A probabilistic model for deriving soil quality criteria based on secondary poisoning of top predators .2. Calculations for dichlorodiphenyltrichloroethane (DDT) and cadmium

被引:44
作者
Jongbloed, RH [1 ]
Traas, TP [1 ]
Luttik, R [1 ]
机构
[1] NATL INST PUBL HLTH & ENVIRONM PROTECT, NL-3720 BA BILTHOVEN, NETHERLANDS
关键词
D O I
10.1006/eesa.1996.0072
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
A simplified food web with three trophic levels is designed: plants and invertebrates at the first, small birds and mammals at the second, and birds and beasts of prey at the third trophic level. Exposure of top predators via separate food chains is analyzed. However, most top predator species are exposed via more than one food chain (food web). Therefore, a species-specific approach is followed too, for which four bird of prey species and two beast of prey species with different food choices are selected: sparrow hawk, kestrel, barn owl, little owl, badger, and weasel. The most critical food chains for secondary poisoning of top predators are soil --> worm/insect --> bird --> bird of prey for dichlorodiphenyltrichloroethane (DDT), and soil --> worm --> bird/ mammal --> bird of prey for cadmium (Cd). The risk for the selected top predator species is much lower than the risk based on these critical food chains because the critical food chains constitute a minor part of their food webs. Species feeding on birds (sparrow hawk) and small carnivorous mammals (barn owl) are exposed to DDT and Cd to a much higher extent than species mainly feeding on small herbivorous mammals (kestrel and weasel). It is recommended to include exposure via the pathways soil --> worm/insect --> bird/mammal --> top predator in procedures for derivation of environmental quality objectives for persistent and highly lipophilic compounds. (C) 1996 Academic Press, Inc.
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页码:279 / 306
页数:28
相关论文
共 141 条
[41]   SPECIES AND AGE-DIFFERENCES IN ACCUMULATION OF CL-36-DDT BY VOLES AND SHREWS IN THE FIELD [J].
FORSYTH, DJ ;
PETERLE, TJ .
ENVIRONMENTAL POLLUTION SERIES A-ECOLOGICAL AND BIOLOGICAL, 1984, 33 (04) :327-340
[42]   UPTAKE OF CL-36-DDT RESIDUES BY SLUGS AND ISOPODS IN THE LABORATORY AND FIELD [J].
FORSYTH, DJ ;
PETERLE, TJ ;
GOODWIN, MK .
ENVIRONMENTAL POLLUTION SERIES A-ECOLOGICAL AND BIOLOGICAL, 1982, 29 (02) :135-143
[43]   STUDY OF GUINEA-PIGS FED SWISS CHARD GROWN ON MUNICIPAL SLUDGE-AMENDED SOIL - MULTI-ELEMENT CONTENT OF TISSUES [J].
FURR, AK ;
STOEWSAND, GS ;
BACHE, CA ;
LISK, DJ .
ARCHIVES OF ENVIRONMENTAL HEALTH, 1976, 31 (02) :87-91
[44]  
GALLAGHER H, 1978, SPREEUW DIEREN DICHT
[45]   EVALUATION OF MODELS FOR PREDICTING TERRESTRIAL FOOD-CHAIN BEHAVIOR OF XENOBIOTICS [J].
GARTEN, CT ;
TRABALKA, JR .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1983, 17 (10) :590-595
[46]  
GENELLY R. E., 1956, AUK, V73, P529
[47]   RELATIONSHIP BETWEEN WATER SOLUBILITY AND BIOACCUMULATION POTENTIAL OF ORGANIC-CHEMICALS IN RATS [J].
GEYER, H ;
KRAUS, AG ;
KLEIN, W ;
RICHTER, E ;
KORTE, F .
CHEMOSPHERE, 1980, 9 (5-6) :277-291
[48]  
GISH CD, 1970, PESTIC MONIT J, V3, P241
[49]   A COMPARISON OF (PB, CD AND ZN) ACCUMULATION IN TERRESTRIAL SLUGS MAINTAINED IN MICROCOSMS - EVIDENCE FOR METAL TOLERANCE [J].
GREVILLE, RW ;
MORGAN, AJ .
ENVIRONMENTAL POLLUTION, 1991, 74 (02) :115-127
[50]  
GRODZINSKA K, 1987, EKOL POL-POL J ECOL, V35, P327