1.1 MB pdf - Bolsa Chica Lowlands Restoration Project
1.1 MB pdf - Bolsa Chica Lowlands Restoration Project
1.1 MB pdf - Bolsa Chica Lowlands Restoration Project
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SECTION 2:PROBLEM FORMULATION<br />
Fish can be exposed to chemicals in sediment and/or surface water through incidental<br />
ingestion, dermal contact, uptake across the gills, and consumption of contaminated aquatic<br />
plants or invertebrates. However, because no suitable model was available to evaluate<br />
food-chain exposures, food ingestion was not included in the evaluation. Fish also serve as<br />
a major route of food chain transfer because they are prey for other fish and semi-aquatic<br />
wildlife.<br />
Exposure through the food chain is limited to chemicals that bioaccumulate. Chemicals can<br />
be accumulated in plants that are consumed by herbivorous animals, which are then<br />
consumed by omnivorous and insectivorous animals, carnivorous animals, and<br />
decomposers. Pesticides, such as DDT and its metabolites, are of primary concern for<br />
bioaccumulation because these chemicals can also biomagnify up the food chain.<br />
2.6 Biota Sampling in Nearby Areas<br />
Aquatic biota similar to those collected within the <strong>Bolsa</strong> <strong>Chica</strong> <strong>Lowlands</strong> (Sections 2.3.1 and<br />
2.5.1) for the ERA have been sampled in nearby areas through other programs. The Seal<br />
Beach National Wildlife Refuge Study (SWDIV 1995) was conducted to assess the effects of<br />
operations at Naval Weapons Station Seal Beach on the biota of the tidal marsh at Seal Beach<br />
National Wildlife Refuge. The study focused on the potential bioaccumulation of chemicals<br />
in species that are the primary food items of the light-footed clapper rail and California least<br />
terns. Results for invertebrates and fish are summarized in Table 2-24.<br />
Fish also were sampled in Anaheim Bay/Huntington Harbour through the Toxic Substances<br />
Monitoring Program (Rasmussen 1995, 1997). Black perch (Embiotoca jacksoni) and barred<br />
surfperch (Amphistichus argenteus) were sampled in 1992-1993 and yellowfin croaker<br />
(Umbrina roneador) were sampled in 1995. Results for these fish are summarized in<br />
Table 2-25. In 1992, the fish contained elevated levels of total chlordane and total DDT, and<br />
in 1993 they contained elevated levels of chromium and total DDT. In 1995, elevated levels<br />
of total chlordane, total DDT, and total PCB were found in fish.<br />
Transplanted California mussels (Mytilus californianus) were sampled at the Warner Avenue<br />
Bridge on Huntington Harbor in 1994 and 1995 (Rasmussen 1996). (Because no suitable<br />
resident population existed there, mussels from Trinidad Head or Bodega Head were<br />
deployed for 4-6 months prior to sampling). Results are presented in Table 2-26. Mussels<br />
contained elevated levels of cadmium, zinc, chlorpyrifos, total chlordane, total DDT,<br />
dieldrin, and total PCB in both 1994 and 1995. In 1994, concentrations of arsenic, lead,<br />
selenium, and oxadiazon also were elevated, and in 1995, chromium, heptachlor epoxide,<br />
and toxaphene were elevated.<br />
ERA REPORT 2-18 SAC/143368(002.DOC)<br />
7/31/02