cumulative), 
other stressors, or cumulative impacts from multiple stressors;
     How anticipated responses to stressors impact either: (1) 
Long-term fitness and survival of individual marine mammals; or (2) 
populations, species, or stocks;
     Effects on marine mammal habitat (e.g., marine mammal prey 
species, acoustic habitat, or other important physical components of 
marine mammal habitat); and
     Mitigation and monitoring effectiveness.

Monitoring Measures

    Dominion must collect sighting data and behavioral responses to 
pile driving activity for marine mammal species observed in the region 
of activity during the period of activity. All observers must be 
trained in marine mammal identification and behaviors and are required 
to have no other construction-related tasks while conducting 
monitoring. PSOs must be stationed on the pile installation vessel. The 
observer platform would be elevated approximately 40-m above the sea 
surface. Dominion estimates that at this height a PSO with minimum 7x50 
binoculars would be able to monitor a first reticule distance of 
approximately 3.2 miles from the sound source. PSOs must monitor the EZ 
and the Level B harassment zone at all times and would document any 
marine mammals observed within these zones, to the extent practicable. 
PSOs must conduct monitoring before, during, and after pile driving and 
removal, with observers located at the best practicable vantage points.
    Dominion must implement the following monitoring procedures:
     A minimum of two PSOs must maintain watch at all times 
when pile driving is underway;
     PSOs must be located at the best possible vantage point(s) 
on the pile installation vessel to ensure that they are able to observe 
the entire EZ and as much of the monitoring zone as possible;
     During all observation periods, PSOs must use binoculars 
and the naked eye to search continuously for marine mammals;
     PSOs must be equipped with reticle binoculars and range 
finders as well as a digital single-lens reflex 35mm camera;
     Position data must be recorded using hand-held or vessel 
based global

[[Page 30946]]

positioning system (GPS) units for each sighting;
     If the EZ is obscured by fog or poor lighting conditions, 
pile driving must not be initiated until the EZ is fully visible. 
Should such conditions arise while pile driving is underway, the 
activity must be halted when practicable, as described above; and
     The EZ and monitoring zone must be monitored for the 
presence of marine mammals before, during, and after all pile driving 
activity.
    Individuals implementing the monitoring protocol will assess its 
effectiveness using an adaptive approach. PSOs will use their best 
professional judgment throughout implementation and seek improvements 
to these methods when deemed appropriate. Any modifications to the 
protocol will be coordinated between NMFS and Dominion.

Data Collection

    We require that observers use standardized data forms. Among other 
pieces of information, Dominion must record detailed information about 
any implementation of delays or shutdowns, including the distance of 
animals to the pile and a description of specific actions that ensued 
and resulting behavior of the animal, if any. We require that, at a 
minimum, the following information be collected on the sighting forms:
     Dates and times (begin and end) of all marine mammal 
monitoring;
     Construction activities occurring during each daily 
observation period, including how many and what type of piles were 
driven and by what method;
     Weather parameters and water conditions during each 
monitoring period (e.g., wind speed, percent cover, visibility, sea 
state);
     The number of marine mammals observed, by species, 
relative to the pile location and if pile driving or removal was 
occurring at time of sighting;
     Age and sex class, if possible, of all marine mammals 
observed;
     PSO locations during marine mammal monitoring;
     Distances and bearings of each marine mammal observed to 
the pile being driven or removed for each sighting (if pile driving or 
removal was occurring at time of sighting);
     Description of any marine mammal behavior patterns during 
observation, including direction of travel and estimated time spent 
within the Level A and Level B harassment zones while the source was 
active;
     Number of individuals of each species (differentiated by 
month as appropriate) detected within the monitoring zone, and 
estimates of number of marine mammals taken, by species (a correction 
factor may be applied to total take numbers, as appropriate);
     Detailed information about any implementation of any 
mitigation triggered (e.g., shutdowns and delays), a description of 
specific actions that ensued, and resulting behavior of the animal, if 
any;
     Description of attempts to distinguish between the number 
of individual animals taken and the number of incidences of take, such 
as ability to track groups or individuals;
     An extrapolation of the estimated takes by Level B 
harassment based on the number of observed exposures within the Level B 
harassment zone and the percentage of the Level B harassment zone that 
was not visible; and
     All PSO datasheets and/or raw sighting data must be 
submitted (in a separate file from the Final Report).
    Dominion must also note behavioral observations, to the extent 
practicable, if a marine mammal has remained in the area during 
construction activities.

Reporting

    A draft report must be submitted to NMFS within 90 days of the 
completion of monitoring for each installation's in-water work window. 
The report must include marine mammal observations pre-activity, 
during-activity, and post-activity during pile driving days, and would 
also provide descriptions of any behavioral responses to construction 
activities by marine mammals. The report must detail the monitoring 
protocol, summarize the data recorded during monitoring including an 
estimate of the number of marine mammals that may have been harassed 
during the period of the report, and describe any mitigation actions 
taken (i.e., delays or shutdowns due to detections of marine mammals, 
and documentation of when shutdowns were called for but not implemented 
and why). A final report must be submitted within 30 days following 
resolution of comments on the draft report.
    In the event that personnel involved in the construction activities 
discover an injured or dead marine mammal, the Dominion must report the 
incident to the Office of Protected Resources (OPR) (301-427-8401), 
NMFS and to the Mid-Atlantic regional stranding coordinator as soon as 
feasible. The report must include the following information:
     Time, date, and location (latitude/longitude) of the first 
discovery (and updated location information if known and applicable);
     Species identification (if known) or description of the 
animal(s) involved;
     Condition of the animal(s) (including carcass condition if 
the animal is dead);
     Observed behaviors of the animal(s), if alive;
     If available, photographs or video footage of the 
animal(s); and
     General circumstances under which the animal was 
discovered.

Negligible Impact Analysis and Determination

    NMFS has defined negligible impact as an impact resulting from the 
specified activity that cannot be reasonably expected to, and is not 
reasonably likely to, adversely affect the species or stock through 
effects on annual rates of recruitment or survival (50 CFR 216.103). A 
negligible impact finding is based on the lack of likely adverse 
effects on annual rates of recruitment or survival (i.e., population-
level effects). An estimate of the number of takes alone is not enough 
information on which to base an impact determination. In addition to 
considering estimates of the number of marine mammals that might be 
``taken'' through harassment, NMFS considers other factors, such as the 
likely nature of any responses (e.g., intensity, duration), the context 
of any responses (e.g., critical reproductive time or location, 
migration), as well as effects on habitat, and the likely effectiveness 
of the mitigation. We also assess the number, intensity, and context of 
estimated takes by evaluating this information relative to population 
status. Consistent with the 1989 preamble for NMFS's implementing 
regulations (54 FR 40338; September 29, 1989), the impacts from other 
past and ongoing anthropogenic activities are incorporated into this 
analysis via their impacts on the environmental baseline (e.g., as 
reflected in the regulatory status of the species, population size and 
growth rate where known, ongoing sources of human-caused mortality, or 
ambient noise levels).
    Pile driving activities associated with the planned project, as 
described previously, have the potential to disturb or temporarily 
displace marine mammals. Specifically, the specified activities may 
result in take, in the form of Level B harassment (potential behavioral 
disturbance) from underwater sounds generated from pile driving. 
Potential takes could occur if individual marine mammals are present in 
the ensonified zone when pile driving is occurring. To avoid 
repetition, the our analyses apply to all the species listed in Table 
1, given that

[[Page 30947]]

the anticipated effects of the planned project on different marine 
mammal species and stocks are expected to be similar in nature.
    Impact pile driving has source characteristics (short, sharp pulses 
with higher peak levels and sharper rise time to reach those peaks) 
that are potentially injurious or more likely to produce severe 
behavioral reactions. However, modeling indicates there is limited 
potential for auditory injury even in the absence of the mitigation 
measures, with no species predicted to experience Level A harassment. 
In addition, the already limited potential for injury is expected to be 
minimized through implementation of the mitigation measures including 
soft start and the implementation of EZs that would facilitate a delay 
of pile driving if marine mammals were observed approaching or within 
areas that could be ensonified above sound levels that could result in 
auditory injury. Given sufficient notice through use of soft start, 
marine mammals are expected to move away from a sound source that is 
annoying prior to its becoming potentially injurious or resulting in 
more severe behavioral reactions. No Level A harassment of any marine 
mammal stocks are anticipated or authorized.
    Repeated exposures of individuals to relatively low levels of sound 
outside of preferred habitat areas are unlikely to significantly 
disrupt critical behaviors. Thus, even repeated Level B harassment of 
some small subset of an overall stock is unlikely to result in any 
significant realized decrease in viability for the affected 
individuals, and thus would not result in any adverse impact to the 
stock as a whole. Instances of more severe behavioral harassment are 
expected to be minimized by mitigation and monitoring measures. Effects 
on individuals that are taken by Level B harassment, on the basis of 
reports in the literature as well as monitoring from other similar 
activities, will likely be limited to reactions such as increased 
swimming speeds, increased surfacing time, or decreased foraging (if 
such activity were occurring) (e.g., Thorson and Reyff, 2006; HDR, 
Inc., 2012; Lerma, 2014). Most likely, individuals will simply move 
away from the sound source and temporarily avoid the area where pile 
driving is occurring. Therefore, we expect that animals disturbed by 
project sound would simply avoid the area during pile driving in favor 
of other, similar habitats. We expect that any avoidance of the project 
area by marine mammals would be temporary in nature and that any marine 
mammals that avoid the project area during construction activities 
would not be permanently displaced.
    Feeding behavior is not likely to be significantly impacted, as 
prey species are mobile and are broadly distributed throughout the 
project area; therefore, marine mammals that may be temporarily 
displaced during construction 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. There are no areas of notable biological significance for 
marine mammal feeding known to exist in the project area, and there are 
no rookeries, mating areas, or calving areas known to be biologically 
important to marine mammals within the project area. The area is part 
of a biologically important migratory area for North Atlantic right 
whales; however, seasonal restrictions on pile driving activity, which 
would restrict pile driving to times of year when right whales are 
least likely to be migrating through the project area, would minimize 
the potential for the activity to impact right whale migration.
    NMFS concludes that exposures to marine mammals due to the project 
would result in only short-term effects to individuals exposed. Marine 
mammals may temporarily avoid the immediate area but are not expected 
to permanently abandon the area. Impacts to breeding, feeding, 
sheltering, resting, or migration are not expected, nor are shifts in 
habitat use, distribution, or foraging success. Serious injury or 
mortality as a result of the planned activities would not be expected 
even in the absence of the mitigation and monitoring measures, and no 
serious injury or mortality of any marine mammal stocks are anticipated 
or authorized. NMFS does not anticipate the marine mammal takes that 
would result from the planned project would impact annual rates of 
recruitment or survival.
    Gray and harbor seals are experiencing an ongoing unusual mortality 
event (UME). Although the ongoing UME is under investigation, the UME 
does not yet provide cause for concern regarding population-level 
impacts to any of these stocks. For harbor seals, the population 
abundance is over 75,000 and annual M/SI (345) is well below PBR 
(2,006) (Hayes et al., 2018). For gray seals, the population abundance 
is over 27,000, and abundance is likely increasing in the U.S. Atlantic 
EEZ and in Canada (Hayes et al., 2018). No injury, serious injury or 
mortality is expected or authorized, and Level B harassment of gray and 
harbor seals will be reduced to the level of least practicable adverse 
impact through implementation of mitigation measures. As such, the 
authorized takes of gray and harbor seals would not exacerbate or 
compound the ongoing UMEs in any way.
    In summary and as described above, the following factors primarily 
support our determination that the impacts resulting from this activity 
are not expected to adversely affect the species or stock through 
effects on annual rates of recruitment or survival:
     No Level A harassment, serious injury or mortality is 
anticipated or authorized;
     The anticipated impacts of the planned activity on marine 
mammals would be temporary behavioral changes due to avoidance of the 
project area;
     Total authorized takes as a percentage of population are 
low for all species and stocks (i.e., less than one percent of all 
stocks);
     The availability of alternate areas of similar habitat 
value for marine mammals to temporarily vacate the project area during 
the project to avoid exposure to sounds from the activity;
     Effects on species that serve as prey species for marine 
mammals from the project are expected to be short-term and are not 
expected to result in significant or long-term consequences for 
individual marine mammals, or to contribute to adverse impacts on their 
populations;
     There are no known important feeding, breeding, or calving 
areas in the project area, and authorized activities are limited to 
times of year when potential impacts to migration would not be 
expected; and
     Mitigation measures, including visual monitoring, 
exclusion and monitoring zones, a bubble curtain used on at least one 
pile, and soft start, are expected to minimize potential impacts to 
marine mammals.
    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.

[[Page 30948]]

Small Numbers

    As noted above, only small numbers of incidental take may be 
authorized under sections 101(a)(5)(A) and (D) of the MMPA for 
specified activities other than military readiness activities. The MMPA 
does not define small numbers and so, in practice, where estimated 
numbers are available, NMFS compares the number of individuals taken to 
the most appropriate estimation of abundance of the relevant species or 
stock in our determination of whether an authorization is limited to 
small numbers of marine mammals. When the predicted number of 
individuals to be taken is less than one third of the species or stock 
abundance, the take is considered to be of small numbers. Additionally, 
other qualitative factors may be considered in the analysis, such as 
the temporal or spatial scale of the activities.
    We authorize incidental take of seven marine mammal stocks. The 
total amount of taking authorized is less than one third of the best 
available population abundance estimate for all stocks (Table 7), which 
we find are small numbers of marine mammals relative to the estimated 
overall population abundances for those stocks.
    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 all affected species 
or stocks.

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.

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 evaluate our proposed action (i.e., the promulgation of 
regulations and subsequent issuance of incidental take authorization) 
and alternatives with respect to potential impacts on the human 
environment.
    This action is consistent with categories of activities identified 
in Categorical Exclusion B4 of the Companion Manual for NAO 216-6A, 
which do not individually or cumulatively have the potential for 
significant impacts on the quality of the human environment and for 
which we have not identified any extraordinary circumstances that would 
preclude this categorical exclusion. Accordingly, NMFS has determined 
that the proposed action qualifies to be categorically excluded from 
further NEPA review.

Endangered Species Act

    Section 7(a)(2) of the Endangered Species Act of 1973 (16 U.S.C. 
1531 et seq.) requires that each Federal agency insure that any action 
it authorizes, funds, or carries out is not likely to jeopardize the 
continued existence of any endangered or threatened species or result 
in the destruction or adverse modification of designated critical 
habitat. To ensure ESA compliance for the issuance of IHAs, NMFS 
consults internally whenever we propose to authorize take for 
endangered or threatened species. No incidental take of ESA-listed 
species is authorized or expected to result from this activity. 
Therefore, NMFS has determined that formal consultation under section 7 
of the ESA was not required for this action.

Authorization

    NMFS has issued an IHA to Dominion for conducting pile driving 
activity offshore of Virginia, for a period of one year, provided the 
previously mentioned mitigation, monitoring, and reporting requirements 
are incorporated.

Donna S. Wieting,
Director, Office of Protected Resources, National Marine Fisheries 
Service.
[FR Doc. 2020-10982 Filed 5-20-20; 8:45 am]
 BILLING CODE 3510-22-P