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EPA's Vessel General Permit and Small Vessel General

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Threats<br />

Natural Threats. Birds <strong>and</strong> larger freshwater fish feed on eggs <strong>and</strong> larvae, while sharks,<br />

pinnipeds <strong>and</strong> other large predators prey on marine adult <strong>and</strong> subadult fish.<br />

Anthropogenic Threats. In general sturgeon have declined from the combined effects from the<br />

construction of dam <strong>and</strong> water diversion projects, dredging <strong>and</strong> blasting, water pollution <strong>and</strong><br />

fisheries. The longevity, slow rate of growth, delayed maturation, <strong>and</strong> bottom-feeding habits of<br />

sturgeon makes them susceptible to over-harvest <strong>and</strong> exposure to (<strong>and</strong> the accumulation of)<br />

contaminants. Many sturgeon also do not spawn on an annual basis, but may spawn every other<br />

year or even more infrequently. Thus even small increases in mortality can affect population<br />

productivity (Heppell 2007). While sturgeon will be exposed to dissolved contaminants in the<br />

water column their body form, feeding habits <strong>and</strong> affinity with bottom sediments may expose<br />

them to a different suite of contaminants than pelagic fish. The sediment exposure pathway may<br />

be more significant. Benthic dwelling fish such as sturgeon may be exposed through the direct<br />

contact with sediment <strong>and</strong> its boundary layer <strong>and</strong> commonly have a higher rate of exposure<br />

through incidental ingestion.<br />

Southern Green Sturgeon<br />

Green sturgeon occur along the west coast of North America from Mexico to the Bering Sea<br />

(Adams et al. 2002, Colway <strong>and</strong> Stevenson 2007). Distinguished primarily according to genetic<br />

differences <strong>and</strong> spawning locations, NMFS recognizes two species of green sturgeon: a northern<br />

species whose populations are relatively healthy, <strong>and</strong> a Southern species that has undergone<br />

significant decline (Adams et al. 2007). NMFS listed the Southern species of green sturgeon as<br />

threatened in 2006 (71 FR 17757).<br />

Green sturgeon are considered one of the most marine-oriented sturgeon species, spending much<br />

of their lives in coastal marine waters, estuaries <strong>and</strong> bays. Early life stages rear in fresh water,<br />

<strong>and</strong> adults return to fresh water when they are 15 years old or older to spawn. Across the species’<br />

range only three rivers contain documented spawning (Moyle et al. 1992, CDFG 2002). Outside<br />

of natal rivers, the distribution of southern green sturgeon <strong>and</strong> northern green sturgeon overlap.<br />

Both the northern species <strong>and</strong> southern species of green sturgeon occupy coastal estuaries <strong>and</strong><br />

coastal marine waters from southern California to Alaska, including Humbolt Bay, the lower<br />

Columbia River estuary, Willapa Bay, Grays Harbor <strong>and</strong> southeast Alaska. In general, green<br />

sturgeon are more common north of Point Conception, California.<br />

Green sturgeon are spring spawners <strong>and</strong> initiate spawning migrations as early as March. Fish in<br />

the Klamath River have been observed initiating migrations between April <strong>and</strong> June, Rogue<br />

River fish between May <strong>and</strong> July, whereas Heubein et al., (2009) observed Sacramento River<br />

fish making their upstream migrations between March <strong>and</strong> April. Spawning generally occurs in<br />

deep pools of large rivers or off-channel coves (Moyle et al. 1992, Moyle et al. 1995, Rien et al.<br />

2001, Heublein et al. 2009). Fish then tend to aggregate in deep pools, where they will oversummer<br />

before outmigrating in the fall, although some fish have been observed outmigrating<br />

relatively soon after presumed spawning events (Heublein et al. 2009). In the Sacramento River<br />

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