National Marine Fisheries Service (NMFS), National Oceanic and Atmospheric Administration (NOAA), Commerce.
Notice; proposed incidental harassment authorization; request for comments.
NMFS received an application from the U.S. Air Force (USAF), Eglin Air Force Base (Eglin AFB), for renewal of an Incidental Harassment Authorization (IHA) to take marine mammals, by harassment, incidental to conducting air-to-surface (A-S) gunnery missions in the Gulf of Mexico (GOM). The USAF's activities are considered military readiness activities. Pursuant to the Marine Mammal Protection Act (MMPA), NMFS requests comments on its proposal to issue an IHA to Eglin AFB to take, by harassment, several species of marine mammal during the specified activity for a period of 1 year.
Comments and information must be received no later than August 19, 2011.
Comments on the application should be addressed to Michael Payne, Chief, Permits, Conservation and Education Division, Office of Protected Resources, National Marine Fisheries Service, 1315 East-West Highway, Silver Spring, MD 20910. The mailbox address for providing e-mail comments is ITP.Hopper@noaa.gov. NMFS is not responsible for e-mail comments sent to addresses other than the one provided here. Comments sent via e-mail, including all attachments, must not exceed a 10-megabyte file size.
Instructions: All comments received are a part of the public record and will generally be posted to http://www.nmfs.noaa.gov/pr/permits/incidental.htm without change. All Personal Identifying Information (for example, name, address, etc.) voluntarily submitted by the commenter may be publicly accessible. Do not submit Confidential Business Information or otherwise sensitive or protected information.
A copy of the application containing a list of the references used in this document and NMFS' 2008 Environmental Assessment (EA) and Finding of No Significant Impact (FONSI) may be obtained by writing to the address specified above, telephoning the contact listed below (see FOR FURTHER INFORMATION CONTACT), or visiting the internet at: http://www.nmfs.noaa.gov/pr/permits/incidental.htm. Documents cited in this notice may also be viewed, by appointment, during regular business hours, at the aforementioned address.Start Further Info
FOR FURTHER INFORMATION CONTACT:
Brian D. Hopper or Candace Nachman, Office of Protected Resources, NMFS, (301) 427-8401.End Further Info End Preamble Start Supplemental Information
Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.) direct the Secretary of Commerce to allow, upon request, the incidental, but not intentional, taking of small numbers of marine mammals by U.S. citizens who engage in a specified activity (other than commercial fishing) within a specified geographical region if certain findings are made and either regulations are issued or, if the taking is limited to harassment, a notice of a proposed authorization is provided to the public for review.
Authorization for incidental takings shall be granted if NMFS finds that the taking will have a negligible impact on the species or stock(s), will not have an unmitigable adverse impact on the availability of the species or stock(s) for subsistence uses (where relevant), and if the permissible methods of taking and requirements pertaining to the mitigation, monitoring and reporting of such takings are set forth. NMFS has defined “negligible impact” in 50 CFR 216.103 as “* * * an impact resulting from the specified activity that cannot be reasonably expected to, and is not reasonably likely to, adversely affect the species or stock through effects on annual rates of recruitment or survival.”
Section 101(a)(5)(D) of the MMPA established an expedited process by which citizens of the U.S. can apply for an authorization to incidentally take small numbers of marine mammals by harassment. Section 101(a)(5)(D) establishes a 45-day time limit for NMFS review of an application followed by a 30-day public notice and comment period on any proposed authorizations for the incidental harassment of marine mammals. Within 45 days of the close of the comment period, NMFS must either issue or deny the authorization.
The National Defense Authorization Act (NDAA) (Pub. L. 108-136) removed the “small numbers” and “specified geographical region” provisions and amended the definition of “harassment” as it applies to a “military readiness activity” to read as follows (section 3(18)(B) of the MMPA):
(i) Any act that injures or has the significant potential to injure a marine mammal or marine mammal stock in the wild [Level A Harassment]; or (ii) Any act that disturbs or is likely to disturb a marine mammal or marine mammal stock in the wild by causing disruption of natural behavioral patterns, including, but not limited to, migration, surfacing, nursing, breeding, feeding, or sheltering, to a point where such behavioral patterns are abandoned or significantly altered [Level B Harassment].
Summary of Request
NMFS originally received an application on February 13, 2003, from Eglin AFB for the taking, by harassment, of marine mammals incidental to programmatic mission activities within the Eglin Gulf Test and Training Range (EGTTR). The EGTTR is described as the airspace over the GOM that is controlled by Eglin AFB. A notice of receipt of Eglin AFB's application and Notice of Proposed IHA and request for 30-day public comment published on January 23, 2006 (71 FR 3474). A 1-year IHA was subsequently issued to Eglin AFB for Start Printed Page 43268this activity on May 3, 2006 (71 FR 27695, May 12, 2006).
On January 29, 2007, NMFS received a request from Eglin AFB for a renewal of its 2006-2007 IHA, which expired on May 2, 2007. This application addendum requested revisions to three components of the IHA requirements: Protected species surveys; ramp-up procedures; and sea state restrictions. A Notice of Proposed IHA and request for 30-day public comment published on May 30, 2007 (72 FR 29974). A 1-year IHA was subsequently issued to Eglin AFB for this activity on December 11, 2008 (73 FR 78318, December 22, 2008) and was effective through December 10, 2009.
On February 17, 2009, NMFS received a request from Eglin AFB for a renewal of its 2008-2009 IHA, which was valid through December 10, 2009. No modifications to the activity location, the mission activities, or the mitigation and monitoring measures that were required under the 2008-2009 IHA were requested by Eglin AFB at that time. A Notice of Proposed IHA and request for 30-day public comment published on October 19, 2009 (74 FR 53474). A 1-year IHA was subsequently issued to Eglin AFB for this activity on January 27, 2010 (75 FR 5045, February 1, 2010), which expired on January 26, 2011.
On May 16, 2011, NMFS received a request from Eglin AFB for a renewal of its IHA, which expired on January 26, 2011. This application is the one considered by NMFS for this request. Eglin AFB has not had coverage for these activities since expiration of the third IHA. However, Eglin AFB has not conducted these activities during the period without MMPA coverage and will wait to resume these training missions until a new MMPA authorization is issued by NMFS.
A-S gunnery operations may potentially impact marine mammals at or near the water surface. Marine mammals could potentially be harassed, injured, or killed by exploding and non-exploding projectiles, and falling debris (USAF, 2002). However, based on analyses provided in the USAF's 2002 Final Programmatic EA (PEA), Eglin's Supplemental Information Request (2003), and NMFS' 2008 EA, as well as for reasons discussed later in this document, NMFS concurs with Eglin that gunnery exercises are not likely to result in any injury or mortality to marine mammals. Potential impacts resulting from A-S test operations include direct physical impacts (DPI) resulting from ordnance. Eglin AFB has requested to take six cetacean species by Level B harassment. The requested species include: dwarf sperm whale (Kogia simus); pygmy sperm whale (K. breviceps); Atlantic bottlenose dolphin (Tursiops truncatus); Atlantic spotted dolphin (Stenella frontalis); pantropical spotted dolphin (S. attenuata); and spinner dolphin (S. longirostris). In addition, although Eglin AFB's acoustic model predicted the take of two cetacean species by Level A harassment (two Atlantic bottlenose dolphin and one Atlantic spotted dolphin), neither NMFS nor Eglin AFB anticipate that injurious Level A harassment will result from the proposed A-S gunnery missions because of Eglin AFB's standard mitigation measures; therefore, NMFS is not proposing to authorize Level A takes of marine mammals.
Description of the Specified Activity
A-S gunnery missions, a “military readiness activity” as defined under 16 U.S.C. 703 note, involve surface impacts of projectiles and small underwater detonations with the potential to affect cetaceans that may occur within the EGTTR. These missions typically involve the use of 25-mm (0.98-in), 40-mm (1.57-in), and 105-mm (4.13-in) gunnery rounds containing, 0.0662 lb (30 g), 0.865 lb (392 g), and 4.7 lbs (2.1 kg) of explosive, respectively. Live rounds must be used to produce a visible surface splash that must be used to “score” the round (the impact of inert rounds on the sea surface would not be detected). The USAF has developed a 105-mm training round (TR) that contains less than 10 percent of the amount of explosive material (0.35 lb; 0.16 kg) as compared to the “Full-Up” (FU) 105-mm (4.13 in) round. The TR was developed as one method to mitigate effects on marine life during nighttime A-S gunnery exercises when visibility at the water surface is poor. However, the TR cannot be used in the daytime since the amount of explosive material is insufficient to be detected from the aircraft.
Water ranges within the EGTTR that are typically used for the gunnery operations are located in the GOM offshore from the Florida Panhandle (areas W-151A, W-151B, W-151C, and W-151D as shown in Figure 1-2 in Eglin's 2011 application). Data indicate that W-151A (Figure 1-3 in Eglin's application) is the most frequently used water range due to its proximity to Hurlburt Field, but activities may occur anywhere within the EGTTR.
Eglin AFB proposes to conduct these mission activities year round during both daytime and nighttime hours. Therefore, NMFS proposes to make the IHA effective for an entire year from the date of issuance (if the IHA is issued).
As required under the 2006 IHA, the AC-130 gunship aircraft was to conduct at least two complete orbits at a minimum safe airspeed around a prospective target area at a maximum altitude of 1,500 ft (457 m). Based on an amendment requested by Eglin AFB, NMFS required an operational altitude of approximately 4,500 to 10,000 ft (1,372-3,048 m) in the 2008 IHA. Ascent occurs over a 10-15 minute period. Eglin AFB has noted that the search area for these orbits ensures that no vessels (or protected species) are within an area of 5 nm (9.3 km) of the target. The AC-130 continues orbiting the selected target point as it climbs to the mission-testing altitude. During the low altitude orbits and the climb to testing altitude, aircraft crew visually scan the sea surface within the aircraft's orbit circle for the presence of vessels and protected species. Primary responsibility for the surface scan is on the flight crew in the cockpit and personnel stationed in the tail observer bubble and starboard viewing window. The AC-130's optical and electronic sensors are also employed for target clearance. If any marine mammals are detected within the AC-130's orbit circle, either during initial clearance or after commencement of live firing, the aircraft will relocate to another target area and repeat the clearance procedures. A typical distance from the coast for this activity is at least 15 mi (24 km).
When offshore, the crews can scan a 5-nm (9.3-km) radius around the potential impact area to ensure it is clear of surface craft, marine mammals, and sea turtles. Scanning is accomplished using radar, all-light television (TV), infrared sensors (IR), and visual means. An alternative area would be selected if any cetaceans or vessels were detected within a 5-nm (9.3 km) search area. Once the scan is completed, Mk-25 flares are dropped and the firing sequence is initiated.
A typical gunship mission lasts approximately 5 hrs without refueling and 6 hrs when air-to-air refueling is accomplished. A typical mission includes the following sequence of events: (1) 30 min for take-off and to perform airborne sensor alignment, align electro-optical sensors (IR and TV) to heads-up display; (2) 1.5 to 2 hrs of dry fire (no ordnance expended) and includes transition time; (3) 1.5 to 2 hrs of live fire, and includes clearing the area and transiting to and from the range (actual firing activities typically do not exceed 30 min); (4) 1 hr air-to-air refueling, if and when performed; and (5) 30 min of transition work (take-offs, approaches, and landings-pattern work).Start Printed Page 43269
The guns are fired during the live-fire phase of the mission. The actual firing can last from 30 min to 1.5 hrs but is typically completed in 30 min. The number and type of A-S gunnery munitions deployed during a mission varies with each type of mission flown. In addition to the 25-, 40-, and 105-mm rounds, marking flares are also deployed as targets. All guns are fired at a specific target in the water, usually the Mk-25 flares, starting with the lowest caliber ordnance or action with the least impact and proceeding to greater caliber sizes. To establish the test target area, two Mk-25 flares are deployed into the center of the 5-nm (9.3-km) radius cleared area (visually clear of aircraft, ships, and surface marine species) on the water's surface. The flare's burn time normally lasts 10 to 20 min but could be much less if actually hit with one of the ordnance projectiles; however, some flares have burned as long as 40 min. Live fires are a continuous event with pauses during the firing usually well under a minute and rarely from 2 to 5 min. Firing pauses would only exceed 10 min if surface boat traffic or marine protected species caused the mission to relocate; if aircraft, gun, or targeting system problems existed; or if more flares needed to be deployed. The Eglin Safety Office has described the gunnery missions as having 95-percent containment with a 99-percent confidence level within a 5-m (16.4-ft) area around the established flare target test area.
Live-fire Event: 25-mm Round
The 25-mm (0.98-in) firing event in a typical mission includes approximately 560 rounds. These rounds are fired in short bursts of 100 rounds. These bursts last approximately 2-3 s with approximately 100 rounds per burst. Based on the very tight target area and extremely small “miss” distance, these bursts of rounds all enter the water within a 5-m (16.4-ft) area. Therefore, when calculations of the marine mammal Zone of Influence (ZOI) and take estimates are made later in this document for the 25-mm rounds, calculations will be based on the total number of rounds fired per year divided by 100.
Live-fire Event: 40-mm Round
The 40-mm (1.57 in) firing event in a typical mission includes approximately 64 rounds with approximately 20 rounds per burst. Each burst lasts from about 2 to 10 seconds. Based on the very tight target area and extremely small “miss” distance, these bursts of rounds all enter the water within a 5-m (16.4 ft) area. Therefore, when calculations of the marine mammal ZOI and take estimates are made later in this document for the 40-mm rounds, calculations will be based on the total number of rounds fired per year divided by 20.
Live-fire Event: 105-mm Round
The 105-mm firing event in a typical mission includes approximately 30 rounds. These rounds are not fired in bursts but as single shots. The 105-mm firing event lasts approximately 5 min with approximately two rounds per minute. Due to the single firing event of the 105-mm round, the peak pressure of each single 105-mm round is measured at a given distance (91 m (295 ft) for the 105-mm TR and 216 m (709 ft) for the 105-mm FU).
As described in Eglin's 2011 application, gunnery testing in this request includes historical baseline yearly amounts in addition to proposed nighttime gunnery missions. Daytime gunnery testing uses the 105-mm FU round and nighttime gunnery training is proposed using the 105-mm TR. The number of 105-mm rounds including nighttime operations would amount to 2,100. As shown in detail in Table 1, Eglin proposes to conduct a total of 25 daytime missions and 45 nighttime missions annually, expending 16,350 rounds in the daytime and 29,430 rounds at night (750 105-mm FU and 1,350 rounds would be the 105-mm TR).
|Category||Expendable||Number of missions||Rounds per missions||Quantity|
|Daytime Missions||105 mm HE||25||30||750|
|25 mm HEI||64||1,600|
|40 mm HEI||560||14,000|
|Nighttime Missions||105 mm HE||45||30||1,350|
|25 mm HEI||64||2,880|
|40 mm HEI||560||25,200|
Description of Marine Mammals in the Area of the Specified Activity
There are 29 species of marine mammals documented as occurring in Federal waters of the GOM. Of these 29 species of marine mammals, approximately 21 may be found in the vicinity of the proposed action area, the EGTTR. These species are the Bryde's whale (Balaenoptera edeni), sperm whale (Physeter macrocephalus), dwarf sperm whale (Kogia sima), pygmy sperm whale (K. breviceps), Atlantic bottlenose dolphin (Tursiops truncatus), Atlantic spotted dolphin (Stenella frontalis), pantropical spotted dolphin (S. atenuarta), Blainville's beaked whale (Mesoplodon densirostris), Cuvier's beaked whale (Ziphius cavirostris), Gervais' beaked whale (M. europaeus), Clymene dolphin (S. clymene), spinner dolphin (S. longirostris), striped dolphin (S. coeruleoalba), killer whale (Orcinus orca), false killer whale (Pseudorca crassidens), pygmy killer whale (Feresa attenuata), Risso's dolphin (Grampus griseus), Fraser's dolphin (Lagenodelphis hosei), melon-headed whale (Peponocephala electra), rough-toothed dolphin (Steno bredanensis), and short-finned pilot whale (Globicephala macrorhynchus). Of these species, only the sperm whale is listed as endangered under the Endangered Species Act (ESA) and as depleted throughout its range under the MMPA. While some of the other species listed here have depleted status under the MMPA, none of the GOM stocks of those species are considered depleted. Eglin AFB's 2011 MMPA application contains a detailed discussion on the description, status, distribution, regional distribution, diving behavior, and acoustics and hearing for the marine mammals in the EGTTR. Additionally, more detailed information on these species can be found in Wursig et al. (2000), NMFS' 2008 EA (see ADDRESSES), and in the NMFS U.S. Atlantic and GOM Stock Assessment Reports (SARs; Waring et al., 2009). This latter document is available at: Start Printed Page 43270 http://www.nefsc.noaa.gov/publications/tm/tm210/. The West Indian manatee (Trichechus manatus) is managed by the U.S. Fish and Wildlife Service and is not considered further in this proposed IHA Federal Register notice.
The species most likely to occur in the area of Eglin AFB's proposed activities for which takes have been requested include: Atlantic bottlenose dolphin; Atlantic spotted dolphin; pantropical spotted dolphin; spinner dolphin; and dwarf and pygmy sperm whales. Bryde's whales, sperm whales, Blainville's beaked whales, Cuvier's beaked whales, Gervais' beaked whales, killer whales, false killer whales, pygmy killer whales, Risso's dolphins, Fraser's dolphins, striped dolphins, Clymene dolphins, rough-toothed dolphins, short-finned pilot whales, and melon-headed whales are rare in the project area and are not anticipated to be impacted by the A-S gunnery mission activities. Therefore, these species are not considered further in this proposed IHA Federal Register notice.
For all species other than the bottlenose dolphin, density estimates were derived from the Navy OPAREA Density Estimates (NODE) for the GOMEX OPAREA report (DON, 2007). Densities were determined using one of two methods: (1) Model-derived estimates; or (2) SAR or other literature-derived estimates. For the model-based approach, density estimates were calculated for each species within areas containing survey effort. A relationship between these density estimates and associated environmental parameters such as depth, slope, distance from the shelf break, sea surface temperature, and chlorophyll-a concentration was formulated using generalized additive models. This relationship was then used to generate a two-dimensional density surface for the region by predicting densities in areas where no survey data exist. All analyses for cetaceans in the GOM were based on data collected through NMFS-derived vessel surveys conducted between 1996 and 2004. Species-specific density estimates derived through spatial modeling were compared with abundance estimates found in the most current SAR to ensure consistency.
Cetacean density estimates provided by various researchers often do not contain adjustments for perception or availability bias. Perception bias refers to the failure of observers to detect animals, although they are present in the survey area and available to be seen. Availability bias refers to animals that are in the survey area, but are not able to be seen because they are submerged when observers are present. Perception and availability bias result in the underestimation of abundance and density numbers (negative bias). The density estimates provided in the NODE report are not corrected for negative bias and, therefore, likely underestimate density. In order to address potential negative bias, density estimates were adjusted using submergence factors. Although submergence time versus surface time probably varies between and among species populations based on geographic location, season, and other factors, submergence times suggested by Moore and Clark (1998) were used for this proposed IHA.
Bottlenose dolphin density estimates were derived from Protected Species Habitat Modeling in the EGTTR (Garrison, 2008). NMFS developed habitat models using recent aerial survey line transect data collected during winter and summer. In combination with remotely sensed habitat parameters (sea surface temperature and chlorophyll), these data were used to develop spatial density models for cetaceans within the continental shelf and coastal waters of the eastern GOM. Encounter rates during the aerial surveys were corrected for sighting probabilities and the probability that animals were available on the surface to be seen. Given that the survey area completely overlaps the present study area and that these survey data are the most recent and best available, these models are considered to best reflect the occurrence of bottlenose dolphins within the study area. Density estimates were calculated for a number of subareas within the EGTTR, and also aggregated into four principal area categories: (1) North-Inshore; (2) South-Inshore; (3) North-Offshore; and (4) South-Offshore. The proposed action would occur within W-151, which is located in the northernmost portion of the EGTTR (Figures 1-2 and 1-3 in Eglin AFB's 2011 application; see ADDRESSES). Therefore, densities in the northern areas are considered to be the most applicable. In order to provide conservative impact estimates, the greatest density between summer and winter seasons was selected. Densities for northern inshore (shoreline to 20 m water depth) and offshore (20 to 200 m water depth) strata were averaged, resulting in an overall density estimate of 0.6319 bottlenose dolphins per square kilometer (km2) to be used in this proposed IHA.
Cetaceans inhabiting the study area may be grouped as odontocetes (toothed whales, including dolphins) or mysticetes (baleen whales), but most of the cetaceans occurring in the Gulf are odontocetes. Typically, very few baleen whales are found in the Gulf and none are expected to occur within the study area given the known distribution of these species. Within the bulk of the EGTTR, over the west Florida continental shelf, the most common species is the bottlenose dolphin (Garrison, 2008), and the Atlantic spotted dolphin also occurs commonly over the continental shelf (Fulling et al., 2003). In the continental slope waters covered by the EGTTR between the 200 m and 2,000 m isobaths, the most common species include bottlenose dolphins, spinner dolphins, and pantropical spotted dolphins in the deeper part of this area. For conservative analysis, the greatest density between summer and winter was used (Table 3-1 in Eglin AFB's 2011 application; see ADDRESSES).
Potential Effects of the Specified Activity on Marine Mammals
A-S gunnery operations may potentially impact marine mammals at or near the water surface. Marine mammals could potentially be harassed, injured or killed by exploding and non-exploding projectiles, and falling debris (USAF, 2002). However, based on analyses provided in the USAF's Final PEA, Eglin's Supplemental Information Request (2003), and NMFS' 2008 EA, NMFS concurs with Eglin that gunnery exercises are not likely to result in any injury or mortality to marine mammals.
Explosive criteria and thresholds for assessing impacts of explosions on marine mammals were discussed by NMFS in detail in its issuance of an IHA for Eglin's Precision Strike Weapon testing activity (70 FR 48675, August 19, 2005) and are not repeated here. Please refer to that document for this background information. However, one part of the analysis has changed. That information is provided here.
Subsequent to the issuance of the USAF 2002 PEA, NMFS updated one of the dual criteria related to the onset level for temporary threshold shift (TTS; Level B harassment). The USAF 2002 PEA describes the onset of TTS by a single explosion (impulse) based on the criterion in use at that time. Newly available information based on lab controlled experiments that used a seismic watergun to induce TTS in one beluga whale and one bottlenose dolphin (Finneran et al., 2002) showed measured TTS2 (TTS level 2 min after exposure) was 7 and 6 dB in the beluga at 0.4 and 30 kHz, respectively, after exposure to intense single pulses at 226 dB re: 1 µPa p-p (peak to peak). This sound pressure level (SPL) is equivalent Start Printed Page 43271to 23 pounds per square inch (psi). Hearing threshold returned to within 2 dB of the pre-exposure value within 4 min of exposure. No TTS was observed in the bottlenose dolphin at the highest exposure condition (228 dB re 1 µPa p-p). Therefore, NMFS updated the SPL from impulse sound that could induce TTS to 23 psi, from the previous 12 psi. Table 3 in this document outlines the acoustic criteria used by NMFS when addressing noise impacts from explosives. These criteria remain consistent with criteria established for other activities in the EGTTR and other acoustic activities authorized under sections 101(a)(5)(A) and (D) of the MMPA. The 23 psi criterion is used in this document and NMFS' 2008 EA for evaluating the potential for the onset of TTS (Level B harassment) in marine mammals. Additional information on the derivation of the 23 psi criterion can be found in the Final Environmental Impact Statement/Overseas Environmental Impact Statement for the Shock Trial of the Mesa Verde (LPD 19) (Department of the Navy, 2008).
|Level B Behavior||176 dB 1/3 Octave SEL (sound energy level).|
|Level B TTS Dual Criterion||182 dB 1/3 Octave SEL.|
|Level A PTS (permanent threshold shift)||205 dB SEL.|
|Level B Dual Criteria||23 psi.|
|Level A Injury||13 psi-msec.|
Direct Physical Impacts (DPI)
Potential impacts resulting from A-S test operations include DPI resulting from ordnance. DPI could result from gunnery ammunition falling into the water. Marine mammals swimming at the surface could potentially be injured or killed by projectiles if not sighted and firing discontinued; however, the possibility of DPI to marine mammals is considered highly unlikely. Therefore, the risk of injury or mortality from DPI is discountable. The assumptions made by Eglin AFB for DPI calculations can be found in the USAF 2002 Final PEA under the analysis for Alternative 1.
Anticipated Effects on Habitat
The primary source of marine mammal habitat impact is noise resulting from gunnery missions. However, the noise does not constitute a long-term physical alteration of the water column or bottom topography, as the occurrences are of limited duration and are intermittent in time. The target flare's burn time normally lasts 10 to 20 min. Given this short time during which the environment is lighted and the variable locations they are dropped, no increases in density of phytoplankton or other organisms introducing primary productivity into the waters are expected to affect marine mammal habitat or populations. Also, live fires are a continuous event with pauses during the firing usually well under a minute and rarely from 2 to 5 min. Likewise, surface vessels associated with the missions are present in limited duration and are intermittent as well.
Other sources that may affect marine mammal habitat were considered and potentially include the introduction of fuel, chaff, debris, ordnance, and chemical residues into the water column. Chemical residues can enter the water through ammunition, flares, drones, missiles, and smoke. However, the small quantities of chemical compounds that may potentially be introduced into the marine waters of the eastern GOM would rapidly disperse. These additions would be too small to adversely impact the GOM waters.
Based on this information, NMFS has preliminarily determined that the proposed A-S gunnery mission activities will not have any impact on the food or feeding success of marine mammals in the northern GOM. Additionally, no loss or modification of the habitat used by cetaceans in the GOM is expected. Marine mammals are anticipated to temporarily vacate the area of live fire events. However, these events usually do not last more than 90 to 120 min at a time, and animals are anticipated to return to the activity area during periods of non-activity. Thus, the proposed activity is not expected to have any habitat-related effects that could cause significant or long-term consequences for individual marine mammals or on the food sources that they utilize.
In order to issue an incidental take authorization (ITA) under sections 101(a)(5)(A) and (D) of the MMPA, NMFS must, where applicable, set forth the permissible methods of taking pursuant to such activity and other means of effecting the least practicable impact on such species or stock and its habitat, paying particular attention to rookeries, mating grounds, and areas of similar significance, and on the availability of such species or stock for taking for certain subsistence uses (where relevant). The NDAA of 2004 amended the MMPA as it relates to military readiness activities and the ITA process such that “least practicable impact” shall include consideration of personnel safety, practicality of implementation, and impact on the effectiveness of the “military readiness activity”. The training activities described in Eglin AFB's application are considered military readiness activities.
The mitigation measures proposed for inclusion in the IHA are the same as those required in the 2010-2011 IHA (75 FR 5045, February 1, 2010). These measures are virtually identical to the mitigation measures that were required in the 2008 IHA (73 FR 78318, December 22, 2008) and the 2006 IHA (71 FR 27695, May 12, 2006). There were only three differences in the mitigation and monitoring measures between the 2006 and 2008 IHAs. Eglin AFB's 2007 application addendum requested revisions to three components of the IHA requirements: Protected species surveys, ramp-up procedures, and sea state restrictions. A discussion of the differences in the requirements can be found in the 2008 IHA Notice of Issuance (73 FR 78318, December 22, 2008) and NMFS' 2008 EA. The revisions to those three requirements are also included in this proposed IHA. However, the explanations as to why Eglin AFB requested the changes and NMFS' determinations specific to those three requirements are not repeated in this document. Readers should refer to either the 2008 IHA notice or NMFS' 2008 EA (see ADDRESSES) for the full explanation.
Development of the Training Round
The largest type of ammunition used during typical gunnery missions is the 105-mm (4.13-in) round containing 4.7 lbs (2.1 kg) of high explosive (HE). This is several times more HE than that found in the next largest round (40 mm/1.57 in). As a mitigation technique, the USAF developed a 105-mm TR that contains only 0.35 lb (0.16 kg) of HE. The TR was developed to dramatically reduce the risk of harassment at night and Eglin AFB anticipates a 96 percent reduction in impact by using the 105-mm TR.
Areas to be used in gunnery missions are visually monitored for marine mammal presence from the AC-130 aircraft prior to commencement of the mission. If the presence of one or more marine mammals is detected, the target area will be avoided. In addition, monitoring will continue during the mission. If marine mammals are detected at any time, the mission will halt immediately and relocate as necessary or be suspended until the Start Printed Page 43272marine mammal has left the area. Daytime and nighttime visual monitoring will be supplemented with IR and TV monitoring. As nighttime visual monitoring is generally considered to be ineffective at any height, the EGTTR missions will incorporate the TR.
The rationale for requiring ramp-up procedures is that this process may allow animals to perceive steadily increasing noise levels and to react, if necessary, before the noise reaches a threshold of significance. The AC-130 gunship's weapons are used in two activity phases. First, the guns are checked for functionality and calibrated. This step requires an abbreviated period of live fire. After the guns are determined to be ready for use, the mission proceeds under various test and training scenarios. This second phase involves a more extended period of live fire and can incorporate use of one or any combination of the munitions available (25-, 40-, and 105-mm rounds). The ramp-up procedure shall be required for the initial gun calibration, and, after this phase, the guns may be fired in any order. Eglin AFB and NMFS believe this process will allow marine species the opportunity to respond to increasing noise levels. If an animal leaves the area during ramp-up, it is unlikely to return while the live-fire mission is proceeding. This protocol allows a more realistic training experience. In combat situations, gunship crews would not likely fire the complete ammunition load of a given caliber gun before proceeding to another gun. Rather, a combination of guns would likely be used as required by an evolving situation. An additional benefit of this protocol is that mechanical or ammunition problems on an individual gun can be resolved while live fire continues with functioning weapons. This also diminishes the possibility of a lengthy pause in live fire, which, if greater than 10 min, would necessitate Eglin's re-initiation of protected species surveys (described next).
In addition to the development of the TR, the visual mitigation, and the ramp-up procedures already described in this document, additional mitigation measures to protect marine life were included in the 2006, 2008, 2009, and 2010 IHAs and are proposed for inclusion in this proposed IHA. These requirements include:
(1) If daytime weather and/or sea conditions preclude adequate aerial surveillance for detecting marine mammals and other marine life, A-S gunnery exercises must be delayed until adequate sea conditions exist for aerial surveillance to be undertaken. Daytime test firing will be conducted only when sea surface conditions are sea state 4 or less on the Beaufort scale.
(2) Prior to each firing event, the aircraft crew will conduct a visual survey of the 5-nm (9.3-km) wide prospective target area to attempt to sight any marine mammals that may be present (the crew will do the same for sea turtles and Sargassum rafts). The AC-130 gunship will conduct at least two complete orbits at a minimum safe airspeed around a prospective target area at a maximum altitude of 6,000 ft (1,829 m). Provided marine mammals (and other protected species) are not detected, the AC-130 can then continue orbiting the selected target point as it climbs to the mission testing altitude. During the low altitude orbits and the climb to testing altitude, the aircraft crew will visually scan the sea surface within the aircraft's orbit circle for the presence of marine mammals. Primary emphasis for the surface scan will be upon the flight crew in the cockpit and personnel stationed in the tail observer bubble and starboard viewing window. The AC-130's optical and electronic sensors will also be employed for target clearance. If any marine mammals are detected within the AC-130's orbit circle, either during initial clearance or after commencement of live firing, the aircraft will relocate to another target and repeat the clearance procedures. If multiple firing events occur within the same flight, these clearance procedures will precede each event.
(3) The aircrews of the A-S gunnery missions will initiate location and surveillance of a suitable firing site immediately after exiting U.S. territorial waters (less than or equal to 12 nm (22 km)). This would potentially restrict most gunnery activities to the shallower continental shelf waters of the GOM where marine mammal densities are typically lower, and thus potentially avoid the slope waters where the more sensitive species (e.g., endangered sperm whales) typically reside.
(4) Observations will be accomplished using all-light TV, IR sensors, and visual means for at least 60 min prior to each exercise.
(5) Aircrews will utilize visual, night vision goggles, and other onboard sensors to search for marine mammals while performing area clearance procedures during night-time pre-mission activities.
(6) If any marine mammals are sighted during pre-mission surveys or during the mission, activities will be immediately halted until the area is clear of all marine mammals for 60 min or the mission location relocated and resurveyed.
(7) If post-detonation surveys determine that an injury or lethal take of a marine mammal has occurred, the test procedure and the monitoring methods must be reviewed with NMFS and appropriate changes must be made, prior to conducting the next air-to-surface gunnery exercise.
NMFS has carefully evaluated the applicant's proposed mitigation measures and considered a range of other measures in the context of ensuring that NMFS prescribes the means of effecting the least practicable impact on the affected marine mammal species and stocks and their habitat. Our evaluation of potential measures included consideration of the following factors in relation to one another:
- The manner in which, and the degree to which, the successful implementation of the measure is expected to minimize adverse impacts to marine mammals;
- The proven or likely efficacy of the specific measure to minimize adverse impacts as planned; and
- The practicability of the measure for applicant implementation, including consideration of personnel safety, practicability of implementation, and impact on the effectiveness of the military-readiness activity.
Based on our evaluation of the applicant's proposed measures, as well as other measures considered by NMFS, NMFS has preliminarily determined that the proposed mitigation measures provide the means of effecting the least practicable impact on marine mammal species or stocks and their habitat, paying particular attention to rookeries, mating grounds, and areas of similar significance, while also considering personnel safety, practicability of implementation, and impact on the effectiveness of the military-readiness activity.
Proposed Monitoring and Reporting
In order to issue an ITA for an activity, Section 101(a)(5)(D) of the MMPA states that NMFS must, where applicable, set forth “requirements pertaining to the monitoring and reporting of such taking”. The MMPA implementing regulations at 50 CFR 216.104 (a)(13) indicate that requests for ITAs must include the suggested means of accomplishing the necessary monitoring and reporting that will result in increased knowledge of the species and of the level of taking or impacts on populations of marine mammals that are Start Printed Page 43273expected to be present in the proposed action area.
The Incidental Take Statement in NMFS' Biological Opinion on this action required certain monitoring measures to protect marine life. NMFS also imposed these same requirements, as well as additional ones, under Eglin AFB's 2006, 2008, and 2010 IHAs as they related to marine mammals. NMFS is proposing to include these same measures in the 2011 IHA (if issued). They are:
(1) The A-S gunnery mission aircrews will participate in the marine mammal species observation training. Each crew member will be required to complete the training prior to participating in a gunnery mission. Observers will receive training in protected species survey and identification techniques.
(2) Aircrews will initiate the post-mission clearance procedures beginning at the operational altitude of approximately 15,000 to 20,000 ft (4,572 to 6,096 m) elevation, and then initiate a spiraling descent down to an observation altitude of approximately 6,000 ft (1,829 m) elevation. Rates of descent will occur over a 3 to 5 min time frame.
(3) Eglin will track their use of the EGTTR for test firing missions and protected species observations, through the use of mission reporting forms.
(4) A-S gunnery missions will coordinate with next-day flight activities to provide supplemental post-mission observations for marine mammals in the operations area of the previous day.
(5) A summary annual report of marine mammal observations and A-S activities will be submitted to the NMFS Southeast Regional Office (SERO) and the Office of Protected Resources either at the time of a request for renewal of an IHA or 90 days after expiration of the current IHA if a new IHA is not requested. This annual report must include the following information: (i) Date and time of each air-to-surface gunnery exercise; (ii) a complete description of the pre-exercise and post-exercise activities related to mitigating and monitoring the effects of A-S gunnery exercises on marine mammal populations; (iii) results of the monitoring program, including numbers by species/stock of any marine mammals noted injured or killed as a result of the gunnery exercises and number of marine mammals (by species if possible) that may have been harassed due to presence within the 5-nm activity zone; and (iv) a detailed assessment of the effectiveness of sensor-based monitoring in detecting marine mammals in the area of A-S gunnery operations.
(6) If any dead or injured marine mammals are observed or detected prior to testing, or injured or killed during live fire, a report must be made to NMFS by the following business day.
(7) Any unauthorized takes of marine mammals (i.e., injury or mortality) must be immediately reported to NMFS and to the respective stranding network representative.
Estimated Take by Incidental Harassment
As it applies to a “military readiness activity”, the definition of harassment is (Section 3(18)(B) of the MMPA):
(i) Any act that injures or has the significant potential to injure a marine mammal or marine mammal stock in the wild [Level A Harassment]; or (ii) Any act that disturbs or is likely to disturb a marine mammal or marine mammal stock in the wild by causing disruption of natural behavioral patterns, including, but not limited to, migration, surfacing, nursing, breeding, feeding, or sheltering, to a point where such behavioral patterns are abandoned or significantly altered [Level B Harassment].
Take by Level B harassment is anticipated as a result of the A-S gunnery mission activities. The exercises are expected to only affect animals at or very near the surface of the water. Cetaceans in the vicinity of the exercises may incur temporary changes in behavior, and/or temporary changes in their hearing thresholds. Based on the proposed mitigation and monitoring measures described earlier in this document, no serious injury or mortality of marine mammals is anticipated as a result of the A-S gunnery mission activities, and no takes by serious injury or mortality are proposed to be authorized.
Estimating the impacts to marine mammals from underwater detonations is difficult due to complexities of the physics of explosive sound under water and the limited understanding with respect to hearing in marine mammals. Detailed assessments were made in the notice for the 2006 and 2008 IHAs on this action (71 FR 27695, May 12, 2006; 73 FR 78318, December 22, 2008) and are repeated in this Federal Register notice. These assessments used, and improved upon, the criteria and thresholds for marine mammal impacts that were developed for the shock trials of the USS SEAWOLF and the USS WINSTON S. CHURCHILL (DDG-81) (Navy, 1998; 2001). The criteria and thresholds used in those actions were adopted by NMFS for use in calculating incidental takes from explosives. Criteria for assessing impacts from Eglin AFB's A-S gunnery exercises include: (1) Mortality, as determined by exposure to a certain level of positive impulse pressure (expressed as pounds per square inch per millisecond or psi-msec); (2) injury, both hearing-related and non-hearing related; and (3) harassment, as determined by a temporary loss of some hearing ability and behavioral reactions. Due to the small amounts of net explosive weight (NEW) for each of the rounds fired in the EGTTR and the mitigation measures proposed by NMFS for implementation, mortality resulting from the resulting sounds generated into the water column from detonations was determined to be highly unlikely and was not considered further by Eglin AFB or NMFS.
Permanent hearing loss is considered an injury and is termed permanent threshold shift (PTS). NMFS, therefore, categorizes PTS as Level A harassment. Temporary loss of hearing ability is termed TTS, meaning a temporary reduction of hearing sensitivity which abates following noise exposure. TTS is considered non-injurious and is categorized as Level B harassment. NMFS recognizes dual criteria for TTS, one based on peak pressure and one based on the greatest 1/3 octave sound exposure level (SEL) or energy flux density level (EFDL), with the more conservative (i.e., larger) of the two criteria being selected for impacts analysis (note: SEL and EFDL are used interchangeably, but with increasing scientific preference for SEL). The peak pressure metric used in previous shock trials to represent TTS was 12 pounds per square inch (psi) which, for the NEW used, resulted in a zone of possible Level B harassment approximately equal to that obtained by using a 182 decibel (dB) re 1 microPa2-s, total EFDL/SEL metric. The 12-psi metric is largely based on anatomical studies and extrapolations from terrestrial mammal data (see Ketten, 1995; Navy, 1999 (Appendix E, CHURCHILL FEIS; and 70 FR 48675 (August 19, 2005)) for background information). However, the results of a more recent investigation involving marine mammals suggest that, for small charges, the 12-psi metric is not an adequate predictor of the onset of TTS but that one should use 23 psi. This explanation is provided earlier in this document.
Documented behavioral reactions occur at noise levels below those considered to cause TTS in marine mammals (Finneran et al., 2002; Schlundt et al., 2000; Finneran and Schlundt, 2004). In controlled experimental situations, behavioral effects are typically defined as Start Printed Page 43274alterations of trained behaviors. Behavioral effects in wild animals are more difficult to define but may include decreased ability to feed, communicate, migrate, or reproduce. Abandonment of an area due to repeated noise exposure is also considered a behavioral effect. Analyses in other sections of this document refer to such behavioral effects as “sub-TTS Level B harassment.” Schlundt et al. (2000) exposed bottlenose dolphins and beluga whales to various pure-tone sound frequencies and intensities in order to measure underwater hearing thresholds. Masking is considered to have occurred because of the ambient noise environment in which the experiments took place. Sound levels were progressively increased until behavioral alterations were noted (at which point the onset of TTS was presumed). It was found that decreasing the sound intensity by 4 to 6 dB greatly decreased the occurrence of anomalous behaviors. The lowest sound pressure levels, over all frequencies, at which altered behaviors were observed, ranged from 178 to 193 dB re 1 µPa for the bottlenose dolphins and from 180 to 196 dB re 1 µPa for the beluga whales. Thus, it is reasonable to consider that sub-TTS (behavioral) effects occur at approximately 6 dB below the TTS-inducing sound level, or at approximately 176 dB in the greatest 1/3 octave band EFDL/SEL.
Table 3 (earlier in this document) summarizes the relevant thresholds for levels of noise that may result in Level A harassment (injury) or Level B harassment via TTS or behavioral disturbance to marine mammals. Mortality and injury thresholds are designed to be conservative by considering the impacts that would occur to the most sensitive life stage (e.g., a dolphin calf). Table 4 provides the estimated ZOI radii for the EGTTR ordnance. At this time, there are no empirical data or information that would allow NMFS to establish a peak pressure criterion for sub-TTS behavioral disruption.
|Expendable||Level A harassment injurious (205 dB) EFD (m)||Level B harassment non-injurious (182 dB) EFD for TTS (m)||Level B harassment non-injurious (23 psi) for TTS (m)||Level B harassment non-injurious (177 dB) EFD for behavior (m)|
|FU = Full-up; TR = Training Round; HE = High Explosive.|
As mentioned previously, the EGTTR live fire events are continuous events with pauses during the firing usually well under a minute and rarely from 2 to 5 min. Live fire typically occurs within a 30 min time frame, including all ordnance fired: 25 mm; 40 mm; and where the 105-mm ordnance are fired as separate rounds with up to 30-s intervals, the 25-mm and the 40-mm are often fired in multiple bursts. These bursts include multiple rounds (20 to 100) within a 2- to 10-s time frame. Eglin notes that even if animal avoidance once firing commences is not considered, the average swim speed (1.5 m/s) of an animal would not allow sufficient time for new animals to re-enter the Level B harassment ZOI (23 psi) within the time frame of a single burst. As such, only the peak pressure of a single round is measured per burst and experienced at a given distance (53 m (161 ft; 25-mm HE), 124 m (400 ft; 40-mm HE)).
It is assumed that the average swim speed per cetacean is approximately 3 knots or 1.5 m/sec. As a conservative scenario, Eglin assumes that there is one animal present within or near the 282 m Level B behavioral harassment ZOI (FU 105-mm round ZOI), which is the largest ZOI evaluated in this analysis, at the time that the 105-mm live firing begins. The overall marine mammal density determination (see Table 3-1 in the IHA application) assumes a uniform distribution of approximately 1.4 animals per km 2, which results in a distance of approximately 843 m between each animal (all species) on average. At this density distribution and typical swim speed, the next available cetacean would approach the perimeter of the 216 m (709 ft) ZOI (23-psi TTS ZOI) in approximately 9.4 min, assuming a straight line path and a continuous swim profile in the direction of the gunnery exercises. With live-fire events for the 105-mm occurring at a rate of approximately 2 rounds/min, approximately 18 to 19 rounds of the 30 round load (or approximately two-thirds of the total load) would be expended within the 9.4 minute time frame. Based on this scenario, one cetacean would be present in the ZOI at the beginning of live fire, and an additional cetacean would enter the ZOI after 9.4 minutes. The remaining 11 to 12 rounds would be expended in approximately 6 minutes, which would not be enough time for an additional animal to enter the ZOI. However, allowing for potential pauses in firing, it may be possible for one additional animal to enter the ZOI, so that up to three cetaceans could be exposed to the 23-psi TTS threshold associated with 105-mm FU ordnance during a typical mission. Therefore, one cetacean would be within the ZOI for every 10 rounds fired (30 divided by 3), on average. The number of rounds required to result in one exposure is considered an event; therefore, the total number of rounds fired per year is divided by 10. It should be noted that this scenario does not take into account the possibility of marine mammals avoiding the area once firing begins.
Based on this discussion, Table 5 in this Federal Register document provides Eglin AFB's estimates of the annual number of marine mammals, by species, potentially taken by Level A harassment and Level B harassment, by the gunnery mission noise. It should be noted that these estimates are derived without consideration of the effectiveness of Eglin AFB's proposed mitigation measures (except use of the TR), which are discussed earlier in this document. As indicated in Table 5, Eglin AFB and NMFS estimate that approximately three marine mammals could potentially be exposed to injurious Level A harassment noise levels (205 dB re 1 μPa 2 -s or higher); however, neither NMFS nor Eglin AFB Start Printed Page 43275anticipate that injurious Level A harassment will result from the proposed A-S gunnery missions because of Eglin AFB's standard mitigation measures, and NMFS is not proposing to authorize Level A takes of marine mammals.
Approximately 212 marine mammals would be exposed annually to non-injurious (TTS) Level B harassment associated with the 182 dB re 1 μPa 2-s threshold. Because these gunnery exercises result in multiple detonations, they have the potential to also result in a temporary modification in behavior by marine mammals at levels below TTS. Based on Eglin AFB and NMFS' estimates, up to 694 marine mammals may experience a behavioral response to these exercises during the time frame of an IHA (see Table 5). Finally, while one would generally expect the threshold for behavioral modification to be lower than that causing TTS, due to a lack of empirical information and data, a dual criteria for Level B behavioral harassment cannot be developed. However, to ensure that takings are covered by this IHA, NMFS estimates that approximately 906 marine mammals of five stocks may incur Level B (harassment) takes during the 1-year period of an IHA. NMFS has preliminarily determined that this number will be significantly lower due to the expected effectiveness of the mitigation measures proposed for inclusion in the IHA (if issued).
Negligible Impact and Preliminary Determination
NMFS has defined “negligible impact” in 50 CFR 216.103 as “* * * an impact resulting from the specified activity that cannot be reasonably expected to, and is not reasonably likely to, adversely affect the species or stock through effects on annual rates of recruitment or survival.” In making a negligible impact determination, NMFS considers a variety of factors, including but not limited to: (1) The number of anticipated mortalities; (2) the number and nature of anticipated injuries; (3) the number, nature, and intensity, and duration of Level B harassment; and (4) the context in which the takes occur.
The takes from Level B harassment will be due to behavioral disturbance and TTS. Although activities would be permitted to occur year-round and can last for approximately 5 to 6 hours at a time, the actual live-fire portion of the exercise usually only lasts for 90 to 120 min. It is possible that some individuals may be taken more than once if those individuals are located in the exercise area on two different days when exercises are occurring. However, multiple exposures are not anticipated to have effects beyond Level B harassment.Start Printed Page 43276
Of the 21 marine mammal species or stocks that may be in the vicinity of the EGTTR gunnery mission activities, only the sperm whale is listed as endangered under the ESA and as depleted under the MMPA. Sperm whale occurrence in the area of the proposed activity is unlikely because almost all reported sightings have occurred in water depths greater than 200 m. Occurrence in the deeper portions of W-151 is possible, although based on reported sightings locations, density is expected to low. Therefore, Eglin AFB has not requested and NMFS has not proposed the issuance of take authorizations for this species. While animals may be impacted in the immediate vicinity of the activity, Start Printed Page 43277because of the small ZOIs (compared to the vast size of the GOM ecosystem where these species live) and the small amounts of explosives used in the A-S gunnery exercises, NMFS has preliminarily determined that there will not be a substantial impact on marine mammals or on the normal functioning of the nearshore or offshore GOM ecosystems. The proposed activity is not expected to impact rates of recruitment or survival of marine mammals since neither mortality (which would remove individuals from the population) nor injury are anticipated to occur. Although the proposed activity is anticipated to result in Level B harassment of marine mammals (both by behavioral disturbance and TTS), the level of harassment is not anticipated to impact rates of recruitment or survival of marine mammals.
Additionally, the mitigation and monitoring measures proposed to be implemented (described earlier in this document) are expected to further minimize the potential for harassment. The protected species surveys will require Eglin AFB to search the area for marine mammals, and if any are found in the live fire area, then the exercise must be suspended until the animal(s) has left the area or relocated. Moreover, the aircrews of the A-S gunnery missions will initiate location and surveillance of a suitable firing site immediately after exiting U.S. territorial waters (less than or equal to 12 nm (22 km)). This would potentially restrict most gunnery activities to the shallower continental shelf waters of the GOM where marine mammal densities are typically lower, and thus potentially avoid the slope waters where the more sensitive species (e.g., endangered sperm whales) typically reside.
Based on the analysis contained herein of the likely effects of the specified activity on marine mammals and their habitat, and taking into consideration the implementation of the mitigation and monitoring measures, NMFS preliminarily finds that Eglin AFB's A-S gunnery mission exercises will result in the incidental take of marine mammals, by Level B harassment only, and that the total taking from the A-S gunnery mission exercises will have a negligible impact on the affected species or stocks.
Impact on Availability of Affected Species or Stock for Taking for Subsistence Uses
There are no relevant subsistence uses of marine mammals implicated by this action. Therefore, NMFS has preliminarily determined that the total taking of affected species or stocks would not have an unmitigable adverse impact on the availability of such species or stocks for taking for subsistence purposes.
Endangered Species Act (ESA)
A Biological Opinion issued by NMFS on October 20, 2004, concluded that the A-S gunnery exercises in the EGTTR are unlikely to jeopardize the continued existence of species listed under the ESA that are within the jurisdiction of NMFS or destroy or adversely modify critical habitat. NMFS has preliminarily determined that this action, including the modifications to the mitigation and monitoring measures in the previous IHAs issued to Eglin AFB and proposed for inclusion in the 2011 IHA (if issued), does not have effects beyond that which was analyzed in that previous consultation, it is within the scope of that action, and reinitiation of consultation is not necessary. However, prior to issuance of this IHA, NMFS will make a final determination whether additional consultation is necessary.
National Environmental Policy Act (NEPA)
The USAF prepared a Final PEA in November 2002 for the EGTTR activity. NMFS made the USAF's 2002 Final PEA available upon request on January 23, 2006 (71 FR 3474). In accordance with NOAA Administrative Order 216-6 (Environmental Review Procedures for Implementing the National Environmental Policy Act, May 20, 1999), NMFS reviewed the information contained in the USAF's 2002 Final PEA, and, on May 1, 2006, determined that the document accurately and completely described the proposed action, the alternatives to the proposed action, and the potential impacts on marine mammals, endangered species, and other marine life that could be impacted by the preferred alternative and the other alternatives. Accordingly, NMFS adopted the USAF's 2002 Final PEA under 40 CFR 1506.3 and made its own FONSI on May 16, 2006. The NMFS FONSI also took into consideration updated data and information contained in NMFS' Federal Register document noting issuance of an IHA to Eglin AFB for this activity (71 FR 27695, May 12, 2006), and previous notices (71 FR 3474, January 23, 2006; 70 FR 48675, August 19, 2005).
As the issuance of the 2008 IHA to Eglin AFB amended three of the mitigation measures for reasons of practicality and safety, NMFS reviewed the USAF's 2002 Final PEA and determined that a new EA was warranted to address: (1) The proposed modifications to the mitigation and monitoring measures; (2) the use of 23 psi as a change in the criterion for estimating potential impacts on marine mammals from explosives; and (3) a cumulative effects analysis of potential environmental impacts from all GOM activities (including Eglin mission activities), which was not addressed in the USAF's 2002 Final PEA. Therefore, NMFS prepared a new EA in December 2008 and issued a FONSI for its action on December 9, 2008. Based on those findings, NMFS determined that it was not necessary to complete an environmental impact statement for the issuance of an IHA to Eglin AFB for this activity. NMFS has preliminarily determined that this proposed activity is within the scope of NMFS' 2008 EA and FONSI.
As a result of these preliminary determinations, NMFS proposes to authorize the take of several species of marine mammals incidental to the USAF, Eglin AFB, for their A-S gunnery mission activities in the GOM provided the previously mentioned mitigation, monitoring, and reporting requirements are incorporated.Start Signature
Dated: July 12, 2011.
James H. Lecky,
Director, Office of Protected Resources, National Marine Fisheries Service.
[FR Doc. 2011-18324 Filed 7-19-11; 8:45 am]
BILLING CODE 3510-22-P