20.01.2015 Views

The Coastal Resource Coordinator's Bioassessment Manual

The Coastal Resource Coordinator's Bioassessment Manual

The Coastal Resource Coordinator's Bioassessment Manual

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

HAZMAT 93-1–Toxicity Tests<br />

Elutriate tests were originally developed for testing dredged material to simulate conditions<br />

occurring during open-water disposal and are not considered appropriate for testing the<br />

toxicity of in-situ sediments. <strong>The</strong> chemical extraction techniques, used for extraction testing,<br />

remove only certain contaminants so the test organisms are not exposed to the full suite of<br />

contaminants that are actually present in the contaminated sediments. Pore water<br />

techniques require specialized laboratory equipment, and contaminant concentrations may<br />

vary depending on the extraction technique. <strong>The</strong>re are currently no generally accepted<br />

protocols for pore water extraction.<br />

Studies reviewed by Ankley et al. (1991) indicated that pore water exposures provide more<br />

information on sediment toxicity than elutriate exposures. <strong>The</strong>y found that pore water<br />

samples were consistently more toxic than sediment elutriate samples. However, they also<br />

found that pore water samples were sometimes more toxic than bulk sediment samples,<br />

possibly due to pH differences or to the dilution of toxicants by the addition of clean water<br />

to bulk sediment samples (Ankley et al., 1991). Chapman and Fink (1984) also noted<br />

differences between toxicity of bulk sediment and sediment elutriate. Toxicity of bulk<br />

sediment to larval polychaetes was generally greater than that of sediment elutriate.<br />

However, elutriate samples from some stations were toxic, while bulk sediment from the<br />

same stations were not (Chapman and Fink, 1984). Contaminants that have low solubility<br />

in water generally have lower toxicities determined by elutriate tests. Bulk sediment testing<br />

is currently the preferred method for testing sediments at hazardous waste sites to<br />

determine the potential for biological effects at the site. <strong>The</strong> sediment toxicity tests in the list<br />

of recommended toxicity test protocols (Table 8-1) are based primarily on exposures to bulk<br />

sediments.<br />

Selecting a Test Organism<br />

A wide variety of organisms have been used in toxicity tests. <strong>The</strong> most commonly used soil<br />

toxicity tests are the seed germination test (typically using common crop species), the root<br />

elongation test (most often performed with lettuce), and the earthworm test. Freshwater<br />

organisms used for water and sediment toxicity tests include algae (Selenastrum), daphnids,<br />

chironomids, amphipods, and fish (especially fathead minnow and rainbow trout). <strong>The</strong><br />

most commonly tested marine and estuarine organisms are amphipods, mysids, and bivalve<br />

or echinoderm larvae. Luminescent bacteria have also been used in tests of water, sediment,<br />

and soil.<br />

3-7 August 1997

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!