[Federal Register Volume 89, Number 93 (Monday, May 13, 2024)]
[Notices]
[Pages 41387-41391]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2024-10417]


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DEPARTMENT OF COMMERCE

National Oceanic and Atmospheric Administration

[RTID 0648-XD876]


Taking and Importing Marine Mammals; Taking Marine Mammals 
Incidental to Geophysical Surveys Related to Oil and Gas Activities in 
the Gulf of Mexico

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

[[Page 41388]]


ACTION: Notice of issuance of letter of authorization.

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SUMMARY: In accordance with the Marine Mammal Protection Act (MMPA), as 
amended, its implementing regulations, and NMFS' MMPA Regulations for 
Taking Marine Mammals Incidental to Geophysical Surveys Related to Oil 
and Gas Activities in the Gulf of Mexico (GOM), notification is hereby 
given that a Letter of Authorization (LOA) has been issued to Anadarko 
Petroleum Corporation (Anadarko) for the take of marine mammals 
incidental to geophysical survey activity in the GOM.

DATES: The LOA is effective from May 15, 2024, through November 15, 
2024.

ADDRESSES: The LOA, LOA request, and supporting documentation are 
available online at: https://www.fisheries.noaa.gov/action/incidental-take-authorization-oil-and-gas-industry-geophysical-survey-activity-gulf-mexico. In case of problems accessing these documents, please call 
the contact listed below (see FOR FURTHER INFORMATION CONTACT).

FOR FURTHER INFORMATION CONTACT: Rachel Wachtendonk, Office of 
Protected Resources, NMFS, (301) 427-8401.

SUPPLEMENTARY INFORMATION: 

Background

    Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.) 
direct the Secretary of Commerce to allow, upon request, the 
incidental, but not intentional, taking of small numbers of marine 
mammals by U.S. citizens who engage in a specified activity (other than 
commercial fishing) within a specified geographical region if certain 
findings are made and either regulations are issued or, if the taking 
is limited to harassment, a notice of a proposed authorization is 
provided to the public for review.
    An authorization for incidental takings shall be granted if NMFS 
finds that the taking will have a negligible impact on the species or 
stock(s), will not have an unmitigable adverse impact on the 
availability of the species or stock(s) for subsistence uses (where 
relevant), and if the permissible methods of taking and requirements 
pertaining to the mitigation, monitoring and reporting of such takings 
are set forth. NMFS has defined ``negligible impact'' in 50 CFR 216.103 
as an impact resulting from the specified activity that cannot be 
reasonably expected to, and is not reasonably likely to, adversely 
affect the species or stock through effects on annual rates of 
recruitment or survival.
    Except with respect to certain activities not pertinent here, the 
MMPA defines ``harassment'' as: any act of pursuit, torment, or 
annoyance which: (i) has the potential to injure a marine mammal or 
marine mammal stock in the wild (Level A harassment); or (ii) has the 
potential to disturb a marine mammal or marine mammal stock in the wild 
by causing disruption of behavioral patterns, including, but not 
limited to, migration, breathing, nursing, breeding, feeding, or 
sheltering (Level B harassment).
    On January 19, 2021, we issued a final rule with regulations to 
govern the unintentional taking of marine mammals incidental to 
geophysical survey activities conducted by oil and gas industry 
operators, and those persons authorized to conduct activities on their 
behalf (collectively ``industry operators''), in U.S. waters of the GOM 
over the course of 5 years (86 FR 5322, January 19, 2021). The rule was 
based on our findings that the total taking from the specified 
activities over the 5-year period will have a negligible impact on the 
affected species or stock(s) of marine mammals and will not have an 
unmitigable adverse impact on the availability of those species or 
stocks for subsistence uses. The rule became effective on April 19, 
2021.
    Our regulations at 50 CFR 217.180 allow for the issuance of LOAs to 
industry operators for the incidental take of marine mammals during 
geophysical survey activities and prescribe the permissible methods of 
taking and other means of effecting the least practicable adverse 
impact on marine mammal species or stocks and their habitat (often 
referred to as mitigation), as well as requirements pertaining to the 
monitoring and reporting of such taking. Under 50 CFR 217.186(e), 
issuance of an LOA shall be based on a determination that the level of 
taking will be consistent with the findings made for the total taking 
allowable under these regulations and a determination that the amount 
of take authorized under the LOA is of no more than small numbers.

Summary of Request and Analysis

    Anadarko plans to conduct a zero offset vertical seismic profile 
(VSP) within Mississippi Canyon Block MC-216. The survey area has water 
depths of approximately 1,875 meters (m). Anadarko plans to use either 
a 12-element, 2,400 cubic inch (in\3\) airgun array, or a 6-element, 
1,500 in\3\ airgun array. The survey is planned to occur for up to 3 
days in May 2024. Please see Anadarko's application for additional 
detail.
    Consistent with the preamble to the final rule, the survey effort 
proposed by Anadarko in its LOA request was used to develop LOA-
specific take estimates based on the acoustic exposure modeling results 
described in the preamble (86 FR 5322, January 19, 2021). In order to 
generate the appropriate take number for authorization, the following 
information was considered: (1) survey type; (2) location (by modeling 
zone \1\); (3) number of days; and (4) season.\2\ The acoustic exposure 
modeling performed in support of the rule provides 24-hour exposure 
estimates for each species, specific to each modeled survey type in 
each zone and season.
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    \1\ For purposes of acoustic exposure modeling, the GOM was 
divided into seven zones. Zone 1 is not included in the geographic 
scope of the rule.
    \2\ For purposes of acoustic exposure modeling, seasons include 
winter (December-March) and summer (April-November).
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    No VSP surveys were included in the modeled survey types, and use 
of existing proxies (i.e., two-dimensional (2D), three-dimensional 
narrow azimuth (3D NAZ), 3D wide-azimuth (WAZ), Coil) is generally 
conservative for use in evaluation of VSP survey effort. Summary 
descriptions of these modeled survey geometries are available in the 
preamble to the proposed rule (83 FR 29212, June 22, 2018). Coil was 
selected as the best available proxy survey type because the spatial 
coverage of the planned survey is most similar to that associated with 
the coil survey pattern.
    For the planned survey, the seismic source array will be deployed 
from a drilling rig at or near the borehole, with the seismic receivers 
(i.e., geophones) deployed in the borehole on wireline at specified 
depth intervals. The coil survey pattern in the model was assumed to 
cover approximately 144 kilometers squared (km\2\) per day (compared 
with approximately 795 km\2\, 199 km\2\, and 845 km\2\ per day for the 
2D, 3D NAZ, and 3D WAZ survey patterns, respectively). Among the 
different parameters of the modeled survey patterns (e.g., area 
covered, line spacing, number of sources, shot interval, total 
simulated pulses), NMFS considers area covered per day to be most 
influential on daily modeled exposures exceeding Level B harassment 
criteria. Because Anadarko's planned survey is expected to cover no 
additional area as a stationary source, the coil proxy is most 
representative of the effort planned by Anadarko in terms of predicted 
Level B harassment.
    In addition, all available acoustic exposure modeling results 
assume use of a 72-element, 8,000 in\3\ array. Thus, estimated take 
numbers for this LOA are

[[Page 41389]]

considered conservative due to the differences in both the airgun array 
(maximum of 12 elements and 2,400 in\3\), and in daily survey area 
planned by Anadarko (as mentioned above), as compared to those modeled 
for the rule.
    The survey is planned to occur in zone 5 during summer.
    For some species, take estimates based solely on the modeling 
yielded results that are not realistically likely to occur when 
considered in light of other relevant information available during the 
rulemaking process regarding marine mammal occurrence in the GOM. The 
approach used in the acoustic exposure modeling, in which seven 
modeling zones were defined over the U.S. GOM, necessarily averages 
fine-scale information about marine mammal distribution over the large 
area of each modeling zone. This can result in unrealistic projections 
regarding the likelihood of encountering particularly rare species and/
or species not expected to occur outside particular habitats. Thus, 
although the modeling conducted for the rule is a natural starting 
point for estimating take, our rule acknowledged that other information 
could be considered (see, e.g., 86 FR 5322, January 19, 2021, 
discussing the need to provide flexibility and make efficient use of 
previous public and agency review of other information and identifying 
that additional public review is not necessary unless the model or 
inputs used differ substantively from those that were previously 
reviewed by NMFS and the public). For this survey, NMFS has other 
relevant information reviewed during the rulemaking that indicates use 
of the acoustic exposure modeling to generate a take estimate for 
Rice's whales and killer whales produces results inconsistent with what 
is known regarding their occurrence in the GOM. Accordingly, we have 
adjusted the calculated take estimates for those species as described 
below.
    NMFS' final rule described a ``core habitat area'' for Rice's 
whales (formerly known as GOM Bryde's whales) \3\ located in the 
northeastern GOM in waters between 100 and 400[thinsp]m depth along the 
continental shelf break (Rosel et al., 2016). However, whaling records 
suggest that Rice's whales historically had a broader distribution 
within similar habitat parameters throughout the GOM (Reeves et al., 
2011; Rosel and Wilcox, 2014). In addition, habitat-based density 
modeling has identified similar habitat (i.e., approximately 100-400 m 
water depths along the continental shelf break) as being potential 
Rice's whale habitat (Roberts et al., 2016; Garrison et al., 2023), and 
Rice's whales have been detected within this depth band throughout the 
GOM (Soldevilla et al., 2022, 2024). See discussion provided at, e.g., 
83 FR 29228, June 22, 2018; 83 FR 29280, June 22, 2018; 86 FR 5418, 
January 19, 2021.
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    \3\ The final rule refers to the GOM Bryde's whale (Balaenoptera 
edeni). These whales were subsequently described as a new species, 
Rice's whale (Balaenoptera ricei) (Rosel et al., 2021).
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    Although Rice's whales may occur outside of the core habitat area, 
we expect that any such occurrence would be limited to the narrow band 
of suitable habitat described above (i.e., 100-400 m) and that, based 
on the few available records, these occurrences would be rare. 
Anadarko's planned activities will occur in water depths of 
approximately 1,875 m in the central GOM. Thus, NMFS does not expect 
there to be the reasonable potential for take of Rice's whale in 
association with this survey and, accordingly, does not authorize take 
of Rice's whale through the LOA.
    Killer whales are the most rarely encountered species in the GOM, 
typically in deep waters of the central GOM (Roberts et al., 2015; 
Maze-Foley and Mullin, 2006). As discussed in the final rule, the 
density models produced by Roberts et al. (2016) represent the output 
of models derived from multi-year observations and associated 
environmental parameters that incorporate corrections for detection 
bias. However, in the case of killer whales, the model is informed by 
few data, as indicated by the coefficient of variation associated with 
the abundance predicted by the model (0.41, the second-highest of any 
GOM species model; Roberts et al., 2016). The model's authors noted the 
expected non-uniform distribution of this rarely-encountered species 
(as discussed above) and expressed that, due to the limited data 
available to inform the model, it ``should be viewed cautiously'' 
(Roberts et al., 2015).
    NOAA surveys in the GOM from 1992 to 2009 reported only 16 
sightings of killer whales, with an additional 3 encounters during more 
recent survey effort from 2017 to 2018 (Waring et al., 2013; https://www.boem.gov/gommapps). Two other species were also observed on fewer 
than 20 occasions during the 1992-2009 NOAA surveys (Fraser's dolphin 
and false killer whale).\4\ However, observational data collected by 
protected species observers (PSOs) on industry geophysical survey 
vessels from 2002 to 2015 distinguish the killer whale in terms of 
rarity. During this period, killer whales were encountered on only 10 
occasions, whereas the next most rarely encountered species (Fraser's 
dolphin) was recorded on 69 occasions (Barkaszi and Kelly, 2019). The 
false killer whale and pygmy killer whale were the next most rarely 
encountered species, with 110 records each. The killer whale was the 
species with the lowest detection frequency during each period over 
which PSO data were synthesized (2002-2008 and 2009-2015). This 
information qualitatively informed our rulemaking process, as discussed 
at 86 FR 5322 and 86 FR 5334 (January 19, 2021), and similarly informs 
our analysis here.
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    \4\ However, note that these species have been observed over a 
greater range of water depths in the GOM than have killer whales.
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    The rarity of encounter during seismic surveys is not likely to be 
the product of high bias on the probability of detection. Unlike 
certain cryptic species with high detection bias, such as Kogia spp. or 
beaked whales, or deep-diving species with high availability bias, such 
as beaked whales or sperm whales, killer whales are typically available 
for detection when present and are easily observed. Roberts et al. 
(2015) stated that availability is not a major factor affecting 
detectability of killer whales from shipboard surveys, as they are not 
a particularly long-diving species. Baird et al. (2005) reported that 
mean dive durations for 41 fish-eating killer whales for dives greater 
than or equal to 1 minute in duration was 2.3-2.4 minutes, and Hooker 
et al. (2012) reported that killer whales spent 78 percent of their 
time at depths between 0 and 10 m. Similarly, Kvadsheim et al. (2012) 
reported data from a study of 4 killer whales, noting that the whales 
performed 20 times as many dives 1-30 m in depth than to deeper waters, 
with an average depth during those most common dives of approximately 3 
m.
    In summary, killer whales are the most rarely encountered species 
in the GOM and typically occur only in particularly deep water. This 
survey would take place in deep waters that would overlap with depths 
in which killer whales typically occur. While this information is 
reflected through the density model informing the acoustic exposure 
modeling results, there is relatively high uncertainty associated with 
the model for this species, and the acoustic exposure modeling applies 
mean distribution data over areas where the species is in fact less 
likely to occur. In addition, as noted above in relation to the general 
take estimation methodology, the assumed proxy source (72-element, 
8,000-in\3\ array) results in a significant overestimate of the actual

[[Page 41390]]

potential for take to occur. NMFS' determination in reflection of the 
information discussed above, which informed the final rule, is that use 
of the generic acoustic exposure modeling results for killer whales 
will generally result in estimated take numbers that are inconsistent 
with the assumptions made in the rule regarding expected killer whale 
take (86 FR 5322, January 19, 2021; 86 FR 5403, January 19, 2021). In 
this case, use of the acoustic exposure modeling produces an estimate 
of one killer whale exposure. Given the foregoing, it is unlikely that 
any killer whales would be encountered during this at most 3-day 
survey, and accordingly no take of killer whales is authorized through 
this LOA.
    In addition, in this case, use of the exposure modeling produces 
results that are smaller than average GOM group sizes for one species 
(Maze-Foley and Mullin, 2006). NMFS' typical practice in such a 
situation is to increase exposure estimates to the assumed average 
group size for a species in order to ensure that, if the species is 
encountered, exposures will not exceed the authorized take number. 
However, other relevant considerations here lead to a determination 
that increasing the estimated exposures to the average group size would 
likely lead to an overestimate of actual potential take. In this 
circumstance, the very short survey duration (maximum of 3 days) and 
relatively small Level B harassment isopleths produced through use of 
the (at most) 12-element, 2,400-in\3\ airgun array (compared with the 
modeled 72-element, 8,000 in\3\ array) mean that it is unlikely that 
certain species would be encountered at all, much less that the 
encounter would result in exposure of a greater number of individuals 
than is estimated through use of the exposure modeling results. As a 
result, in this case NMFS has not increased the estimated exposure 
values to assumed average group size in authorizing take.
    Based on the results of our analysis, NMFS has determined that the 
level of taking expected for this survey and authorized through the LOA 
is consistent with the findings made for the total taking allowable 
under the regulations for the affected species or stocks of marine 
mammals. See table 1 in this notice and table 9 of the rule (86 FR 
5322, January 19, 2021).

Small Numbers Determination

    Under the GOM rule, NMFS may not authorize incidental take of 
marine mammals in an LOA if it will exceed ``small numbers.'' In short, 
when an acceptable estimate of the individual marine mammals taken is 
available, if the estimated number of individual animals taken is up 
to, but not greater than, one-third of the best available abundance 
estimate, NMFS will determine that the numbers of marine mammals taken 
of a species or stock are small. For more information please see NMFS' 
discussion of the MMPA's small numbers requirement provided in the 
final rule (86 FR 5322, January 19, 2021; 86 FR 5438, January 19, 
2021).
    The take numbers for authorization, which are determined as 
described above, are used by NMFS in making the necessary small numbers 
determinations through comparison with the best available abundance 
estimates (see discussion at 86 FR 5322, January 19, 2021 and 86 FR 
5391, January 19, 2021). For this comparison, NMFS' approach is to use 
the maximum theoretical population, determined through review of 
current stock assessment reports (SAR; https://www.fisheries.noaa.gov/national/marine-mammal-protection/marine-mammal-stock-assessments) and 
model-predicted abundance information (https://seamap.env.duke.edu/models/Duke/GOM). For the latter, for taxa where a density surface 
model could be produced, we use the maximum mean seasonal (i.e., 3-
month) abundance prediction for purposes of comparison as a 
precautionary smoothing of month-to-month fluctuations and in 
consideration of a corresponding lack of data in the literature 
regarding seasonal distribution of marine mammals in the GOM. 
Information supporting the small numbers determinations is provided in 
table 1.

                                             Table 1--Take Analysis
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                                                                    Authorized                        Percent
                             Species                                 take \a\      Abundance \b\     abundance
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Rice's whale....................................................               0              51             n/a
Sperm whale.....................................................              79           2,207             3.6
Kogia spp.......................................................          \c\ 29           4,373             0.7
Beaked whales...................................................             338           3,768             9.0
Rough-toothed dolphin...........................................              58           4,853             1.2
Bottlenose dolphin..............................................             267         176,108             0.2
Clymene dolphin.................................................             160          11,895             1.3
Atlantic spotted dolphin........................................             110          74,785             0.1
Pantropical spotted dolphin.....................................             726         102,361             0.7
Spinner dolphin.................................................             195          25,114             0.8
Striped dolphin.................................................              62           5,229             1.2
Fraser's dolphin................................................          \d\ 19           1,665             1.1
Risso's dolphin.................................................              47           3,764             1.2
Melon-headed whale..............................................             109           7,003             1.6
Pygmy killer whale..............................................              25           2,126             1.2
False killer whale..............................................              40           3,204             1.3
Killer whale....................................................               0             267             n/a
Short-finned pilot whale........................................              32           1,981             1.6
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\a\ Scalar ratios were not applied in this case due to brief survey duration.
\b\ Best abundance estimate. For most taxa, the best abundance estimate for purposes of comparison with take
  estimates is considered here to be the model-predicted abundance (Roberts et al., 2016). For those taxa where
  a density surface model predicting abundance by month was produced, the maximum mean seasonal abundance was
  used. For those taxa where abundance is not predicted by month, only mean annual abundance is available. For
  Rice's whale and killer whale, the larger estimated SAR abundance estimate is used.
\c\ Includes 2 takes by Level A harassment and 27 takes by Level B harassment.
\d\ Modeled exposure estimate less than assumed average group size (Maze-Foley and Mullin, 2006).


[[Page 41391]]

    Based on the analysis contained herein of Anadarko's proposed 
survey activity described in its LOA application and the anticipated 
take of marine mammals, NMFS finds that small numbers of marine mammals 
will be taken relative to the affected species or stock sizes (i.e., 
less than one-third of the best available abundance estimate) and 
therefore the taking is of no more than small numbers.

Authorization

    NMFS has determined that the level of taking for this LOA request 
is consistent with the findings made for the total taking allowable 
under the incidental take regulations and that the amount of take 
authorized under the LOA is of no more than small numbers. Accordingly, 
we have issued an LOA to Anadarko authorizing the take of marine 
mammals incidental to its geophysical survey activity, as described 
above.

    Dated: May 6, 2024
Kimberly Damon-Randall,
Director, Office of Protected Resources, National Marine Fisheries 
Service.
[FR Doc. 2024-10417 Filed 5-10-24; 8:45 am]
 BILLING CODE 3510-22-P