NMFS Biological Opinion on U.S. Navy training ... - Govsupport.us
NMFS Biological Opinion on U.S. Navy training ... - Govsupport.us NMFS Biological Opinion on U.S. Navy training ... - Govsupport.us
FINAL PROGRAMMATIC BIOLOGICAL OPINION ON U.S. NAVY ACTIVITIES IN THE HAWAII RANGE COMPLEX 2008-2013 When they are in coastal or marine waters, loggerhead turtles are affected by a completely different set of human activities that include discharges of toxic chemicals and other pollutants into the marine ecosystem; underwater explosions; hopper dredging, offshore artificial lighting; entrainment or impingement in power plants; entanglement in marine debris; ingestion of marine debris; boat collisions; poaching, and interactions with commercial fisheries. Of these, interactions with fisheries represents a primary threat because of number of individuals that are captured and killed in fishing gear each year. Loggerhead sea turtles are also captured and killed in commercial fisheries. In the Pacific Ocean, between 2,600 and 6,000 loggerhead sea turtles are estimated to have been captured and killed in longline fisheries in 2000 (Lewison et al. 2004). Shallow-set Hawai'i based longline fisheries are estimated to have captured and killed several hundred loggerhead sea turtles before they were closed in 2001. When they were re-opened in 2004, with substantial modifications to protect sea turtles, these fisheries were estimated to have captured and killed about fewer than 5 loggerhead sea turtles each year. Between 2004 and 2008, shallow-set fisheries based out of Hawai'i are estimated to have captured about 45 loggerhead sea turtles, killing about 10 of these sea turtles. A recent biological opinion on these fisheries expected this rate of interaction and deaths to continue into the foreseeable future (
FINAL PROGRAMMATIC BIOLOGICAL OPINION ON U.S. NAVY ACTIVITIES IN THE HAWAII RANGE COMPLEX 2008-2013 Status The most recent reviews show that only two loggerhead nesting beaches have greater than 10,000 females nesting per year: South Florida (U.S.) and Masirah Island (Oman). The status of the Oman nesting colony has not been evaluated recently so the current size of this population and its trend are unknown. Nesting colonies in the U.S. have been reported to produce 68,000 to 90,000 nests per year. Recent analyses of nesting data from southeast Florida nesting colonies, which are the largest nesting colonies in the western Atlantic Ocean, suggest that this nesting population is declining. Long-term nesting data suggest similar declines in loggerhead nesting in North Carolina, South Carolina, and Georgia. In the Eastern Atlantic, the Cape Verde Islands support an intermediately-sized loggerhead nesting colony. In 2000, researchers tagged over 1,000 nesting females on just 5 km (3.1 mi) of beach on Boavista Island (Ehrhart et al. 2003). In the Western Atlantic (excluding the U.S.), Brazil supports an intermediately-sized loggerhead nesting assemblage. Published and unpublished reports provide an estimate of about 4,000 nests per year in Brazil (Ehrhart et al. 2003). Loggerhead nesting throughout the Caribbean is sparse. In the Mediterranean, loggerhead nesting is confined almost exclusively to the eastern portion of the Mediterranean Sea. The main nesting assemblages occur in Cyprus, Greece, and Turkey. However, small numbers of loggerhead nests have been recorded in Egypt, Israel, Italy, Libya, Syria, and Tunisia. Based on the recorded number of nests per year in Cyprus, Greece, Israel, Tunisia, and Turkey, loggerhead nesting in the Mediterranean ranges from about 3,300 to 7,000 nests per season (Margaritoulis et al. 2003). Loggerheads nest throughout the Indian Ocean and, with the exception of Oman, the number of nesting females is small. Most trends in loggerhead nesting populations in the Indian Ocean are unknown. Loggerhead populations in Honduras, Mexico, Colombia, Israel, Turkey, Bahamas, Cuba, Greece, Japan, and Panama have been declining. Balazs and Wetherall (1991) speculated that 2,000 to 3,000 female loggerheads may nest annually in all of Japan; however, more recent data suggest that only approximately 1,000 female loggerhead turtles may nest there (Bolten et al. 1996; Sea Turtle Association of Japan 2002). Monitoring of nesting beaches at Gamoda (Tokushima Prefecture) has been ongoing since 1954. Surveys at this site showed a marked decline in the number of nests between 1960 and the mid-1970s. Since then, the number of nests has fluctuated, but has been downward since 1985 (Bolten et al. 1996; Sea Turtle Association of Japan 2002). Monitoring on several other nesting beaches, surveyed since the mid-1970s, revealed increased nesting during the 1980s before declining during the early 1990s. The number of nests at Gamoda remains very small, fluctuating between near zero (1999) to about 50 nests (1996 and 1998; Kamezaki et al. 2003). Scattered nesting has also been reported on Papua New Guinea, New Zealand, Indonesia, and New Caledonia; however, population sizes on these islands have not been ascertained. Survey data are not available for other nesting assemblages in the south Pacific (
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FINAL PROGRAMMATIC BIOLOGICAL OPINION ON U.S. NAVY ACTIVITIES IN THE HAWAII RANGE COMPLEX 2008-2013<br />
When they are in coastal or marine waters, loggerhead turtles are affected by a completely different set of human<br />
activities that include discharges of toxic chemicals and other pollutants into the marine ecosystem; underwater<br />
explosi<strong>on</strong>s; hopper dredging, offshore artificial lighting; entrainment or impingement in power plants; entanglement<br />
in marine debris; ingesti<strong>on</strong> of marine debris; boat collisi<strong>on</strong>s; poaching, and interacti<strong>on</strong>s with commercial fisheries.<br />
Of these, interacti<strong>on</strong>s with fisheries represents a primary threat beca<strong>us</strong>e of number of individuals that are captured<br />
and killed in fishing gear each year.<br />
Loggerhead sea turtles are also captured and killed in commercial fisheries. In the Pacific Ocean, between 2,600 and<br />
6,000 loggerhead sea turtles are estimated to have been captured and killed in l<strong>on</strong>gline fisheries in 2000 (Lewis<strong>on</strong> et<br />
al. 2004). Shallow-set Hawai'i based l<strong>on</strong>gline fisheries are estimated to have captured and killed several hundred<br />
loggerhead sea turtles before they were closed in 2001. When they were re-opened in 2004, with substantial<br />
modificati<strong>on</strong>s to protect sea turtles, these fisheries were estimated to have captured and killed about fewer than 5<br />
loggerhead sea turtles each year. Between 2004 and 2008, shallow-set fisheries based out of Hawai'i are estimated to<br />
have captured about 45 loggerhead sea turtles, killing about 10 of these sea turtles. A recent biological opini<strong>on</strong> <strong>on</strong><br />
these fisheries expected this rate of interacti<strong>on</strong> and deaths to c<strong>on</strong>tinue into the foreseeable future (<str<strong>on</strong>g>NMFS</str<strong>on</strong>g> 2008).<br />
Loggerhead sea turtles have also been and are expected to c<strong>on</strong>tinue to be captured and killed in the deep-set based<br />
l<strong>on</strong>gline fisheries based out of Hawai'i and American Samoa.<br />
Shrimp trawl fisheries account for the highest number of loggerhead sea turtles that are captured and killed, but they<br />
are also captured and killed in trawls, traps and pots, l<strong>on</strong>glines, and dredges. Al<strong>on</strong>g the Atlantic coast of the U.S.,<br />
<str<strong>on</strong>g>NMFS</str<strong>on</strong>g> estimated that almost 163,000 loggerhead sea turtles are captured in shrimp trawl fisheries each year in the<br />
Gulf of Mexico, with 3,948 of those sea turtles dying as a result of their capture. Each year, several hundred<br />
loggerhead sea turtles are also captured in herring fisheries; mackerel, squid, and butterfish fisheries; m<strong>on</strong>kfish<br />
fisheries; pound net fisheries, summer flounder and scup fisheries; Atlantic pelagic l<strong>on</strong>gline fisheries; and gillnet<br />
fisheries in Pamlico Sound. Although most of these turtles are released alive, these fisheries are combine to capture<br />
about 2,000 loggehead sea turtles each year, killing almost 700; the health effects of being captured <strong>on</strong> the sea turtles<br />
that survive remain unknown.<br />
In the pelagic envir<strong>on</strong>ment, loggerhead sea turtles are exposed to a series of l<strong>on</strong>gline fisheries that include the U.S.<br />
Atlantic tuna and swordfish l<strong>on</strong>gline fisheries, an Azorean l<strong>on</strong>gline fleet, a Spanish l<strong>on</strong>gline fleet, and vario<strong>us</strong> fleets<br />
in the Mediterranean Sea (Aguilar et al. 1995, Bolten et al. 1994, Cro<strong>us</strong>e 1999). In the benthic envir<strong>on</strong>ment in<br />
waters off the coastal U.S., loggerheads are exposed to a suite of fisheries in federal and state waters including trawl,<br />
purse seine, hook and line, gillnet, pound net, l<strong>on</strong>gline, dredge, and trap fisheries.<br />
Like all of the other sea turtles we have disc<strong>us</strong>sed, loggerhead sea turtles are threatened by domestic or domesticated<br />
animals that prey <strong>on</strong> their nests; artificial lighting that disorients adult female and hatchling sea turtles, which can<br />
dramatically increase the mortality rates of hatchling sea turtles; beach replenishment; ingesti<strong>on</strong> and entanglement in<br />
marine debris; and envir<strong>on</strong>mental c<strong>on</strong>taminants.<br />
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