Institute of Marine Sciences, School of Biological Sciences, University of Portsmouth, Ferry Road, Portsmouth, UK.
Institute of Marine Sciences, School of Biological Sciences, University of Portsmouth, Ferry Road, Portsmouth, UK.
Environ Pollut. 2018 Dec;243(Pt B):1498-1508. doi: 10.1016/j.envpol.2018.09.091. Epub 2018 Sep 27.
Copper and zinc are metals that have been traditionally thought of as past contamination legacies. However, their industrial use is still extensive and current applications (e.g. nanoparticles and antifouling paints) have become additional marine environment delivery routes. Determining a pollutant's genotoxicity is an ecotoxicological priority, but in marine benthic systems putative substances responsible for sediment genotoxicity have rarely been identified. Studies that use sediment as the delivery matrix combined with exposures over life-history relevant timescales are also missing for metals. Here we assess copper and zinc's genotoxicity by exposing the ecologically important polychaete Alitta virens to sediment spiked with environmentally relevant concentrations for 9 months. Target bioavailable sediment and subsequent porewater concentrations reflect the global contamination range for coasts, whilst tissue concentrations, although elevated, were comparable with other polychaetes. Survival generally reduced as concentrations increased, but monthly analyses show that growth was not significantly different between treatments. The differential treatment mortality may have enabled the surviving worms in the high concentration treatments to capture more food thus removing any concentration treatment effects for biomass. Using the alkaline comet assay we confirm that both metals via the sediment are genotoxic at concentrations routinely found in coastal regions and this is supported by elevated DNA damage in worms from field sites. However, combined with the growth data it also highlights the tolerance of A. virens to DNA damage. Finally, using long term (decadal) monitoring data we show stable or increasing sediment concentrations of these metals for many areas. This will potentially mean coastal sediment is a significant mutagenic hazard to the benthic community for decades to come. An urgent reappraisal of the current input sources for these 'old pollutants' is, therefore, required.
铜和锌是传统上被认为是过去污染遗留物的金属。然而,它们的工业用途仍然很广泛,目前的应用(例如纳米颗粒和防污涂料)已成为海洋环境的其他输送途径。确定污染物的遗传毒性是生态毒理学的优先事项,但在海洋底栖系统中,负责沉积物遗传毒性的假定物质很少被识别。对于金属,使用沉积物作为输送基质并结合在与生命史相关的时间范围内进行暴露的研究也很少。在这里,我们通过用环境相关浓度的铜和锌对生态重要的多毛类环节动物 Alitta virens 进行为期 9 个月的沉积物污染暴露,来评估它们的遗传毒性。目标生物可利用的沉积物和随后的孔隙水浓度反映了全球沿海地区的污染范围,而组织浓度虽然升高,但与其他多毛类动物相当。存活率通常随着浓度的增加而降低,但每月的分析表明,处理之间的生长没有显著差异。差异处理死亡率可能使高浓度处理中的存活蠕虫能够捕获更多的食物,从而消除了生物量的任何浓度处理效应。使用碱性彗星试验,我们证实了这两种金属通过沉积物在沿海地区常规发现的浓度下具有遗传毒性,这得到了来自现场的蠕虫中 DNA 损伤升高的支持。然而,结合生长数据,它还突出了 A. virens 对 DNA 损伤的耐受性。最后,使用长期(数十年)监测数据,我们显示了这些金属在许多地区的沉积物浓度稳定或增加。这意味着未来几十年,沿海沉积物将对底栖生物群落构成重大的诱变危害。因此,迫切需要重新评估这些“旧污染物”的当前输入源。