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EPA's Vessel General Permit and Small Vessel General

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fish, jellyfish, mollusks, <strong>and</strong> tunicates (Witzell <strong>and</strong> Schmid 2005).<br />

Diving<br />

Kemp’s ridley sea turtles can dive from a few seconds in duration to well over two <strong>and</strong> a half<br />

hours, although most dives range from 16 to 34 minutes (Mendonca <strong>and</strong> Pritchard 1986, Renaud<br />

1995). Individuals spend the vast majority of their time underwater; over 12-hour periods, 89%<br />

to 96% of their time is spent below the surface (Byles 1989b, Gitschlag 1996).<br />

Green sea turtle (Chelonia mydas)<br />

Species description <strong>and</strong> distribution<br />

The green sea turtle is a large, herbivorous, hard-shelled turtle. It has a circumglobal<br />

distribution, occurring throughout tropical, subtropical, <strong>and</strong>, to a lesser extent, temperate waters.<br />

Status<br />

In 1978, the green sea turtle was listed as threatened for all populations with the exception of the<br />

Florida <strong>and</strong> Pacific coast of Mexico breeding populations, which were listed as endangered (43<br />

FR 32800). The International Union for Conservation of Nature (IUCN) has classified the<br />

species as endangered.<br />

Population designations, abundance <strong>and</strong> trends<br />

The species can be divided into two distinct populations: Atlantic <strong>and</strong> Indo-Pacific. Nesting<br />

beaches within each population are connected genetically via male mediated gene flow (Karl et<br />

al. 1992, Roberts et al. 2004), but females generally return to their natal beaches to nest, resulting<br />

in maternally isolated subpopulations (Bowen et al. 1992). An estimated 100,000 – 150,000<br />

females nest each year at 46 locations. Based historical trends at some of these locations, there<br />

appears to an increase in the global population size, but trend data are available for just over half<br />

of all sites examined <strong>and</strong> very few datasets span a full generation (Seminoff 2004). Nesting is<br />

stable or increasing at most sites throughout the Atlantic (NMFS & USFWS 1991). Nesting has<br />

declined throughout the Pacific, with the exception of Hawaii, where the nesting population has<br />

steadily increased in abundance over the past 30 years (Balazs <strong>and</strong> Chaloupka 2004).<br />

Threats<br />

Habitat loss threatens the species globally. Nesting habitat is destroyed by human development,<br />

including: construction of buildings <strong>and</strong> pilings, beach armoring <strong>and</strong> renourishment, <strong>and</strong> s<strong>and</strong><br />

extraction (Lutcavage et al. 1997, Bouchard et al. 1998). Lights on or adjacent to nesting<br />

beaches is often fatal to emerging hatchlings (Witherington <strong>and</strong> Bjorndal 1991) <strong>and</strong> alters the<br />

behavior of nesting adults (Witherington 1992). Anthropogenic disturbances also threaten coastal<br />

marine habitats, particularly areas rich in seagrass <strong>and</strong> marine algae. These impacts include<br />

contamination from herbicides, pesticides, oil spills, <strong>and</strong> other chemicals, as well as structural<br />

degradation from excessive boat anchoring <strong>and</strong> dredging (Francour et al. 1999, Lee Long et al.<br />

2000, Waycott et al. 2005). Further, the introduction of alien algae species threatens the stability<br />

of some coastal ecosystems <strong>and</strong> may lead to the elimination of preferred dietary species of green<br />

sea turtles (De Weede 1996). In the Pacific, where populations are declining, direct take of<br />

164

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