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EPA's Vessel General Permit and Small Vessel General

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Louisiana parakeet (Conuropsis carolinensis ludoviciana) became extinct followed two years<br />

later by the extinction of its relative, the Carolina parakeet (C. c. carolinensis). The heath hen<br />

became extinct in the mid-1920s, the June sucker (Chasmistes liorus liorus) in the mid-1930s,<br />

Tecopa pupfish (Cyprinodon nevadensis calidae) in the early 1940s, <strong>and</strong> Ash Meadows killifish<br />

(Empetrichthys merriami) <strong>and</strong> Thicktail chub (Gila crassicauda) in the 1950s. Over the past 200<br />

years, a substantial portion of the bird fauna of the Hawaiian isl<strong>and</strong>s -including the Oahu akepa,<br />

Kona finch, Lanai creeper, black mamo, <strong>and</strong> Hawai’i o’o- became extinct combined with the<br />

extinction of substantial portions of the freshwater mussel fauna of the Mississippi, Ohio, <strong>and</strong><br />

Tennessee Rivers <strong>and</strong> regional extirpations of the flora <strong>and</strong> fauna of California, Florida, Oregon,<br />

Puerto Rico, <strong>and</strong> the desert states.<br />

Status <strong>and</strong> Trends of Waters of the United States<br />

All of the endangered <strong>and</strong> threatened species <strong>and</strong> designated critical habitat under the jurisdiction<br />

of NMFS depend on the health of aquatic ecosystems for their survival. These species were<br />

listed as endangered or threatened, at least in part, because of the consequences of human<br />

activities on the aquatic ecosystems -the estuaries, rivers, lakes, streams, <strong>and</strong> associated<br />

wetl<strong>and</strong>s, floodplains, <strong>and</strong> riparian ecosystems- of the United States, its Territories <strong>and</strong><br />

possessions. The status <strong>and</strong> trends of those aquatic ecosystems determines the status <strong>and</strong> trends<br />

of these species <strong>and</strong> the critical habitat that has been designated for them.<br />

Over the past 30 to 40 years, the nation’s aquatic ecosystems have improved substantially. In<br />

particular, pollution from point sources has been significantly reduced over the past 35 years.<br />

Sewage <strong>and</strong> industrial discharges into aquatic ecosystems have been controlled <strong>and</strong> some<br />

agricultural pesticides have been restricted or banned. Programs like the Conservation Reserve<br />

Program have taken highly erodible l<strong>and</strong>s out of production. Despite this progress, however,<br />

many aquatic ecosystems remain highly polluted. Of the waters bodies they assessed -39 percent<br />

of the river <strong>and</strong> stream miles, 46 percent of the lake area <strong>and</strong> 51 percent of the estuarine area-<br />

one or more designated uses are impaired. Non-point pollution from urban <strong>and</strong> agricultural l<strong>and</strong><br />

(e.g. siltation, nutrients, bacteria, metals <strong>and</strong> oxygen depleting substances) that is transported by<br />

precipitation <strong>and</strong> runoff was the primary cause of the impairment.<br />

These water quality problems, particularly the problem of non-point sources of pollution, have<br />

resulted from the changes humans have imposed on the l<strong>and</strong>scapes of the United States over the<br />

past 100 – 200 years. One way of relating these changes in water quality to l<strong>and</strong> uses relies on<br />

the surface area of a watershed that is covered by porous versus impervious surfaces. Most l<strong>and</strong><br />

areas that are covered by natural vegetation are highly porous <strong>and</strong> have very little sheet flow;<br />

precipitation falling on these l<strong>and</strong>scapes infiltrates the soil, is transpired by the vegetative cover<br />

or evaporates. The increased transformation of the l<strong>and</strong>scapes of the United States into a mosaic<br />

of urban <strong>and</strong> suburban l<strong>and</strong> uses has increased the area of impervious surfaces -roads, rooftops,<br />

parking lots, driveways <strong>and</strong> sidewalks- in those l<strong>and</strong>scapes.<br />

The amount of impervious surface in a watershed is a reliable indicator of a suite of phenomena<br />

that influence a watershed’s hydrology (Center for Watershed Protection, 2003). Above certain<br />

thresholds, l<strong>and</strong>scapes with impervious surfaces respond to precipitation differently than other<br />

204

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