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Toxicity and critical body residues of Cd, Cu and Cr in the aquatic oligochaete Tubifex tubifex (Müller) based on lethal and sublethal effects

机译:基于致死作用和亚致死作用的水生寡头Tubifex tubifex(Müller)中Cd,Cu和Cr的毒性和关键身体残留

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The aim of the present study was to estimate critical body residues (CBRs) of three metals [cadmium (Cd), copper (Cu), chromium (Cr)] in the aquatic oligochaete Tubifex tubifex based on lethal (LBR) and sublethal effects (CBR), and to discuss the relevance of the exposure to sediment for deriving CBR. Toxicity parameters (LC50, EC50, LBR50 and CBR50) were estimated for each metal by means of data on survival and on several sublethal variables measured in short-term (4 days), water-only exposures and in long-term, chronic (14 and 28 days) exposures using metal-spiked sediment. Sublethal endpoints included autotomy in short-term exposure, as well as reproduction and growth in chronic bioassays. LBR 50 and CBR50 were 3-6 times higher in sediment than in water-only exposure to Cd and about 2-11 times higher for Cu, depending on the measured endpoint; however, for Cr these parameters varied only by a factor of 1.2. Cu and Cr LBR50 and CBR50 values in 96 h water-only exposure were very similar (survival 2.39 μmol Cu g-1 dw, 2.73 μmol Cr g-1 dw; autotomy 0.53 μmol Cu g-1 dw, 0.78 μmol Cr g-1 dw). However, in metal-spiked sediments, 28 d CBR 50 values for autotomy, reproduction and growth ranged 6.76-29.54 μmol g-1 dw for Cd, 3.88-6.23 μmol g-1 dw for Cu, 0.65 μmol g-1 dw for Cr (calculated only on total number of young). Exposure conditions (time and presence/absence of sediment) seem to be influential in deriving metal CBR values of Cd and Cu, while appear to be irrelevant for Cr. Thus, CBR approach for metals is complex and tissue residue-toxicity relationship is not directly applicable so far.
机译:本研究的目的是基于致死作用(LBR)和亚致死作用(TBR),估算水生寡头Tubifextubifex中三种金属[镉(Cd),铜(Cu),铬(Cr)]的临界残留量(CBR)( CBR),并讨论了暴露于沉积物与CBR的相关性。每种金属的毒性参数(LC50,EC50,LBR50和CBR50)通过生存数据和短期(4天),纯水暴露以及长期,长期(14)中测得的几个亚致死变量来估算和28天)使用金属针状沉淀物进行暴露。亚致死终点包括短期暴露中的自动切开,以及慢性生物测定中的繁殖和生长。 LBR 50和CBR50的沉积物比纯水接触Cd的要高3-6倍,Cu的要高2-11倍,这要取决于所测量的终点。但是,对于Cr,这些参数仅变化1.2倍。纯水暴露96 h时的Cu和Cr LBR50和CBR50值非常相似(生存2.39μmolCu g-1 dw,2.73μmolCr g-1 dw;切开0.53μmolCu g-1 dw,0.78μmolCr g-1 dw)。但是,在金属掺入的沉积物中,自动切割,繁殖和生长的28 d CBR 50值对Cd为6.76-29.54μmolg-1 dw,对Cu为3.88-6.23μmolg-1 dw,对Cr为0.65μmolg-1 dw (仅根据年轻人总数计算)。暴露条件(时间和沉积物的存在/不存在)似乎对得出Cd和Cu的金属CBR值有影响,而与Cr无关。因此,金属的CBR方法很复杂,并且组织残留-毒性关系目前还不能直接应用。

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