Research Centre for Toxic Compounds in the Environment (RECETOX), Faculty of Science, Masaryk University, Kamenice 753/5, Brno CZ-62500, Czech Republic.
Research Centre for Toxic Compounds in the Environment (RECETOX), Faculty of Science, Masaryk University, Kamenice 753/5, Brno CZ-62500, Czech Republic.
J Hazard Mater. 2014 Jan 15;264:514-20. doi: 10.1016/j.jhazmat.2013.10.039. Epub 2013 Oct 26.
Artificial soil is an important standard medium and reference material for soil ecotoxicity bioassays. Recent studies have documented the significant variability of their basic properties among different laboratories. Our study investigated (i) the variability of ten artificial soils from different laboratories by means of the fate, extractability and bioavailability of phenanthrene and lindane, and (ii) the relationships of these results to soil properties and ageing. Soils were spiked with (14)C-phenanthrene and (14)C-lindane, and the total residues, fractions extractable by hydroxypropyl-β-cyclodextrin, and the fractions of phenanthrene mineralizable by bacteria were determined after 1, 14, 28 and 56 days. Significant temporal changes in total residues and extractable and mineralizable fractions were observed for phenanthrene, resulting in large differences between soils after 56 days. Phenanthrene mineralization by indigenous peat microorganisms was suggested as the main driver of that, outweighing the effects of organic matter. Lindane total residues and extractability displayed much smaller changes over time and smaller differences between soils related to organic matter. Roughly estimated, the variability between the artificial soils was comparable to natural soils. The implications of such variability for the results of toxicity tests and risk assessment decisions should be identified. We also suggested that the sterilization of artificial soils might reduce unwanted variability.
人工土壤是土壤生态毒性生物测定的重要标准介质和参考材料。最近的研究记录了不同实验室之间其基本性质的显著差异。我们的研究调查了(i)来自不同实验室的十种人工土壤通过菲和林丹的归宿、可提取性和生物可利用性的可变性,以及(ii)这些结果与土壤性质和老化的关系。土壤中添加了(14)C-菲和(14)C-林丹,在 1、14、28 和 56 天后,测定了总残留物、羟丙基-β-环糊精可提取的分数以及细菌可矿化的菲分数。菲的总残留物、可提取和可矿化分数在 56 天后发生了显著的时间变化,导致土壤之间存在很大差异。土著泥炭微生物对菲的矿化被认为是主要驱动力,超过了有机质的影响。林丹的总残留物和可提取性随时间的变化很小,而且与有机质有关的土壤之间的差异也很小。大致估计,人工土壤之间的可变性与天然土壤相当。这种可变性对毒性试验结果和风险评估决策的影响应该加以确定。我们还建议对人工土壤进行消毒,以减少不必要的可变性。