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Experimental modeling of the acute toxicity and cytogenotoxic fate of composite mixtures of chromate copper and arsenate oxides associated with CCA preservative using Clarias gariepinus (Burchell 1822)

机译:使用Clarias gariepinus(Burchell 1822)对铬酸盐铜和砷酸盐氧化物与CCA防腐剂相关的混合物进行急性毒性和细胞遗传毒性的实验模型

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摘要

Concurrent occurrence of chromium (Cr), copper (Cu) and arsenic (As) from chromated copper arsenate (CCA) wood preservative in aquatic ecosystems demands that their joint-actions in eliciting toxic effects be assessed for adequate understanding of the health risk they may pose to biota. was exposed to As O , CrO and CuO and their composite mixtures (1:1 and 1:1:1) at various concentrations (0 – 600 mg/L) for 96-h to determine the acute toxicity using OECD (1992) protocol. was then exposed to sub-lethal concentrations corresponding to 6.25, 12.5, 25.0, 50.0 and 100% of the 96-h LC for 7 days to assess the cytogenotoxic effects using piscine micronucleus (MN) test. The 96-h LC showed that the metals/metalloid demonstrated differential interactions in a concentration dependent pattern. The 96-h LC showed that Cr was the most toxic while Cu and As:Cu were indeterminate (Cr > Cr:Cu > As:Cr > As > As:Cr:Cu > Cu = As:Cu indeterminate). Isobologram and synergistic ratio (SR) models predicted antagonistic interaction between Cu:Cr and As:Cr and synergism between As:Cu in the causation of morbidity and mortality of . Interaction factor model predicted antagonism as common interactive mechanism among the metal/metalloid mixtures in the induction of MN and abnormal nuclear erythrocytes in . Predicted interactions among the three metals/ metalloid were largely antagonism and synergism towards the induction of acute toxicity and cytogenotoxicity. The models employed herein may be useful in establishing environmental safe limits for mixtures of metals/metalloids against the induction of acute toxicity and DNA damage in lower aquatic vertebrates.
机译:在水生生态系统中从铬化砷酸铜(CCA)木材防腐剂中同时出现铬(Cr),铜(Cu)和砷(As)要求评估它们在引发毒性作用中的共同作用,以充分了解它们可能带来的健康风险对生物群构成。使用OECD(1992)规程将其暴露于不同浓度(0 – 600 mg / L)的As O,CrO和CuO及其复合混合物(1:1和1:1:1)中96小时,以确定急性毒性。然后将其暴露于相当于96小时液相色谱法的6.25、12.5、25.0、50.0和100%的亚致死浓度下7天,以使用鱼微核(MN)测试评估细胞遗传毒性作用。 96小时液相色谱显示,金属/准金属以浓度依赖性模式表现出不同的相互作用。 96小时液相色谱显示Cr最具毒性,而Cu和As:Cu不确定(Cr> Cr:Cu> As:Cr> As> As:Cr:Cu> Cu = As:Cu不确定)。等效线图和协同比(SR)模型预测了Cu:Cr和As:Cr之间的拮抗作用以及As:Cu之间的协同作用,导致了发病率和死亡率。相互作用因子模型预测拮抗是金属/类金属混合物诱导MN和异常核红细胞共同相互作用的机制。三种金属/准金属之间的预测相互作用主要是对诱导急性毒性和细胞遗传毒性的拮抗作用和协同作用。本文采用的模型可用于建立金属/准金属混合物的环境安全极限,以防止在低级水生脊椎动物中引起急性毒性和DNA损伤。

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