Modeling response of species to microcontaminants: comparative ecotoxicology by (sub)lethal body burdens as a function of species size and partition ratio of chemicals.
A model was designed and calibrated with accumulation data to calculate the internal concentrations of microcontaminants in organisms as a function of a few constants and variables. The main factors are the exposure time, the external exposure concentration, the partition ratio of the compound, and the size of the taxon concerned. The model was applied to calculate the lethal and sublethal body burdens of several priority compounds and some major taxa. Estimations were generally confirmed at the order of magnitude level by measured residues and applied doses if available. According to the estimations, most priority compounds chosen were critical for most taxa above internal concentrations of 0.1 mmol.kg-1 wet wt. Trichloromethane, 1,2,4-trichlorobenzene, and hexachlorobenzene were lethal above this level only, whereas other organic microcontaminants affected at least some taxa at lower body burdens. The log(Kow) of the organic compounds ranged from 2.0 to 7.0. Keeping in mind that bioconcentration and -magnification ratios for metals may be quite variable, the lowest critical residues estimated were just below the value of 0.1 mmol.kg-1 wet wt. Here, external concentrations encountered in natural habitats seem to be a promising tool for predictive comparative ecotoxicology. The critical body burdens for plants and invertebrates may have been overestimated due to uncertainty about the parameters. Among the different taxa, however, the fish families chosen (Salmonidae and Cyprinidae) seem to be most sensitive to most compounds. Internal response concentrations of the herbicide atrazine were the lowest in micro- and macrophytes, whereas parathion affected invertebrates at low levels. The database that provided the external response concentrations was also consulted to estimate so-called extrapolation or safety factors. On average, long-term no effect concentrations in water are estimated to be about 10-30 times below short-term median lethal levels. In general, short-term versus long-term, lethal versus sublethal, and median versus no response concentration ratios each contributed factors of about 2-3 to this overall ratio. The model for internal concentrations indicated that the ratio between the short-term and the long-term LC50 will be high for large species and high octanol-water partition ratios.
Hendriks
A J
AJ
Institute for Inland Water Management and Waste Water Treatment, Lelystad, The Netherlands.
D020003:1-Octanol; D000818:Animals; D001280:Atrazine / Q000378:metabolism / Q000633:toxicity; D001822:Body Burden; D002138:Calibration; D002722:Chlorobenzenes / Q000378:metabolism / Q000633:toxicity; D002725:Chloroform / Q000378:metabolism / Q000633:toxicity; D004781:Environmental Exposure; D004785:Environmental Pollutants / Q000378:metabolism* / Q000633:toxicity; D005399:Fishes; D006540:Herbicides / Q000378:metabolism / Q000633:toxicity; D006581:Hexachlorobenzene / Q000378:metabolism / Q000633:toxicity; D007306:Insecticides / Q000378:metabolism / Q000633:toxicity; D007928:Lethal Dose 50; D000442:Octanols / Q000737:chemistry; D010278:Parathion / Q000378:metabolism / Q000633:toxicity; D013045:Species Specificity; D014867:Water / Q000737:chemistry; D014874:Water Pollutants, Chemical / Q000378:metabolism*
D002722:Chlorobenzenes; D004785:Environmental Pollutants; D006540:Herbicides; D007306:Insecticides; D000442:Octanols; D014874:Water Pollutants, Chemical; D014867:Water; C009947:1,2,4-trichlorobenzene; D006581:Hexachlorobenzene; D010278:Parathion; D002725:Chloroform; D020003:1-Octanol; D001280:Atrazine