Gimbert Frédéric, de Vaufleury Annette, Douay Francis, Coeurdassier Michaël, Scheifler Renaud, Badot Pierre-Marie
Department of Environmental Biology, University of Franche-Comté, EA 3184 MR UsC INRA, Place Leclerc, 25030 Besançon Cedex, France.
Ecotoxicol Environ Saf. 2008 May;70(1):138-46. doi: 10.1016/j.ecoenv.2007.05.014. Epub 2007 Jul 17.
Juvenile snails were exposed during their growth period to Cd-contaminated field and artificial soils and then transferred to uncontaminated soil to assess the sequels of previous exposure on adult reproduction. Growth modelling highlighted growth inhibitions of 5% and 10% after 70 and 84 days of exposure to 20 and 100 mg Cd kg(-1) in artificial soils, respectively. Growth disruption was accompanied by a decrease in the clutch number and a 4-week delay in the egg-laying cycle. Although it was also contaminated at 20 mg Cd kg(-1), the contaminated field soil did not lead to detectable effects in snails, suggesting a lower Cd bioavailability confirmed by the bioaccumulation analysis. We demonstrated that the 28-day growth test, as advised by the ISO-guideline, may not be sufficient to assess sublethal toxic effects of realistically contaminated soils. For this purpose, a life cycle experimental set-up is proposed, allowing a thorough assessment of toxicity during successive life stages.
将幼年蜗牛在其生长期间暴露于受镉污染的田间土壤和人工土壤中,然后转移到未受污染的土壤中,以评估先前暴露对成年蜗牛繁殖的后续影响。生长模型显示,在人工土壤中暴露于20和100 mg Cd kg(-1) 70天和84天后,生长抑制分别为5%和10%。生长中断伴随着产卵数减少和产卵周期延迟4周。尽管受污染的田间土壤中镉含量也为20 mg Cd kg(-1),但未对蜗牛产生可检测到的影响,生物累积分析证实其镉生物有效性较低。我们证明,按照ISO指南建议进行的28天生长试验可能不足以评估实际受污染土壤的亚致死毒性效应。为此,提出了一种生命周期实验设置,以便全面评估连续生命阶段的毒性。