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Benthic invertebrate bioassays with toxic sediment and pore water
Author(s) -
Giesy John P.,
Rosiu Cornell J.,
Graney Robert L.,
Henry Mary G.
Publication year - 1990
Publication title -
environmental toxicology and chemistry
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 1.1
H-Index - 171
eISSN - 1552-8618
pISSN - 0730-7268
DOI - 10.1002/etc.5620090214
Subject(s) - bioassay , daphnia magna , sediment , environmental chemistry , benthic zone , photobacterium phosphoreum , biology , toxicity , dilution , ec50 , chemistry , ecology , biochemistry , paleontology , physics , organic chemistry , in vitro , thermodynamics
The relative sensitivities of bioassays to determine the toxicity of sediments were investigated and three methods of making the sample dilutions required to generate dose‐response relationships were compared. The assays studied were: (a) Microtox®, a 15‐min assay of Photobacterium phosphoreum bioluminescence inhibition by pore water; (b) 48‐h Daphnia magna lethality test in pore water; (c) 10‐d subchronic assay of lethality to and reduction of weight gain by Chironomus tentans performed in either whole sediment or pore water; (d) 168‐h acute lethality assay of Hexagenia limbata in either whole sediment or pore water. The three methods of diluting sediments were: (a) extracting pore water from the toxic location and dilution with pore water from the control station; (b) diluting whole sediment from the toxic location with control whole sediment from a reference location, then extracting pore water; and (c) diluting toxic, whole sediment with whole sediment from a reference location, then using the whole sediment in bioassays. Based on lethality, H. limbata was the most sensitive organism to the toxicity of Detroit River sediment. Lethality of D. magna in pore water was similar to that of H. limbata in whole sediment and can be used to predict effects of whole sediment toxicity to H. limbata. The concentration required to cause a 50% reduction in C. tentans growth (10‐d EC50) was approximately that which caused 50% lethality of D. magna (48‐h LC50) and was similar to the toxicity that restricts benthic invertebrate colonization of contaminated sediments. While the three dilution techniques gave similar results with some assays, they gave very different results in other assays. The dose‐response relationships determined by the three dilution techniques would be expected to vary with sediment, toxicant and bioassay type, and the dose‐response relationship derived from each technique needs to be interpreted accordingly.