{"refrec":{"BRefID":128129,"RR":"<b>Criel, P.; Lock, K.; Van Eeckhout, H.; Oorts, K.; Smolders, E.; Janssen, C.R.</b> (2008). Influence of soil properties on copper toxicity for two soil invertebrates. <i>Environ. Toxicol. Chem. 27(8)</i>: 1748-1755. <a href=\"https://dx.doi.org/10.1897/07-545.1\" target=\"_blank\">https://dx.doi.org/10.1897/07-545.1</a>","BEntID":122220,"PublicFlag":1,"CheckedFlag":1,"wosflag":1,"vabbflag":0,"RefStringPartII":". <i>Environ. Toxicol. 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These soils were carefully selected to cover the range of toxicity-influencing parameters encountered in the European Union. Toxicity values varied greatly among soils, with 28-d median effect concentrations ranging from 72.0 to 781 mg Cu/kg dry weight for <i>E. fetida</i> and from 45.4 to 2,270 mg Cu/kg dry weight for <i>F. candida</i>. For both species, variation in copper toxicity values was best explained by differences in the actual cation-exchange capacity (CEC) at soil pH. Using the obtained regression algorithms, the observed toxicity could, in most cases, be predicted within a factor of two for <i>E. fetida</i> and within a factor of three for <i>F. candida</i>. The developed models were validated in three additional European field soils, a standard artificial soil and a standard field soil. The presented regression equations, based on the actual CEC, offer an easy-to-apply method for taking the influence of soil properties on metal toxicity into account. 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