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EPA's Vessel General Permit and Small Vessel General

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damage to mortality.<br />

Baleen whales are exposed to these neurotoxins by preying on highly contaminated zooplankton<br />

(Durbin et al. 2002). For example, the summertime habitat of the North Atlantic right whale<br />

overlaps with seasonal blooms of the toxic dinoflagellate Alex<strong>and</strong>rium fundyense. Foraging right<br />

whales would ingest large concentrations of contaminated copepods, which affect respiratory<br />

capabilities, feeding behavior, <strong>and</strong> ultimately the reproductive condition of the populations<br />

(Durbin et al. 2002).<br />

Sea Turtles<br />

<strong>Vessel</strong> mediated ANS can include the organisms that cause harmful algal blooms. As described<br />

above, harmful algal blooms can produce toxic compounds, including brevetoxin, saxitoxin <strong>and</strong><br />

microcystins. Toxins can bioaccumulate in high trophic level marine animals (Bushaw-Newton<br />

<strong>and</strong> Sellner 1999), with adverse effects ranging from cell <strong>and</strong> tissue damage to mortality.<br />

Immune system responses have been affected by brevetoxin exposure in the endangered<br />

Loggerhead sea turtle (BE).<br />

Mollusks<br />

Invasive species are likely to adversely affect endangered abalone species via predation,<br />

competition, <strong>and</strong> by transmitting parasites. The invasive green crab, described earlier, preys on a<br />

variety of mollusks <strong>and</strong> is likely to prey upon black <strong>and</strong> white abalone. The invasive snail<br />

Batillaria attramentaria outcompetes a native mollusk species, Cerithidea californica, along<br />

northern California via a more efficient ability to convert food into body tissue <strong>and</strong> possibly<br />

greater dispersal potential (Savino <strong>and</strong> Kolar 1996, Carlton 1999, Pothaven et al. 2001). It, or<br />

other introduced sea snails, are likely to compete with reduced black <strong>and</strong> white abalaone<br />

populations for prey <strong>and</strong> habitat. In addition, mollusks are particularly sensitive to pathogens.<br />

Withering syndrome threatens the survival <strong>and</strong> recovery of the black abalone; it is caused by a<br />

Rickettsia-like bacterium, XenoHaliotis californiensis, that was likely introduced to southern<br />

California via ballast water discharge (Friedman et al. 2000, Smith et al. 2003, Bower 2009,<br />

Cohen 2010). Various species of the genus Vibrio have been identified in ballast water<br />

(Anguiano-Beltrán et al. 1998, Ben-Haim <strong>and</strong> Rosenberg 2002, Aguirremacedo et al. 2008) <strong>and</strong><br />

are known to cause high rates of mortality in abalone (Chew 1990, Ciguarria <strong>and</strong> Elston<br />

1997)Simon et al. 2006) (Nell 2002, Lleonart et al. 2003, Nehring 2006, Haupt et al. 2010). A<br />

parasitic worm, Terebrasabella heterouncinata, was introduced to red abalone via aquaculture<br />

but likely to be spread to endangered abalone species via ballast water (Kuris <strong>and</strong> Culver 1999,<br />

Cohen <strong>and</strong> Webb 2002, Culver <strong>and</strong> Kuris 2002, Bower 2006). Thus, the introduction of ANS is<br />

likely to reduce the survival of endangered mollusks through predation, competition, <strong>and</strong> disease<br />

transmission.<br />

Corals<br />

<strong>Vessel</strong>-mediated introductions of ANS adversely affect coral species through the mechanisms of<br />

competition <strong>and</strong> disease transmission. Invasive corals <strong>and</strong> algae overgrow native corals (Lesser<br />

et al. 2007). For example, introduced red algae competes with native Hawaiian coral species for<br />

space on the reef (Lafferty <strong>and</strong> Kuris 1996). The snowflake coral, Carajoa riisei, has overgrown<br />

up to 90% of surveyed black coral colonies in Hawai’i, where it was introduced via shipping<br />

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