Composite Training Unit Exercises and Joint Task ... - Govsupport.us
Composite Training Unit Exercises and Joint Task ... - Govsupport.us Composite Training Unit Exercises and Joint Task ... - Govsupport.us
COMPTUEX/JTFEX EA/OEA Final Chapter 4susceptibility between fish with these two types of bladders (Yelverton et al., 1975; Yelverton, 1981).After a nearby underwater blast, most fish that die do so within 1–4 hours, and almost all do so within 24hours (Yelverton et al., 1975; Yelverton, 1981).The rapid rise time of the shock wave resulting from detonation of high explosives causes most of theorgan and tissue damage. Mortality of fish correlates better with impulse, measured in units of pressuretime, than with other blast parameters (Yelverton, 1981). The received impulse depends on the depth atwhich the fish is swimming, the depth of the charge, the mass of the charge, and the distance from chargeto fish. Fish near the bottom or near a bank will receive a larger impulse. A fish on the bottom over ahard surface would receive a greater impulse than it would in open water (Yelverton et al., 1975;Yelverton, 1981). Bottom reflection can also be enhanced if it is focused by bottom terrain.Data from explosive blast studies indicate that very fast, high-level acoustic exposures can cause physicaldamage and/or mortally wound fishes (Hastings and Popper, 2005). There is also reason to believe thatlesser effects might also occur, but these have not been well documented. Just as in investigations testingthe effects of sound, however, the number of species studied in tests of the effects of explosives is verylimited, and there have been no investigations to determine whether blasts that do not kill fish have hadany impact on short- or long-term hearing loss, or on other aspects of physiology (e.g., cell membranepermeability, metabolic rate, stress), and/or behavior (e.g., feeding or reproductive behavior, movementfrom preferred home sites).In addition to impacts occurring near the ocean surface, there is also the possibility that falling fragmentsmay injure or kill individual fish. However, most missiles hit their target or are disabled before hitting thewater. Therefore, most of these missiles and targets hit the water as fragments, which quickly dissipatetheir kinetic energy within a short distance from the surface. Similarly, expended small-arms rounds mayalso strike the water surface with sufficient force to cause injury, but most fish swim some distance belowthe surface of the water. Therefore, fewer fish are exposed to mortality from falling fragments whoseeffects are limited to the near surface.Given the random distribution of juvenile and adult pelagic fish species, planktonic eggs and larvae, andprey items, the relatively large area of the range, and the relatively infrequent number of operations,recovery is expected to occur quickly. The abundance and diversity of fish within the OPAREAs areunlikely to measurably decrease as a result of implementation of the No Action Alternative or ProposedAction. Significant impacts on fish populations are not anticipated with implementation of the No ActionAlternative or Proposed Action.4.3.1.3.3 SoundThere are insufficient data on the effects of exposure to sound, in particular mid-frequency sound, on thevast majority of fishes, and there is a great diversity of ear structures, hearing capabilities, and/or acousticbehaviors among fish. The literature on the detection of, and response to, sound are limited and the dataon vulnerability to injury are almost totally non-existent, only relevant to particular species, and becauseof the great diversity of fishes are not easily extrapolated.If the sound is loud enough and within the range of frequencies that a fish can hear, a sound will bedetected by a fish at some distance from the source. Because of the variable hearing thresholds, thisdistance will vary among species. Theoretically, a yellowfin tuna would have to be much closer than anAtlantic cod to hear a low-frequency sound at a given energy level. Underwater sounds have been usedby fishermen to guide herring and other schooling fish to their nets (Yelverton, 1981), or to exclude fishfrom water intakes (Haymes and Patrick, 1986). The noises made by fishing boats can scare some targetFebruary 2007 4-14
COMPTUEX/JTFEX EA/OEA Final Chapter 4fish (Anon., 1970). Sudden changes in noise level can cause fish to dive or to avoid the sound bychanging direction. Time of year, whether the fish have eaten, and the nature of the sound signal may allinfluence how fish will respond to the sound.In the studies that have been conducted, effects of noise or sonar have been noted at the individual level.However, these studies have focused on a few species and it is not known whether their responses arerepresentative of the wide diversity of other marine fish species. Based on the limited informationcurrently available, mid-frequency active sonar is not likely to injure or kill fish, and any behavioralavoidance of an area is expected to be temporary. Fish species are unlikely to be affected at thepopulation level. Note that the SOCAL OPAREA has maintained a healthy and thriving population ofmany recreationally and commercially important fish species in concert with the historical use of the areafor Navy training.4.3.1.4 Effects on Essential Fish HabitatThis section discusses the potential impacts to Essential Fish Habitat (EFH) established for speciesmanagement under Fishery .Management Plans (FMPs). Coastal Pelagics and Pacific Groundfish(NMFS, 1998) may utilize both nearshore and offshore areas during their lives, as eggs and larvae formost species are planktonic and can occur in nearshore and offshore waters, while adults may be presentin nearshore and/or offshore waters. EFH is established for the life stages of managed species.Adverse effects mean any impact that reduces quality and/or quantity of EFH. Adverse effects mayinclude direct or indirect physical, chemical, or biological alterations of the waters or substrate and lossof, or injury to, benthic organisms, prey species and their habitat, and other ecosystem components, ifsuch modifications reduce the quality and/or quantity of EFH. Adverse effects to EFH may result fromactions occurring within EFH or outside of EFH and may include site-specific or habitat-wide impacts,including individual, cumulative, or synergistic consequences of actions (50 CFR 600.810(a)).Rocky substrate can support extensive communities and provides habitat for a diverse ecosystem of fish,invertebrates, and algae. Live bottoms, as defined by the Bureau of Land Management, are areas“containing biological assemblages consisting of such sessile invertebrates as sea fans, sea whips,hydroids, anemones, ascidians, sponges, bryozoans, and hard corals living upon and attached to naturallyoccurring hard or rocky formations with rough, broken, or smooth topography; and whose lithotopefavors accumulation of turtles, pelagic and demersal fish.” In the SOCAL OPAREA, colonized hardbottom, macroalgae, invertebrates, and deep-slope terraces are found near San Clemente Island , and theoffshore banks (e.g., Tanner and Cortes).. The marine benthic invertebrate assemblages are extremelydiverse and include representatives of nearly all phyla.The majority of the operations that use live munitions, bombs, or missiles occur in the open ocean awayfrom sensitive nearshore benthic habitats. Underwater detonations will occur in areas of soft bottom.Rocky substrate, colonized hard bottoms, and live bottom habitat will be avoided. The conduct of allvessel sinkings in water at least 1,000 fathoms (6,000 feet) deep and at least 50 nautical miles from land.Therefore, SINKEX operations would not destroy or adversely effect sensitive benthic habitats.Expendable materials such as sonobuoys, torpedoes, targets, munitions, intact missiles would eventuallysink to the bottom, and are unlikely to result in any physical impacts to the sea floor because they wouldsink into a soft bottom, where they eventually would be covered by shifting sediments. Soft-bottomhabitats are less sensitive than hard bottom habitats, and, in such areas, the effects of expended materialswould be minimal. Rates of deterioration would vary, depending on material and conditions in theimmediate marine and benthic environment.4-15 February 2007
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COMPTUEX/JTFEX EA/OEA Final Chapter 4s<strong>us</strong>ceptibility between fish with these two types of bladders (Yelverton et al., 1975; Yelverton, 1981).After a nearby underwater blast, most fish that die do so within 1–4 hours, <strong>and</strong> almost all do so within 24hours (Yelverton et al., 1975; Yelverton, 1981).The rapid rise time of the shock wave resulting from detonation of high explosives ca<strong>us</strong>es most of theorgan <strong>and</strong> tissue damage. Mortality of fish correlates better with impulse, measured in units of pressuretime, than with other blast parameters (Yelverton, 1981). The received impulse depends on the depth atwhich the fish is swimming, the depth of the charge, the mass of the charge, <strong>and</strong> the distance from chargeto fish. Fish near the bottom or near a bank will receive a larger impulse. A fish on the bottom over ahard surface would receive a greater impulse than it would in open water (Yelverton et al., 1975;Yelverton, 1981). Bottom reflection can also be enhanced if it is foc<strong>us</strong>ed by bottom terrain.Data from explosive blast studies indicate that very fast, high-level aco<strong>us</strong>tic exposures can ca<strong>us</strong>e physicaldamage <strong>and</strong>/or mortally wound fishes (Hastings <strong>and</strong> Popper, 2005). There is also reason to believe thatlesser effects might also occur, but these have not been well documented. J<strong>us</strong>t as in investigations testingthe effects of sound, however, the number of species studied in tests of the effects of explosives is verylimited, <strong>and</strong> there have been no investigations to determine whether blasts that do not kill fish have hadany impact on short- or long-term hearing loss, or on other aspects of physiology (e.g., cell membranepermeability, metabolic rate, stress), <strong>and</strong>/or behavior (e.g., feeding or reproductive behavior, movementfrom preferred home sites).In addition to impacts occurring near the ocean surface, there is also the possibility that falling fragmentsmay injure or kill individual fish. However, most missiles hit their target or are disabled before hitting thewater. Therefore, most of these missiles <strong>and</strong> targets hit the water as fragments, which quickly dissipatetheir kinetic energy within a short distance from the surface. Similarly, expended small-arms rounds mayalso strike the water surface with sufficient force to ca<strong>us</strong>e injury, but most fish swim some distance belowthe surface of the water. Therefore, fewer fish are exposed to mortality from falling fragments whoseeffects are limited to the near surface.Given the r<strong>and</strong>om distribution of juvenile <strong>and</strong> adult pelagic fish species, planktonic eggs <strong>and</strong> larvae, <strong>and</strong>prey items, the relatively large area of the range, <strong>and</strong> the relatively infrequent number of operations,recovery is expected to occur quickly. The abundance <strong>and</strong> diversity of fish within the OPAREAs areunlikely to measurably decrease as a result of implementation of the No Action Alternative or ProposedAction. Significant impacts on fish populations are not anticipated with implementation of the No ActionAlternative or Proposed Action.4.3.1.3.3 SoundThere are insufficient data on the effects of exposure to sound, in particular mid-frequency sound, on thevast majority of fishes, <strong>and</strong> there is a great diversity of ear structures, hearing capabilities, <strong>and</strong>/or aco<strong>us</strong>ticbehaviors among fish. The literature on the detection of, <strong>and</strong> response to, sound are limited <strong>and</strong> the dataon vulnerability to injury are almost totally non-existent, only relevant to particular species, <strong>and</strong> beca<strong>us</strong>eof the great diversity of fishes are not easily extrapolated.If the sound is loud enough <strong>and</strong> within the range of frequencies that a fish can hear, a sound will bedetected by a fish at some distance from the source. Beca<strong>us</strong>e of the variable hearing thresholds, thisdistance will vary among species. Theoretically, a yellowfin tuna would have to be much closer than anAtlantic cod to hear a low-frequency sound at a given energy level. Underwater sounds have been <strong>us</strong>edby fishermen to guide herring <strong>and</strong> other schooling fish to their nets (Yelverton, 1981), or to exclude fishfrom water intakes (Haymes <strong>and</strong> Patrick, 1986). The noises made by fishing boats can scare some targetFebruary 2007 4-14