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Combined Toxicity of Lead and Cadmium on Embryogenesis and Early Larval Stages of the European Clam Ruditapes decussatus

机译:铅和镉对欧洲蛤仔Ruditapes decussatus胚胎发生和幼虫早期的联合毒性

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Individual and combined toxicities of lead (Pb) and cadmium (Cd) were investigated using sperm motility andnembryo-larval bioassay of the clam Ruditapes decussatus. Fertilization and embryogenesis success and larvalnmortality were recorded after incubation of sperm (during 30 min before use for insemination), fertilized eggsn(24 h) and D-shaped larvae (96 h) in seawater, both with single metals and combinations of the two tested metals.nIn spermiotoxicity bioassays, these metals, both individually and in combination, significantly ( p < 0.05) reducednthe fertilization rate only at two higher concentrations that were studied. Median effective concentration (EC50)nvalues were 1033 lg/L (5 lM), 2098.5 lg/L (18.6 lM), and 1442 lg/L (10.8 lM), respectively for individual Pb,nCd, and the mixture (Pb + Cd). Embryogenesis success was also noticeably affected by the single metals and theirnmixture. Median effective concentrations (EC50) values were 256.5 lg/L (1.24 lM), 570.9 lg/L (5.08 lM), andn355.4 lg/L (2.68 lM), respectively for individual Pb, Cd, and the mixture (Pb + Cd). Median lethal concentrationn(LC50) for 96 h larval mortality bioassay registered for individual Pb, Cd, and for the mixture were 453.6 lg/Ln(2.2 lM), 877.8 lg/L (7.8 lM), and 565.6 lg/L (4.3 lM), respectively. Marking–Dawson additive toxicity indicesnwere 0.01, 0.08, and 0.18, respectively, for spermiotoxicity, embryotoxicity, and larval mortality tests, indicatingnadditive effects with a slight trend toward synergism, which was statistically significant only for larval mortality.nThis work shows that both clam embryos and larvae bioassays are useful tools that can be used to evaluatentoxicity of field samples of seawater, sediments, and effluents containing several toxicants.
机译:使用蛤Ru(Ruditapes decussatus)的精子活动性和胚幼虫生物测定法研究了铅(Pb)和镉(Cd)的个体和联合毒性。精子孵化后(用于授精前30分钟内),受精卵n(24小时)和D形幼虫(96小时)在海水中孵化后记录受精,胚胎发生成功率和幼虫死亡率,均使用单种金属和两种测试组合在精子毒性生物测定中,这些金属,无论是单独还是组合使用,仅在所研究的两个较高浓度下才显着(p <0.05)降低了受精率。单个Pb,nCd和混合物(Pb + Cd)的中位有效浓度(EC50)n值分别为1033 lg / L(5 lM),2098.5 lg / L(18.6 lM)和1442 lg / L(10.8 lM) )。单一金属及其混合物也显着影响了胚胎发生的成功。单个Pb,Cd和混合物(Pb +)的中位有效浓度(EC50)值分别为256.5 lg / L(1.24 lM),570.9 lg / L(5.08 lM)和n355.4 lg / L(2.68 lM)。光盘)。分别针对单个Pb,Cd和混合物进行的96 h幼虫死亡率生物测定中的致死浓度n(LC50)为453.6 lg / Ln(2.2 lM),877.8 lg / L(7.8 lM)和565.6 lg / L(4.3 lM ), 分别。精子毒性,胚胎毒性和幼虫死亡率试验的Marking-Dawson加性毒性指数分别为0.01、0.08和0.18,表明其加和效应具有协同作用的轻微趋势,这仅在幼虫死亡率上具有统计学意义。幼虫生物测定法和幼虫生物测定法是有用的工具,可用于评估含有几种毒物的海水,沉积物和废水的现场样本的毒性。

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