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Influence of sample matrix on the alkaline extraction of Cr(VI) in soils and industrial materials

机译:样品基质对土壤和工业材料中Cr(VI)碱萃取的影响

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An accurate and efficient determination of the highly toxic Cr(VI) in solid materials is important to determine the total Cr(VI) inventory of contaminated sites and the Cr(VI) release potential from such sites into the environment. Most commonly, total Cr(VI) is extracted from solid materials following a hot alkaline extraction procedure (US EPA method 3060A) where a complete release of water-extractable and sparingly soluble Cr(VI) phase is achieved. This work presents an evaluation of matrix effects that may occur during the hot alkaline extraction and in the determination of the total Cr(VI) inventory of variably composed contaminated soils and industrial materials (cement, fly ash) and is compared to water-extractable Cr(VI) results. Method validation including multiple extractions and matrix spiking along with chemical and mineralogical characterization showed satisfying results for total Cr(VI) contents for most of the tested materials. However, unreliable results were obtained by applying method 3060A to anoxic soils due to the degradation of organic material and/or reactions with Fe2+-bearing mineral phases. In addition, in certain samples discrepant spike recoveries have to be also attributed to sample heterogeneity. Separation of possible extracted Cr(III) by applying cation-exchange cartridges prior to solution analysis further shows that under the hot alkaline extraction conditions only Cr(VI) is present in solution in measurable amounts, whereas Cr(III) gets precipitated as amorphous Cr(OH) 3(am). It is concluded that prior to routine application of method 3060A to a new material type, spiking tests are recommended for the identification of matrix effects. In addition, the mass of extracted solid material should to be well adjusted to the heterogeneity of the Cr(VI) distribution in the material in question.
机译:准确有效地确定固体材料中剧毒的Cr(VI)对于确定受污染场所的总Cr(VI)库存以及从此类场所释放到环境中的Cr(VI)潜力很重要。最常见的是,按照热碱萃取程序(US EPA方法3060A)从固体材料中萃取出总Cr(VI),可完全释放水可萃取和微溶的Cr(VI)相。这项工作提出了在热碱萃取过程中以及确定各种组成的受污染土壤和工业材料(水泥,粉煤灰)的总Cr(VI)存量时可能发生的基质效应的评估,并将其与可水萃取的Cr进行了比较。 (六)结果。方法验证包括多次萃取和基质加标以及化学和矿物学表征,结果表明,大多数被测材料的总Cr(VI)含量令人满意。但是,由于有机材料的降解和/或与含Fe2 +的矿物相的反应,将方法3060A应用于缺氧土壤无法获得可靠的结果。另外,在某些样品中,不同的加标回收率也必须归因于样品的异质性。在溶液分析之前通过应用阳离子交换柱分离可能的萃取出的Cr(III)进一步表明,在热碱萃取条件下,溶液中仅存在可测量量的Cr(VI),而Cr(III)则以非晶态Cr的形式沉淀(OH)3(上午)。结论是,在将方法3060A常规应用到新材料类型之前,建议使用尖峰测试来识别基体效应。此外,提取的固体材料的质量应适当调整,以适应所讨论材料中Cr(VI)分布的不均匀性。

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