Taking and Importing Marine Mammals; Taking Marine Mammals Incidental to Geophysical Surveys Related to Oil and Gas Activities in the Gulf of America
In accordance with the Marine Mammal Protection Act (MMPA), as amended, its implementing regulations, and NMFS' MMPA regulations for taking marine mammals incidental to geophysi...
National Marine Fisheries Service (NMFS), National Oceanic and Atmospheric Administration (NOAA), Commerce.
ACTION:
Notice; issuance of Letters of Authorization.
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 America (GOA), notification is hereby given that NMFS has issued six separate Letters of Authorization (LOAs) to WesternGeco, LLC (WesternGeco), TGS, Future Energy Consultants (FEC), bp Exploration & Production Inc. (bp), Viridien, and LLOG Exploration Offshore, L.L.C. (LLOG), for the take of marine mammals incidental to geophysical survey activity in the GOA.
DATES:
The LOA issued to WesternGeco is effective from April 20, 2026, through August 31, 2026. The LOA issued to TGS is effective from April 20, 2026, through May 31, 2026. The LOA issued to FEC is effective from June 1, 2026, through December 31, 2026. The LOA issued to bp is effective from May 1, 2026, through August 31, 2026. The LOA issued to Viridien is effective from June 1, 2026, through May 31, 2027. The LOA issued to LLOG is effective from June 1, 2026, through April 19, 2031.
Jenna Harlacher, 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. 1361et 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
( printed page 24810)
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 GOA [1]
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, and became effective on April 19, 2021.
The 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.
NMFS subsequently discovered that the 2021 rule was based on erroneous take estimates. We conducted another rulemaking using correct take estimates and other newly available and pertinent information relevant to the analyses supporting some of the findings in the 2021 final rule and the taking allowable under the regulations. We issued a final rule in April 2024, effective May 24, 2024 (89 FR 31488, April 24, 2024).
On August 28, 2025, NMFS Office of Protected Resources (OPR) received a request from NMFS Office of Policy (Policy) for reimplementation of the current Incidental Take Regulation (ITR) to avoid a lapse in ITRs offering incidental take coverage for GOA geophysical survey activities. On October 20, 2025, Bureau of Ocean Energy Management (the original petitioner for the current ITRs) submitted a request to be included in the process as a co-petitioner. In response to these requests, NMFS issued a new final rule, effective April 20, 2026, through April 19, 2031 (91 FR 20784, April 17, 2026).
The reimplementation of the regulations continues the established framework for authorization of incidental take through LOAs. The final rule made no changes to the specified activities or the specified geographical region in which those activities would be conducted, and there are no changes to the associated mitigation, monitoring, and reporting requirements.
Summary of Requests and Analysis
WesternGeco
On December 3, 2025, NMFS previously issued a LOA to WesternGeco under the 2021 ITR (90 FR 56734, December 8, 2025) to take marine mammals incidental to a planned geophysical survey. WesternGeco's survey was not completed by the expiration of the 2021 ITR and required issuance of a new LOA to cover survey activity through August 31, 2026. WesternGeco plans to conduct a three-dimensional (3D) ocean bottom node (OBN) survey over 200 lease blocks in the Green Canyon and Walker Ridge areas, with water depths ranging from approximately 1,400 to 3,200 meters (m). WesternGeco will use one of the following source configurations: a conventional airgun array source consisting of 28 elements with a total volume of 5,000 cubic inches (in3
) or a combination of the conventional airgun array source and a low-frequency tuned pulse source (TPS). The TPS was not included in the acoustic exposure modeling used for the rule. However, NMFS previously reviewed these sources as “new and unusual technologies” and determined that use of TPS is not expected to cause effects beyond those considered in the rulemaking, and that use of modeling results from a traditional airgun array as a proxy for take that may occur incidental to use of the TPS is conservative. Please see WesternGeco's application and original notice of issuance (90 FR 56734, December 8, 2025) for additional details.
The current LOA will cover 92 days of sound source operation, with 11 days planned in Zone 5 and 81 days planned in Zone 7. The monthly distribution of survey days is not known in advance, though we assume that the planned 92 days of source operation would occur contiguously. Take estimates for each species are based on the time period that produces the greatest value and have been updated based on the revised survey plan. There are no other changes to the previously planned survey.
TGS
On December 20, 2024, NMFS issued a LOA to TGS (89 FR 105536, December 27, 2024) to take marine mammals incidental to a planned geophysical survey, effective December 20, 2024, through December 19, 2025. Please see the
Federal Register
notice of issuance for additional detail regarding the LOA and the survey activity.
On July 22, 2025, TGS informed NMFS that its planned survey area and timing had shifted and, accordingly, they requested a modification to the LOA to reflect the new survey area and dates. No survey activity had begun. TGS requested the expiration date be extended to April 19, 2026, and increase the survey to 105 total days of sound source operation in Zone 6. On August 19, 2025, NMFS issued a modified LOA to TGS (90 FR 41060; August 22, 2025).
On November 26, 2025, TGS notified NMFS that the survey area had changed again based on market interest. TGS requested an increase of survey days to 140 total days of sound source operation with 139 days in zone 6 and 1 day in zone 7. On December 29, 2025, NMFS issued a second modified LOA (90 FR 60651) to reflect another change to the survey area. There were no other changes to the planned survey.
TGS' survey was not completed by the expiration of the 2021 ITR and required
( printed page 24811)
issuance of a new LOA to cover survey activity through May 31, 2026.
TGS plans to conduct a 3D OBN survey over 453 lease blocks in the East Breaks area, with water depths ranging from approximately 1,200 to 2,000 m. TGS anticipates using two source vessels with a low-frequency airgun source known as Gemini (also referred to as a dual barbell source). The Gemini source was not included in the acoustic exposure modeling used for the rule. However, NMFS previously reviewed these sources as “new and unusual technologies” and determined that it is not expected to cause effects beyond those considered in the rulemaking, and that use of modeling results from a traditional airgun array as a proxy for take that may occur incidental to use of the Gemini is conservative. Please see TGS's application and original notice for additional details (89 FR 105536, December 27, 2024).
The current LOA will cover 18 days of sound source operation in Zone 6. The monthly distribution of survey days is not known in advance, though we assume that the planned 18 days of source operation would occur contiguously. Take estimates for each species are based on the time period that produces the greatest value and have been updated based on the revised survey plan. There are no other changes to the previously planned survey.
FEC
FEC plans to conduct a FloatSeis seismic field trial survey in the lease block LA5A, with water depths ranging from approximately 50-180 m. See section F of the LOA application for a map of the area. FEC plans to use both a 2,450 in3
airgun array, and a 220 in3
airgun array. Please see the LOA application for additional details.
Consistent with the preamble to the final rule, the survey effort proposed by FEC in its LOA request was used to develop LOA-specific take estimates based on the acoustic exposure modeling results described in the preamble (91 FR 20784, April 17, 2026). In order to generate the appropriate take number for authorization, the following information was considered: (1) survey type; (2) location (by modeling zone i
); (3) number of days; (4) source; and (5) month.ii
The acoustic exposure modeling performed in support of the rule provides 24-hour exposure estimates for each species, specific to each modeled source and survey type in each zone and month.
FEC's survey type was not included in the modeled survey types, and use of existing proxies (
i.e.,
two-dimensional (2D), 3D narrow-azimuth (NAZ), 3D wide-azimuth (WAZ), Coil) is generally conservative for use in evaluation of both types of survey efforts (
i.e.,
survey effort using the 2,450 in3
and 220 in3
airgun arrays), largely due to the greater area covered by the modeled proxies. Summary descriptions of these modeled survey geometries are available in the preamble to the proposed rule (91 FR 9014, 9018, February 24, 2026). For the survey effort using the 2,450 in3
airgun array, the 4,130 in3
airgun array was selected as the best proxy and coil was selected as the best available proxy survey type in this case because the spatial coverage of the planned survey is most similar to the coil survey pattern.
For the survey effort using the 220 in3
airgun array, the above proxies are conservative, therefore the exposure modeling results were generated using the single airgun proxy. Because these results assume use of a 90-in3
airgun, the take numbers authorized for this part of the survey activity are considered the most similar to the 220 in3
sound source planned for use by FEC, as compared to the other proxies modeled for the rule.
The survey will take place over approximately 5 days, all within Zone 2. The monthly distribution of survey days is not known in advance, though we assume that the planned 5 days of source operation would occur contiguously. Take estimates for each species are based on the time period that produces the greatest value.
bp
Bp plans to conduct a 3D OBN and distributed acoustic sensing (DAS) survey in the Garden Banks and Walker Ridge areas, with water depths ranging from approximately 700 to 2,400 m. See section F of the LOA application for a map of the area. Bp anticipates using a single source vessel towing a triple source airgun array. Each source would have a maximum of 28 elements, and total volume up to 5,110 in3
. Please see the LOA application for additional details.
Consistent with the preamble to the final rule, the survey effort proposed by bp in its LOA request was used to develop LOA-specific take estimates based on the acoustic exposure modeling results described in the preamble (91 FR 20784, April 17, 2026). In order to generate the appropriate take number for authorization, the following information was considered: (1) survey type; (2) location (by modeling zone i
); (3) number of days; (4) source; and (5) month.ii
In this case, because bp plans to use up to a 5,110 in3
airgun array, the 5,110 in3
airgun array proxy was selected. The acoustic exposure modeling performed in support of the rule provides 24-hour exposure estimates for each species, specific to each modeled source and survey type in each zone and month.
No 3D OBN or DAS surveys were included in the modeled survey types, and use of existing proxies (
i.e.,
2D, 3D NAZ, 3D WAZ, Coil) is generally conservative for use in evaluation of 3D OBN or DAS survey effort, largely due to the greater area covered by the modeled proxies. Summary descriptions of these modeled survey geometries are available in the preamble to the proposed rule (91 FR 9014, 9018, February 24, 2026). Coil was selected as the best available proxy survey type in this case because the spatial coverage of the planned survey is most similar to the coil survey pattern. The planned survey will involve a single source vessel, with total survey area coverage of approximately 2,321 kilometers squared (km2
), similar to that assumed for the coil survey proxy of 3,364 km2
. 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. Although bp is not proposing to perform a survey using the coil geometry, the coil proxy is most representative of the effort planned by bp in terms of predicted Level B harassment exposures.
The survey is estimated to include 106 days of sound source operation, with 69 days planned in Zone 5 and 37 days planned in Zone 7. The monthly distribution of survey days is not known in advance, though we assume that the planned 106 days of source operation would occur contiguously. Take estimates for each species are based on the time period that produces the greatest value.
For the Rice's whale, take estimates based on the modeling yielded results that are not realistically likely to occur when considered in light of other relevant information concerning Rice's whale habitat preferences considered during the rulemaking process. NMFS' 2026 proposed rule provided detailed discussion regarding Rice's whale habitat (see,
e.g.,91 FR 9014, 9026, February 24, 2026). In summary, recent survey data, sightings, and acoustic data support Rice's whale occurrence in waters throughout the GOA between approximately 100 m and 400 m depth along the continental shelf break, and associated habitat-based density modeling has identified similar habitat
( printed page 24812)
(
i.e.,
approximately 100 to 400 m water depths along the continental shelf break) as being Rice's whale habitat (Garrison
et al.,
2023; Soldevilla
et al.,
2022, 2024).
Although Rice's whales may occur outside of the general depth range expected to provide suitable habitat, we expect that any such occurrence would be rare. Bp's planned activities will occur in water depths of approximately 1,400 to 3,200 m in the central GOA. Thus, NMFS does not expect that take of Rice's whale is likely in association with this survey and, accordingly, does not authorize take of Rice's whale through the LOA.
Viridien
Viridien plans to conduct a long offset sparse OBN survey over 1,061 lease blocks in the Central GOA, with water depths ranging from approximately 600 to 1,500 m. See section F of the LOA application for a map of the area.
Viridien anticipates using two dual-source vessels and would preferentially use the low-frequency TPS. Alternatively, Viridien may use a conventional airgun array source consisting of 42 elements with a total volume of 5,220 in3
. Please see Viridien's application for additional details.
The TPS was not included in the acoustic exposure modeling developed in support of the rule. However, the TPS was previously described and evaluated in support of previous LOAs and we rely on those analyses here (86 FR 37309, 37310, July 15, 2021; 87 FR 55790, 55791, September 12, 2022). For additional details regarding sources, see section C of the LOA application. Based on this information we have determined there will be no effects of a magnitude or intensity different from those evaluated in support of the rule. NMFS therefore expects that use of modeling results supporting the final rule relating to use of airgun arrays is expected to be conservative as a proxy for use in evaluating potential impacts of use of the TPS.
Consistent with the preamble to the final rule, the survey effort proposed by Viridien in its LOA request was used to develop LOA-specific take estimates based on the acoustic exposure modeling results described in the preamble (91 FR 20784, April 17, 2026). In order to generate the appropriate take number for authorization, the following information was considered: (1) survey type; (2) location (by modeling zone i
); (3) number of days; (4) source; and (5) month.ii
To determine the most appropriate proxy array from the exposure modeling, the directionally dependent source level in a plane parallel to the sea surface was compared to the three airgun array sources which were originally modeled, including the 4,130, 5,110, and 8,000 in3
arrays. Out of these three proxies, the source which had the smallest relative error (arithmetic mean difference taken over the azimuthal or vessel bearing angle) was chosen as the most representative proxy. In this case, the 5,110 in3
had the lowest mean error (0.3 dB) and was the airgun array proxy that was selected. In this case, because Viridien may also elect to use the specified 42-element, 5,220 in3
airgun array source, this was used to determine the appropriate proxy. The acoustic exposure modeling performed in support of the rule provides 24-hour exposure estimates for each species, specific to each modeled source and survey type in each zone and month.
No OBN surveys were included in the modeled survey types, and use of existing proxies (
i.e.,
2D, 3D NAZ, 3D WAZ, Coil) is generally conservative for use in evaluation of 3D OBN survey effort, largely due to the greater area covered by the modeled proxies. Summary descriptions of these modeled survey geometries are available in the preamble to the proposed rule (91 FR 9014, 9018, February 24, 2026). Coil was selected as the best available proxy survey type in this case because the spatial coverage of the planned survey is most similar to the coil survey pattern. The planned OBN survey will involve two source vessels sailing along closely spaced survey lines, with daily survey area coverage of approximately 144 km2
per day, similar to that assumed for the coil survey proxy. 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. Although Viridien is not proposing to perform a survey using the coil geometry, the coil proxy is most representative of the effort planned by Viridien in terms of predicted Level B harassment exposures.
The survey will take place over approximately 115 days with 65 days of sound source operation, including 55 days in Zone 6 and 10 days in Zone 7. The monthly distribution of survey days is not known in advance, though we assume that the planned 65 days of source operation would occur contiguously. Take estimates for each species are based on the time period that produces the greatest value.
For the Rice's whale, take estimates based on the modeling yielded results that are not realistically likely to occur when considered in light of other relevant information concerning Rice's whale habitat preferences considered during the rulemaking process. NMFS' 2026 proposed rule provided detailed discussion regarding Rice's whale habitat (see,
e.g.,91 FR 9014, 9026, February 24, 2026). In summary, recent survey data, sightings, and acoustic data support Rice's whale occurrence in waters throughout the GOA between approximately 100 m and 400 m depth along the continental shelf break, and associated habitat-based density modeling has identified similar habitat (
i.e.,
approximately 100 to 400 m water depths along the continental shelf break) as being Rice's whale habitat (Garrison
et al.,
2023; Soldevilla
et al.,
2022, 2024).
Although Rice's whales may occur outside of the general depth range expected to provide suitable habitat, we expect that any such occurrence would be rare. Viridien's planned activities will occur in water depths of approximately 600 to 1,500 m in the central GOA. Thus, NMFS does not expect that take of Rice's whale is likely in association with this survey and, accordingly, does not authorize take of Rice's whale through the LOA.
LLOG
LLOG plans to conduct survey effort at multiple platform locations in the GOA. Survey effort could be conducted as Zero Offset, Offset, or Walkaway vertical seismic profile (VSP), Salt Proximity Survey, and/or Checkshot surveys. Water depths at the locations where LLOG plans to conduct survey effort range from approximately 366 to 2,300 m. LLOG plans to use either a 12-element, 2,400 in3
airgun array, or a 6-element, 1,500 in3
airgun array.
Consistent with the preamble to the final rule, the survey effort proposed by LLOG in its LOA request was used to develop LOA-specific take estimates based on the acoustic exposure modeling results described in the preamble (91 FR 20784, April 17, 2026). In order to generate the appropriate take number for authorization, the following information was considered: (1) survey type; (2) location (by modeling zone i
); (3) number of days; (4) source; and (5) month.ii
In this case, the 4,130 in3
airgun array was selected. This proxy selection represents the least impactful modeled airgun array but remains conservative for purposes of evaluating LLOG's planned survey effort (
i.e.,
maximum 12-element, 2,400 in3
array). The acoustic exposure modeling
( printed page 24813)
performed in support of the rule provides 24-hour exposure estimates for each species, specific to each modeled source and survey type in each zone and month.
No VSP surveys were included in the modeled survey types, and use of existing proxies (
i.e.,
2D, 3D NAZ, 3D WAZ, Coil) is generally conservative for use in evaluation of VSP survey effort, largely due to the greater area covered by the modeled proxies. Summary descriptions of these modeled survey geometries are available in the preamble to the proposed rule (91 FR 9014, 9018, February 24, 2026). Coil was selected as the best available proxy survey type in this case because the spatial coverage of the new survey activity is most similar to the coil survey pattern.
For the survey activity, the seismic source array will be deployed in one of the following forms: Zero Offset VSP—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; Offset VSP—in a fixed position deployed from a supply vessel on an offset position; Walkaway VSP—attached to a line, or a series of lines, towed by a supply vessel; 3D VSP—source moves along a spiral or line swaths towed by a supply vessel; Salt-Proximity—consists typically of a combination of both Zero Offset VSP plus a fixed Offset VSP; or Checkshot—similar to Zero Offset VSP, typically hung from a platform and a sensor placed at a few depths in the well, where only the first energy arrival is recorded. The coil survey pattern in the model was assumed to cover approximately 144 km2
per day (compared with approximately 795 km2
, 199 km2
, and 845 km2
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 LLOG'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 LLOG in terms of predicted Level B harassment.
The survey will take place over approximately 26 days total, including 9 days in zone 5, 9 days in zone 6, and 8 days in zone 7. The monthly distribution of survey days is not known in advance. Take estimates for each species are based on the month that produces the greatest value.
Based on the results of our analysis, NMFS has determined that the level of taking expected for each survey and authorized through each of the LOAs is consistent with the findings made for the total taking allowable under the regulations. See table 1 in this notice and table 7 of the rule (91 FR 20784, April 17, 2026).
Small Numbers Determination
Under the 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 (see 91 FR 20784, April 17, 2026). For more information please see NMFS' discussion of small numbers in the 2026 final rule (91 FR 20784, April 17, 2026).
For WesternGeco's, bp's, Viridien's and LLOG's respective surveys, the take numbers for authorization are determined as described above in the Summary of Request and Analysis section. Subsequently, the total incidents of harassment for each species are multiplied by scalar ratios (except in the cases where the take estimate has been rounded up to reflect a group size) to produce a derived product that better reflects the number of individuals likely to be taken within a survey (as compared to the total number of instances of take), accounting for the likelihood that some individual marine mammals may be taken on more than 1 day (see 91 FR 20784, April 17, 2026). The output of this scaling, where appropriate, is incorporated into adjusted total take estimates that are the basis for NMFS' small numbers determinations, as depicted in table 1-4.
For TGS' and FEC's respective surveys, the take numbers for authorization, determined as described above in the Summary of Request and Analysis section, are used by NMFS in making the necessary small numbers determinations, through comparison with the best available abundance estimates (see discussion at 91 FR 20784, 20812, April 17, 2026). For this comparison, NMFS' approach is to use the maximum theoretical population, determined through review of current SARs (
https://www.fisheries.noaa.gov/national/marine-mammal-protection/marine-mammal-stock-assessments) and model-predicted abundance information (
https://seamap.env.duke.edu/models/SEFSC/GOM/). Information supporting the small numbers determinations is provided in table 5-6.
Table 1—WesternGeco Survey Take Analysis 1
Species
Authorized take
Scaled take 1
Abundance 2
Percent
abundance
Rice's whale
0
51
n/a
Sperm whale
527
223
2,451
9.1
Kogia
spp.
3
268
79.6
1,385
7.2
Beaked whales
421
43
1,038
4.1
Rough-toothed dolphin
1,200
344
4,853
7.1
Bottlenose dolphin
336
96
166,538
0.1
Clymene dolphin
488
140
6,136
2.3
Atlantic spotted dolphin
99
28
21,506
0.1
Pantropical spotted dolphin
18,955
5,440
50,209
10.8
Spinner dolphin
239
69
2,991
2.3
Striped dolphin
2,074
595
16,102
3.7
( printed page 24814)
Fraser's dolphin
545
156
1,665
9.4
Risso's dolphin
256
75
1,974
3.8
Blackfish 4
2,122
626
9,535
6.6
Short-finned pilot whale
130
39
3,277
1.2
1
Scalar ratios were applied to “Authorized Take” values as described at 91 FR 20784 (April 17, 2026) to derive scaled take numbers shown here.
2
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 (Garrison
et al.,
2023). For Rice's whale, Atlantic spotted dolphin, spinner dolphin, and Risso's dolphin, the estimated SAR abundance estimate is used.
3
Includes 20 takes by Level A harassment and 248 takes by Level B harassment. Scalar ratio is applied to takes by Level B harassment only; small numbers determination made on basis of scaled Level B harassment take plus authorized Level A harassment take.
4
The “blackfish” guild includes melon-headed whales, false killer whales, pygmy killer whales, and killer whales.
Table 2—
bp
Survey Take Analysis 1
Species
Authorized take
Scaled take 1
Abundance 2
Percent
abundance
Rice's whale
0
51
n/a
Sperm whale
816
345
2,451
14.1
Kogia
spp
3
271
82
1,385
7.1
Beaked whales
1,376
139
1,038
13.4
Rough-toothed dolphin
2,037
585
4,853
12.0
Bottlenose dolphin
1,895
544
166,538
0.3
Clymene dolphin
718
206
6,136
3.4
Atlantic spotted dolphin
562
161
21,506
0.8
Pantropical spotted dolphin
21,781
6,251
50,209
12.5
Spinner dolphin
385
111
2,991
3.7
Striped dolphin
2,736
785
16,102
4.9
Fraser's dolphin
795
228
1,665
13.7
Risso's dolphin
548
162
1,974
8.2
Blackfish 4
3,057
902
9,535
9.5
Short-finned pilot whale
760
224
3,277
6.8
1
Scalar ratios were applied to “Authorized Take” values as described 91 FR 20784, 20818 (April 17, 2026) to derive scaled take numbers shown here.
2
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 (Garrison
et al.,
2023). For Rice's whale, Atlantic spotted dolphin, spinner dolphin, and Risso's dolphin, the estimated SAR abundance estimate is used.
3
Includes 17 takes by Level A harassment and 254 takes by Level B harassment. Scalar ratio is applied to takes by Level B harassment only; small numbers determination made on basis of scaled Level B harassment take plus authorized Level A harassment take.
4
The “blackfish” guild includes melon-headed whales, false killer whales, pygmy killer whales, and killer whales.
Table 3—Viridien Survey Take Analysis 1
Species
Authorized take
Scaled take 1
Abundance 2
Percent
abundance
Rice's whale
0
51
n/a
Sperm whale
504
213
2,451
8.7
Kogia
spp
3
219
66
1,385
2.0
Beaked whales
209
21
1,038
2.0
Rough-toothed dolphin
1,322
379
4,853
7.8
Bottlenose dolphin
1,738
499
166,538
0.3
Clymene dolphin
2,373
681
6,136
11.1
Atlantic spotted dolphin
2,938
843
21,506
3.9
Pantropical spotted dolphin
10,936
3,139
50,209
6.3
Spinner dolphin 4
152
2,991
1.1
Striped dolphin
2,154
10
16,102
3.8
Fraser's dolphin
533
153
1,665
9.2
Risso's dolphin
360
106
1,974
5.4
Blackfish 5
3,742
1,104
9,535
11.6
Short-finned pilot whale
1,811
534
3,277
16.3
1
Scalar ratios were applied to “Authorized Take” values as described at 91 FR 20784, 20818 (April 17, 2026) to derive scaled take numbers shown here.
2
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 (Garrison
et al.,
2023). For Rice's whale, Atlantic spotted dolphin, spinner dolphin, and Risso's dolphin, the estimated SAR abundance estimate is used.
3
Includes 13 takes by Level A harassment and 206 takes by Level B harassment. Scalar ratio is applied to takes by Level B harassment only; small numbers determination made on basis of scaled Level B harassment take plus authorized Level A harassment take.
4
Modeled take of 34 increased to account for potential encounter with a group of average size (Maze-Foley and Mullin, 2006)
5
The “blackfish” guild includes melon-headed whales, false killer whales, pygmy killer whales, and killer whales.
( printed page 24815)
Table 4—LLOG Survey Take Analysis 1
Species
Authorized take
Scaled take 1
Abundance-2
Percent
abundance
Rice's whale
0
51
n/a
Sperm whale
194
82
2,451
3.3
Kogia
spp
3
86
26
1,385
2.2
Beaked whales
343
35
1,038
3.3
Rough-toothed dolphin
500
144
4,853
3.0
Bottlenose dolphin
547
157
166,538
0.1
Clymene dolphin
709
203
6,136
3.3
Atlantic spotted dolphin
526
151
21,506
0.7
Pantropical spotted dolphin
4,970
1,426
50,209
2.8
Spinner dolphin 4
152
2,991
5.1
Striped dolphin
1,265
363
16,102
2.3
Fraser's dolphin
199
57
1,665
3.4
Risso's dolphin
143
42
1,974
2.1
Blackfish 5
1,390
410
9,535
4.3
Short-finned pilot whale
380
112
3,277
3.4
1
Scalar ratios were applied to “Authorized Take” values as described at 91 FR 20784, 20818 (April 17, 2026) to derive scaled take numbers shown here.
2
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 (Garrison
et al.,
2023). For Rice's whale, Atlantic spotted dolphin, spinner dolphin, and Risso's dolphin, the estimated SAR abundance estimate is used.
3
Includes 5 takes by Level A harassment and 81 takes by Level B harassment. Scalar ratio is applied to takes by Level B harassment only; small numbers determination made on basis of scaled Level B harassment take plus authorized Level A harassment take.
4
Modeled take of 66 increased to account for potential encounter with a group of average size (Maze-Foley and Mullin, 2006)
5
The “blackfish” guild includes melon-headed whales, false killer whales, pygmy killer whales, and killer whales.
Table 5—TGS Survey Take Analysis 1
Species
Authorized take
Abundance 2
Percent
abundance
Rice's whale
0
51
n/a
Sperm whale
105
2,451
4.3
Kogia
spp
3
39
1,385
2.8
Beaked whales
35
1,038
3.4
Rough-toothed dolphin
341
4,853
7.0
Bottlenose dolphin
389
166,538
0.2
Clymene dolphin
469
6,136
7.6
Atlantic spotted dolphin
794
21,506
3.7
Pantropical spotted dolphin
1441
50,209
2.9
Spinner dolphin
4
152
2,991
5.1
Striped dolphin
220
16,102
1.4
Fraser's dolphin
137
1,665
8.2
Risso's dolphin
39
1,974
2.0
Blackfish 5
773
9,535
8.1
Short-finned pilot whale
265
3,277
8.1
1
Scalar ratios were not applied in this case due to brief survey duration.
2
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 (Garrison
et al.,
2023). For Rice's whale, Atlantic spotted dolphin, spinner dolphin, and Risso's dolphin, the estimated SAR abundance estimate is used.
3
Includes 2 takes by Level A harassment and 37 takes by Level B harassment. Scalar ratio is applied to takes by Level B harassment only; small numbers determination made on basis of authorized Level B harassment take plus authorized Level A harassment take.
4
Modeled take of 1 increased to account for potential encounter with a group of average size (Maze-Foley and Mullin, 2006)
5
The “blackfish” guild includes melon-headed whales, false killer whales, pygmy killer whales, and killer whales.
Table 6—FEC Survey Take Analysis 1
Species
Authorized take
Abundance 2
Percent
abundance
Rice's whale
0
51
n/a
Sperm whale
0
2,451
n/a
Kogia
spp.
0
1,385
n/a
Beaked whales
0
1,038
n/a
Rough-toothed dolphin
14
4,853
0.1
Bottlenose dolphin
1,570
166,538
0.9
Clymene dolphin
0
6,136
n/a
Atlantic spotted dolphin
95
21,506
0.4
Pantropical spotted dolphin
0
50,209
n/a
Spinner dolphin
0
2,991
n/a
Striped dolphin
0
16,102
n/a
Fraser's dolphin
0
1,665
n/a
( printed page 24816)
Risso's dolphin
0
1,974
n/a
Blackfish 3
0
9,535
n/a
Short-finned pilot whale
0
3,277
n/a
1
Scalar ratios were not applied in this case due to brief survey duration.
2
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 (Garrison
et al.,
2023). For Rice's whale, Atlantic spotted dolphin, spinner dolphin, and Risso's dolphin, the estimated SAR abundance estimate is used.
3
The “blackfish” guild includes melon-headed whales, false killer whales, pygmy killer whales, and killer whales.
Based on the analysis contained herein of WesternGeco's, TGS', FEC's, bp's, Viridien's, and LLOG's planned survey activities described in their respective LOA applications and the anticipated take of marine mammals, NMFS finds that for each LOA 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 for each LOA.
Authorization
NMFS has determined that the level of taking for each 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 each LOA is of no more than small numbers. Accordingly, we have issued LOAs to WesternGeco, TGS, FEC, bp, Viridien, and LLOG, authorizing the take of marine mammals incidental to its geophysical survey activity, as described above.
Dated: May 4, 2026.
Kimberly Damon-Randall,
Director, Office of Protected Resources, National Marine Fisheries Service.
Endnotes
i
For purposes of acoustic exposure modeling, the GOA was divided into seven zones. Zone 1 is not included in the geographic scope of the rule.
ii
Acoustic propagation modeling was performed for two seasons: Winter (December-March) and Summer (April-November). Marine mammal density data is generally available on a monthly basis, and therefore further refines take estimates temporally.
Footnotes
1.
Pursuant to Executive Order 14172, “Restoring Names That Honor American Greatness,” and Department of the Interior Secretarial Order 3423, “The Gulf of America,” the body of water formerly known as the Gulf of Mexico is now called the Gulf of America.
Use this for formal legal and research references to the published document.
91 FR 24809
Web Citation
Suggested Web Citation
Use this when citing the archival web version of the document.
“Taking and Importing Marine Mammals; Taking Marine Mammals Incidental to Geophysical Surveys Related to Oil and Gas Activities in the Gulf of America,” thefederalregister.org (May 7, 2026), https://thefederalregister.org/documents/2026-09060/taking-and-importing-marine-mammals-taking-marine-mammals-incidental-to-geophysical-surveys-related-to-oil-and-gas-activ.