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g. maturity index) were monitored over a period of 8-10 weeks. The response of the nematode communities strongly varied between soil types, and these differences were more pronounced for Zn than for pyrene. Interestingly, the structure of the respective native nematode communities was shown to play a larger role for explaining the varying toxic effects than soil properties governing the bioavailability of the spiked chemicals. We demonstrated that exposure of natural nematode communities in their original soil matrix to the metal zinc an
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