UMR CNRS 6249 Chrono-Environment, University of Franche-Comté, 16 route de Gray, 25030, Besançon Cedex, France.
TESORA, Le Visium, 22 Avenue Aristide Briand, 94110, Arcueil, France.
Environ Sci Pollut Res Int. 2021 Aug;28(32):43629-43642. doi: 10.1007/s11356-021-13618-x. Epub 2021 Apr 10.
To date, no study has linked the environmental and the ecogenotoxicological bioavailability of contaminants to land snails. Yet, understanding the specific ecotoxicological mechanisms from bioaccumulation to genotoxicity is necessary e.g., to build an adverse outcome pathway relevant to risk assessment. Consequently, the aim of our study is to look for relationships between accumulated concentrations of As, Cd and Hg in sub-adult snails and ecotoxicological effects at the individual (survival and growth) and molecular (genomic stability) levels. This study combines random amplified polymorphic DNA (RAPD) coupled with high-resolution capillary electrophoresis system (HRS) and micronucleus (MN) assay on haemocytes to consider various types of cytogenomic damage, such as chromosomal aberrations, breakages, adducts and mutations. The results showed alteration of the individual endpoints at higher accumulation quotients (AQs) that reflect the excess of transfers to snails, especially with decreased survival for As. In addition, genotoxic effects were observed with an increased occurrence of MN in haemocytes for the three meta(loid)s considered (R from 0.57 to 0.61 as a function of the meta(loid)s). No concentration-dependent decrease in genome stability was highlighted by RAPD-HRS in snails exposed to As and Cd but not Hg. Our results demonstrate the complementarity of the RAPD-HRS and the MN assay for understanding the different genotoxic mechanisms of the three metal(loid)s studied in land snails. They show a way to better assess environmental risks of contaminated soils by associating ecotoxicity, genotoxicity and bioaccumulation assays (ISO 24032), i.e., ecogenotoxicological bioavailability. Convergences highlighted here between the bioaccumulation of metal(loid)s in viscera and genotoxic effects in haemocytes constitute a way to better assess the bioavailability of contaminants in soils to the land snail and the subsequent environmental risk.
迄今为止,尚无研究将污染物的环境和生态毒理学生物有效性与陆地蜗牛联系起来。然而,了解从生物积累到遗传毒性的特定生态毒理学机制是必要的,例如,建立与风险评估相关的不利结果途径。因此,我们的研究目的是寻找亚成体蜗牛中砷、镉和汞的积累浓度与个体(生存和生长)和分子(基因组稳定性)水平的生态毒理学效应之间的关系。本研究结合随机扩增多态性 DNA(RAPD)与高分辨率毛细管电泳系统(HRS)和血淋巴细胞微核(MN)测定,考虑了各种类型的细胞遗传毒性损伤,如染色体畸变、断裂、加合物和突变。结果表明,在更高的积累比(AQ)下,个体终点发生了变化,这反映了向蜗牛的过量转移,尤其是砷的存活率降低。此外,还观察到三种金属(类)的血淋巴细胞 MN 发生率增加(R 从 0.57 到 0.61,取决于金属(类)),这表明存在遗传毒性效应。暴露于砷和镉但未暴露于汞的蜗牛中,RAPD-HRS 未显示基因组稳定性随浓度降低而降低。我们的结果表明,RAPD-HRS 和 MN 测定法在理解三种金属(类)在陆地蜗牛中的不同遗传毒性机制方面具有互补性。它们展示了一种通过将生态毒性、遗传毒性和生物积累测定法(ISO 24032)结合起来,更好地评估受污染土壤的环境风险的方法,即生态毒理学生物有效性。这里强调的金属(类)在内脏中的生物积累与血淋巴细胞中的遗传毒性效应之间的趋同,为更好地评估污染物在土壤中对陆地蜗牛的生物有效性以及随后的环境风险提供了一种方法。