INTERPRETING AQUATIC TOXICITY QSARS - THE SIGNIFICANCE OF TOXICANT BODY RESIDUES AT THE PHARMACOLOGICAL END-POINT

被引:40
作者
MCCARTY, LS
MACKAY, D
SMITH, AD
OZBURN, GW
DIXON, DG
机构
[1] NORLAB ENVIRONM SERV INC,THUNDER BAY P7C 5W2,ONTARIO,CANADA
[2] LAKEHEAD UNIV,DEPT BIOL,THUNDER BAY P7B 5E1,ONTARIO,CANADA
[3] UNIV TORONTO,INST ENVIRONM STUDIES,TORONTO M5S 1A4,ONTARIO,CANADA
[4] UNIV WATERLOO,DEPT BIOL,WATERLOO N2L 3G1,ONTARIO,CANADA
关键词
D O I
10.1016/0048-9697(91)90205-S
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Aquatic QSAR investigations employ bioassay data where a biological response is associated with a toxicant concentration in the exposure water. Although convenient this ignores the fundamental principle that the response is more closely related to an amount present in the organism. This problem has been examined using acute toxicity and bioconcentration QSARs employing log K(ow) as the molecular descriptor. Combining these QSAR relationships enables estimates of the amount of toxicant in organisms to be made. For acute narcosis (50% mortality) the toxicant level in the hydrophobic (lipid) phase of an exposed organism is, as a first approximation, constant at approximately 50 mmol l-1 of lipid. For the acute toxicity of a variety of hydrophobic narcotic organics examined by US EPA-Duluth in tests with fathead minnows, this corresponds to a whole-body residue of about 4 mmol kg-1. Although the level in the hydrophobic phase remains constant, for hydrophilic chemicals (log K(ow) < 1.5) the contribution of the hydrophilic (water) phase of the organism dominates and total body residues should be similar to the respective threshold LC50s. This has important implications in simple pharmacokinetic modelling and in interpreting residue levels in organisms collected in environmental monitoring studies.
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页码:515 / 525
页数:11
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