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The Relative Sensitivity of Four Benthic Invertebrates to Selected Metals in Spiked Exposures and Application to Contaminated Field Sediment

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The relative sensitivities of four benthic invertebrates (๐˜๐˜บ๐˜ข๐˜ญ๐˜ฆ๐˜ญ๐˜ญ๐˜ข ๐˜ข๐˜ป๐˜ต๐˜ฆ๐˜ค๐˜ข, ๐˜Š๐˜ฉ๐˜ช๐˜ณ๐˜ฐ๐˜ฏ๐˜ฐ๐˜ฎ๐˜ถ๐˜ด ๐˜ณ๐˜ช๐˜ฑ๐˜ข๐˜ณ๐˜ช๐˜ถ๐˜ด, ๐˜๐˜ฆ๐˜น๐˜ข๐˜จ๐˜ฆ๐˜ฏ๐˜ช๐˜ข spp., and ๐˜›๐˜ถ๐˜ฃ๐˜ช๐˜ง๐˜ฆ๐˜น ๐˜ต๐˜ถ๐˜ฃ๐˜ช๐˜ง๐˜ฆ๐˜น) were determined separately for cadmium, copper, and nickel in 96-hour water-only and in spiked sediment exposures. Survival (LC25's and LC5O's), growth and reproduction (IC25's) endpoints were compared amongst the four species. In the water-only tests, ๐˜. ๐˜ข๐˜ป๐˜ต๐˜ฆ๐˜ค๐˜ข is the most sensitive species to cadmium and nickel, with mean LC5O's of 0.013 and 3.6 mg/L respectively, and ๐˜Š. ๐˜ณ๐˜ช๐˜ฑ๐˜ข๐˜ณ๐˜ช๐˜ถ๐˜ด is the most sensitive species to copper, with a mean LC5O of 0.043 mg/L. In the spiked sediment exposures, ๐˜๐˜ฆ๐˜น๐˜ข๐˜จ๐˜ฆ๐˜ฏ๐˜ช๐˜ข spp. is most sensitive species to copper with a mean LC5O in sediment of 93 ฮผg/g and a mean IC25 of 38 ฮผg/g, and ๐˜. ๐˜ข๐˜ป๐˜ต๐˜ฆ๐˜ค๐˜ข is most sensitive species to cadmium and nickel, with mean LC5O's of 33 and 67 ฮผg/g respectively and mean IC25's of 10 and 40 ฮผg/g respectively. Overall, ๐˜›. ๐˜ต๐˜ถ๐˜ฃ๐˜ช๐˜ง๐˜ฆ๐˜น is the least sensitive species to all metals tested, and the number of young produced/adult is the most sensitive of the reproduction endpoints for ๐˜›. ๐˜ต๐˜ถ๐˜ฃ๐˜ช๐˜ง๐˜ฆ๐˜น. The relative sensitivities reveal that two endpoints, ๐˜Š๐˜ฉ๐˜ช๐˜ณ๐˜ฐ๐˜ฏ๐˜ฐ๐˜ฎ๐˜ถ๐˜ด and ๐˜๐˜ฆ๐˜น๐˜ข๐˜จ๐˜ฆ๐˜ฏ๐˜ช๐˜ข survival, can be used to possibly distinguish between cadmium, copper, and nickel metal toxicity. Species test responses in field-collected sediments from areas contaminated primarily by the above mentioned metals were compared to the determined sensitivities in order to establish the causative agent of toxicity. Sediment toxicity was categorized first by comparing species responses to those established for a reference database. Responses in the field sediment support suspected toxicant in some cases, but not others. Multivariate analyses were used to assess sediment toxicity in the field sites based on the species responses, and these analyses reveal that the test endpoints respond to different environmental variables in ordination space. A comparison of test responses in the field sites to those in reference sites in ordination space reveals 13 of the 15 field-collected sites to be toxic or severely toxic.

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