Cellular biomarker responses of limpets (Mollusca) as measure of sensitivity to cadmiumcontamination

K. Reinecke, W. Schoeman, S. Reinecke
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引用次数: 3

Abstract

Due to the availability and chemical nature of some heavy metals, sub-lethal toxicant levels may persist in the ocean waters and may cause physiological problems and toxicity in invertebrates and other marine organisms. Although studies of metal concentrations in False Bay showed relatively low mean concentrations of Cd, invertebrates such as molluscs, crustaceans and many other groups are able to accumulate high levels of heavy metals in their tissues and still survive in the heaviest polluted areas. They can accumulate numerous pollutants from natural waters in quantities that are many orders of magnitude higher than background levels. Bioaccumulation ofcadmium in intertidal species could cause stress which may be measurable at the cellular level. A variety of limpet species that may serve as suitable ecotoxicological monitoring species occur in abundance on rocky shores along the South African coastline. The aim of this study was to obtain sensitivity data which could contribute to the selection of a suitable monitoring species and the eventual establishment of a species sensitivity distribution model (SSD) with a biomarker responseas endpoint. The limpets Cymbula oculus, Scutellastra longicosta, Cymbula granatina and Scutellastragranularis as well as water samples were collected at two localities in False Bay, South Africa. Analysis of water and biological samples were done by atomic absorption spectrometry. Exposures were done to three different sublethal concentrations of cadmium in the laboratory in static flow tanks over three days. There was a moderate increase in cadmium body concentrations over time. Results obtained at three exposure concentrations showed no significant differences in metal concentrations between the different C. oculus samples. Significant differences were obtained between the control and the exposure groups for each exposure time except between the control and the 1mg/L CdCl2 exposure group after 24 and 72 hours of exposure. Cd body concentrations(soft tissue) varied between 4.56 and 21.41µg/g (wet mass).Mean Cd concentrations in soft tissue of S. longicosta was considerably lower (varying between 1.18 and 19.58 µg/g Cd ) than in the tissues of C. oculus. The control group differed significantly from the 0.8 and 1 mg/L CdCl2 exposures after 48 and 72 hours. Mean Cd body concentrations in S. granular is were the highest of all exposed species, reaching a level of 148 µg/g Cd at the highest exposure concentration and differed significantly from the means of the other samples of the 0.8 mg/L CdCl2 exposure group after 72 hours and from the 1 mg/L CdCl2 group after 24 hours. Significant differences were also obtained between theCd body concentrations of C. granatina for the three exposure concentrations and three exposure times. Lysosomal membrane integrity was determined for both exposed and control animals, using the neutral red retention assay. Three of the four species showed a significant decrease in retention times with an increase in Cd concentration. Inter-species differences in sensitivity to environmentally relevant cadmium concentrations were reflected in the biomarker responses. Based on reduction of NRR times, the order of relative sensitivity to cadmium was S. granularis >C. oculus> S. longicosta.> C.granatina.
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帽贝(软体动物)对镉污染敏感性的细胞生物标志物反应
由于某些重金属的可获得性和化学性质,亚致死毒性水平可能在海水中持续存在,并可能对无脊椎动物和其他海洋生物造成生理问题和毒性。虽然对福斯湾金属浓度的研究表明,镉的平均浓度相对较低,但软体动物、甲壳类动物和许多其他无脊椎动物能够在其组织中积累高水平的重金属,并且仍然在污染最严重的地区生存。它们可以从天然水体中积累大量污染物,其数量比本底水平高出许多个数量级。潮间带物种中镉的生物积累可能导致应激,这种应激可以在细胞水平上测量。各种各样的帽贝可以作为合适的生态毒理学监测物种,在南非海岸线的岩石海岸大量出现。本研究的目的是获得敏感性数据,以帮助选择合适的监测物种,并最终建立具有生物标志物响应终点的物种敏感性分布模型(SSD)。在南非福斯湾(False Bay)的两个地点采集了金针贝(Cymbula oculus)、金针贝(Scutellastra longicosta)、金针贝(Cymbula granatina)和金针贝(Scutellastragranularis)以及水样。水和生物样品的分析采用原子吸收光谱法。在实验室的静态流动槽中,对三种不同的亚致死浓度的镉进行了为期三天的暴露。随着时间的推移,体内镉的浓度有适度的增加。在三种暴露浓度下获得的结果表明,不同样品之间的金属浓度没有显着差异。在暴露24小时和72小时后,除了对照组和1mg/L CdCl2暴露组之间的差异外,在每个暴露时间内,对照组和暴露组之间都有显著差异。Cd体(软组织)浓度在4.56 ~ 21.41µg/g(湿质量)之间变化。龙骨棘软组织中Cd的平均浓度(1.18 ~ 19.58µg/g Cd)明显低于龙骨棘。48小时和72小时后,对照组与暴露于0.8 mg/L和1 mg/L CdCl2组有显著差异。在所有暴露物种中,沙参的Cd体平均浓度最高,最高暴露浓度达到148µg/g Cd,与0.8 mg/L CdCl2暴露组的其他样品在72小时后的平均值和1 mg/L CdCl2暴露组在24小时后的平均值有显著差异。三种暴露浓度和三种暴露时间下,肉苁茸体内ecd浓度也存在显著差异。使用中性红保留法测定暴露动物和对照动物的溶酶体膜完整性。随着Cd浓度的增加,其中3个品种的滞留时间显著减少。物种间对环境相关镉浓度敏感性的差异反映在生物标志物反应中。根据NRR次数的减少,对镉的相对敏感性依次为S. granularis bbbbc。oculus> S. longicosta。> C.granatina。
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