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Comparative embryo/larval sensitivity of Australian marine bivalves to ten metals: A disjunct between physiology and phylogeny

机译:澳大利亚海洋纤维二气对的比较胚胎/幼料:生理学和系统发育之间的分散

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Metal contamination within the urbanized coastal zon is one threat linked to a decline in the abundance, distribution and/or species diversity of wild marine bivalve populations. This study determined the 48-h embryo/larval sensitivity (no-effect concentration (NEC) and median-effect concentration (EC50)) often marine bivalve species (nine endemic to Australia) to aluminium (Al), cadmium (Cd), chromium (Cr), cobalt (Co), copper (Cu), iron (Fe), lead (Pb), manganese (Mn), nickel (Ni) and zinc (Zn), key metal contaminants impacting urbanized coastal zones in south-eastern Australia, in natural seawater (20-22 °C, 30‰ salinity, pH 7.8-7.9,1.2 mg/L dissolved organic carbon). For all metals, except Fe, the order of sensitivity was oysters > mussels > scallops > cockles > clams, where the economically-important oysters, Magallana gigas and Saccostrea glomerata, were 2.6 (Al) to 4.2 (Cd) times more sensitive than the least sensitive clam species. For all bivalve species, the order of metal sensitivity was Cu > Pb > Zn = Ni > Co > Cd > Al > Cr(Ⅵ) > Mn > Fe(Ⅲ), where Cu was eight times more toxic than Zn or Ni, 28 times more toxic than Cd, 220 times more toxic than Cr(Ⅵ) and 570 times more toxic than Fe(Ⅲ). Iron, unlike the other nine soluble metals, occurred as particulate Fe(Ⅲ) oxyhydroxide, where EC50 values decreased with increasing exposure time as the larval (D-veliger) stage. There was no significant (p > 0.05) effect of embryo/larval mass, or surface area/volume, on metal sensitivity. Further, there was no significant (p > 0.05) relationship between metal sensitivity and phylogeny (genetic distance). Divalent metal sensitivity was positively related (r~2 = 0.87) to cell surface metal-binding affinity. The current Australian marine water quality guideline for Ni is not protective of the ten bivalve species (NECs were 2-6-fold below the guideline), while the guideline for Zn is not protective of oysters.
机译:城市化沿海河口内的金属污染是野生海洋双行性群体的丰富,分布和/或物种多样性下降的一种威胁。该研究确定了48-H胚胎/幼虫敏感性(无效应浓度(NEC)和中值 - 效应浓度(EC50))经常将海洋双子纤维物种(九个流行于澳大利亚)到铝(Al),镉(CD),铬(Cr),钴(Co),铜(Cu),铁(Fe),铅(Pb),锰(Mn),镍(Ni)和锌(Zn),影响东南城市化沿海地区的关键金属污染物澳大利亚,天然海水(20-22°C,30°C,pH 7.8-7.9,1.2 mg / L溶解有机碳)。对于所有金属除外,敏感性除外,敏感性是牡蛎>贻贝>扇贝>蛤蜊,在经济上重要的牡蛎,马格拉纳吉伐和骶疣的蛤蜊,Magallana gigas和saccostrea glomerata是2.6(Al)到4.2(CD)时间比这更敏感最不敏感的蛤蜊物种。对于所有双均法物种,金属敏感性的顺序是Cu> Pb> Zn = Ni> CO> Cd> Al> Cr(Ⅳ)> Mn> Fe(Ⅲ),其中Cu是毒性多于Zn或Ni,28的八倍毒性多于Cd的时间,毒性比Cr(ⅵ)毒性220倍,毒性多于Fe(Ⅲ)。与其他九种可溶性金属不同,铁作为颗粒Fe(Ⅲ)羟基氧化物,其中EC50值随着幼虫(D-Veliger)阶段的曝光时间而增加。胚胎/幼虫质量或表面积/体积没有显着(p> 0.05)效果,金属敏感性。此外,金属敏感性和系统发育(遗传距离)之间没有显着(p> 0.05)的关系。二价金属敏感性与细胞表面金属结合亲和力正相关(R〜2 = 0.87)。目前澳大利亚海洋水质的NI澳大利亚海水水质指南不受保护10种(NEC在指南下方2-6倍),而Zn的指导则不受保护牡蛎。

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