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Bioassay-directed fractionation and chemical identification of mutagens in bioremediated soils.

机译:生物测定法指导的分馏和生物鉴定土壤中诱变剂的化学鉴定。

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摘要

Soil from a Superfund site (Reilly Tar Site, St. Louis Park, Minnesota) contaminated with polycyclic aromatic hydrocarbons (PAHs) from creosote was treated with several bioremediation technologies including bioslurry (BS), biopile (BP), compost (CMP), and land treatment (LT). These treatment technologies are being evaluated in pilot scale laboratory systems by the U.S. Environmental Protection Agency's National Risk Management Research Laboratory in Cincinnati, Ohio. To evaluate the genotoxicity and identify the mutagens in the soil before and after the various treatments, fractionated extracts of five soils were bioassayed for mutagenic activity with a microsuspension modification of the Salmonella histidine reversion assay. Soils were extracted by sonication using dichloromethane (DCM). The five extracts were fractionated in triplicate (two for bioassay and one for chemical analysis) by reverse-phase high-performance liquid chromatography (HPLC) using hexane/DCM/methanol, and the fraction for bioassay were solvent-exchanged into dimethyl sulfoxide by nitrogen evaporation. Forty HPLC fractions for each sample were bioassayed in strain YG1041 with and without exogenous liver metabolic activation. As shown in a companion paper, the mutagenicity of two treatments (BS and BP) was significantly greater than the mutagenicity of the untreated soil. Mutagenic fractions (> 500 revertants) were analyzed by gas chromatography/mass spectrometry (GC/MS). PAH analysis of the soils indicated that all treatments were effective in reducing the total PAH concentration (48-74%). Qualitative GC/MS analysis of the mutagenic fractions from the BS and BP treatments indicated that they contained azaarenes, which are mutagens. The CMP and LT processes were the most effective and least toxic bioremediation procedures based on mutagenic potency and chemical analysis. This research demonstrated that the combination of bioassays and chemical analysis provided a more accurate determination of toxicity in these complex environmental mixtures.
机译:来自超级基金站点(明尼苏达州圣路易斯公园的Reilly Tar站点,明尼苏达州)的土壤被杂酚油污染了多环芳烃,并采用了多种生物修复技术,包括生物浆(BS),生物堆(BP),堆肥(CMP)和土地处理(LT)。这些处理技术正在美国环境保护局位于俄亥俄州辛辛那提市的国家风险管理研究实验室的中试规模实验室系统中进行评估。为了评估遗传毒性并在各种处理之前和之后鉴定土壤中的诱变剂,对生物体的五个土壤的分级提取物进行了沙门氏菌组氨酸还原测定的微悬浮修饰生物诱变活性分析。使用二氯甲烷(DCM)通过超声处理提取土壤。使用己烷/ DCM /甲醇,通过反相高效液相色谱(HPLC)将五种提取物一式三份分馏(两份用于生物分析,一份用于化学分析),然后用氮气将用于生物分析的馏分溶剂交换为二甲亚砜。蒸发。在有和没有外源性肝代谢活化的情况下,在菌株YG1041中对每个样品的40个HPLC级分进行生物测定。如随附文件所示,两种处理(BS和BP)的致突变性均显着大于未处理土壤的致突变性。通过气相色谱/质谱法(GC / MS)分析诱变级分(> 500个回复体)。对土壤的PAH分析表明,所有处理均有效降低了总PAH浓度(48-74%)。对来自BS和BP处理的诱变级分的定性GC / MS分析表明,它们含有氮杂芳烃,它们是诱变剂。基于致突变力和化学分析,CMP和LT工艺是最有效,毒性最低的生物修复程序。这项研究表明,生物测定法与化学分析法的结合可以更准确地测定这些复杂环境混合物中的毒性。

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