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Metal oxides and annealed metals as alternatives to metal salts for fixed-ratio metal mixture ecotoxicity tests in soil

机译:金属氧化物和退火金属作为金属盐的替代品,用于固定比金属混合物生态毒性试验土壤中

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In soil metal ecotoxicology research, dosing is usually performed with metal salts, followed by leaching to remove excess salinity. This process also removes some metals, affecting metal mixture ratios as different metals are removed by leaching at different rates. Consequently, alternative dosing methods must be considered for fixed ratio metal mixture research. In this study three different metal mixture dosing methods (nitrate, oxide and annealed metal dosing) were examined for metal concentrations and toxicity. In the nitrate metal dosing method leaching reduced total metal retention and was affected by soil pH and cation exchange capacity (CEC). Acidic soils 3.22 (pH 3.4, CEC 8 meq/100g) and WTRS (pH 4.6, CEC 16 meq/100g) lost more than 75 and 64% of their total metals to leaching respectively while Elora (6.7 pH, CEC 21 meq/100g) and KUBC (pH 5.6, CEC 28 meq/100g) with higher pH and CEC only lost 13.6% and 12.2% total metals respectively. Metal losses were highest for Ni, Zn and Co (46.0%, 63.7% and 48.4% metal loss respectively) whereas Pb and Cu (5.6% and 20.0% metal loss respectively) were mostly retained, affecting mixture ratios. Comparatively, oxide and annealed metal dosing which do not require leaching had higher total metal concentrations, closer to nominal doses and maintained better mixture ratios (percent of nominal concentrations for the oxide metal dosing were Pb = 109.9%, Cu = 84.6%, Ni = 101.9%, Zn = 82.3% and Co = 97.8% and for the annealed metal dosing were Pb = 81.7%, Cu = 80.3%, Ni = 100.5%, Zn = 89.2% and Co = 101.3%). Relative to their total metal concentrations, nitrate metal dosing (lowest metal concentrations) was the most toxic followed by metal oxides dosing while the annealed dosing method was generally non-toxic. Due to the lack of toxicity of the annealed metals and their higher dosing effort, metal oxides, are the most appropriate of the tested dosing methods, for fixed-ratio metal mixtures studies with soil invertebrates.
机译:在土壤金属生态毒理学研究中,给药通常用金属盐进行,然后浸出以除去过量的盐度。该方法还除去一些金属,影响金属混合物比例,因为通过以不同的速率浸出来除去不同的金属。因此,必须考虑替代给药方法,用于固定比例的金属混合物研究。在这项研究中,检查了三种不同的金属混合物给药方法(硝酸盐,氧化物和退火金属给药),用于金属浓度和毒性。在硝酸盐金属计量法中,浸出总金属保留并受土壤pH和阳离子交换能力(CEC)的影响。酸性土壤3.22(pH 3.4,CEC 8 Meq / 100g)和WTR(pH 4.6,CEC 16 Meq / 100g)分别在Elora(6.7 pH,CEC 21 Meq / 100g (pH值高的KUBC(pH 5.6,CEC 28 MEQ / 100g)分别损失了13.6%和12.2%的总金属。金属损失对于Ni,Zn和Co(分别为46.0%,63.7%和48.4%金属损失)最高,而Pb和Cu(分别为5.6%和20.0%金属损失)主要保留,影响混合比率。相比之下,不需要浸出的氧化物和退火金属剂量具有更高的总金属浓度,更接近标称剂量,并保持更好的混合比(氧化物金属给药的标称浓度的百分比Pb = 109.9%,Cu = 84.6%,Ni = 101.9%,Zn = 82.3%,Co = 97.8%,对于退火金属剂量为Pb = 81.7%,Cu = 80.3%,Ni = 100.5%,Zn = 89.2%,Co = 101.3%)。相对于它们的总金属浓度,硝酸金属计量(最低金属浓度)是最有毒的,然后是金属氧化物给药,而退火的计量方法通常是无毒的。由于退火金属的毒性缺乏和较高的给药努力,金属氧化物是最合适的测试给药方法,用于固定比金属混合物与土壤无脊椎动物的研究。

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