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Oxygen and Chlorine Isotopic Fractionation during Perchlorate Biodegradatipn: Laboratory Results and Implications for Forensics and Natural Attenuation Studies

机译:高氯酸盐生物降解过程中的氧和氯同位素分馏:实验室结果及法医学和自然衰减研究的意义

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Perchlorate is a widespread environmental contaminant having both anthropogenic and natural sources. Stable isotope ratios of O and Cl in a given sample of perchlorate may be used to distinguish its source(s). Isotopic ratios may also be useful for identifying the extent of biodegradation of perchlorate, which is critical for assessing natural attenuation of this contaminant in groundwater. For this approach to be useful, however, the kinetic isotopic fractionations of O and Cl during perchlorate biodegradation must first be determined as a function of environmental variables such as temperature and bacterial species. A laboratory study was performed in which the O and Cl isotope ratios of perchlorate were monitored as a function of degradation by two separate bacterial strains (Azospira suillum JPLRND and Dechlorospirillum sp. FBR2) at both 10℃ and 22℃ with acetate as the electron donor. Perchlorate was completely reduced by both strains within 280 h at 22℃ and 615 h at 10℃. Measured values of isotopic fractionation factors were ε~(18)O = -36.6 to -29.0% and ε~(37)Cl = -14.5 to -11.5per thousand, and these showed no apparent systematic variation with either temperature or bacterial strain. An experiment using ~(18)O-enriched water < δ~(18)O = +198per thousand) gave results indistinguishable from those observed in the isotopically normal water (δ~(18)O = —8.1per thousand) used in the other experiments, indicating negligible isotope exchange between perchlorate and water during biodegradation. The fractionation factor ratio ε~(18)O/ε~(37)Cl was nearly invariant in all experiments at 2.50 ± 0.04. These data indicate that isotope ratio analysis will be useful for documenting perchlorate biodegradation in soils and groundwater. The establishment of a microbial fractionation factor ratio (ε~(18)O/ ε~(37)Cl) also has significant implications for forensic studies.
机译:高氯酸盐是一种具有人为和自然来源的广泛环境污染物。给定高氯酸盐样品中O和Cl的稳定同位素比可用于区分其来源。同位素比对于确定高氯酸盐的生物降解程度也可能有用,这对于评估地下水中这种污染物的自然衰减至关重要。然而,为了使这种方法有用,必须首先根据环境变量(例如温度和细菌种类)确定高氯酸盐生物降解过程中O和Cl的动力学同位素分馏。进行了一项实验室研究,其中在10℃和22℃下使用醋酸盐作为电子供体,通过两个单独的细菌菌株(水生细螺旋藻JPLRND和Dechlorospirillum sp。FBR2)监测高氯酸盐的O和Cl同位素比作为降解的函数。 。两种菌株在22℃下280 h和10℃下615 h都将高氯酸盐完全还原。同位素分馏因子的测量值为ε〜(18)O = -36.6至-29.0%和ε〜(37)Cl = -14.5至-11.5 /千,无论温度或细菌菌株均无明显系统变化。使用〜(18)O富水<δ〜(18)O = + 198 /千的实验得出的结果与在同位素中使用的同位素正常水(δ〜(18)O = -8.1 /千)所观察到的结果没有区别。其他实验表明,在生物降解过程中高氯酸盐和水之间的同位素交换可忽略不计。在所有实验中,分馏因子比ε〜(18)O /ε〜(37)Cl几乎不变,为2.50±0.04。这些数据表明同位素比分析将有助于记录土壤和地下水中高氯酸盐的生物降解。微生物分离因子比(ε〜(18)O /ε〜(37)Cl)的建立对法医研究也具有重要意义。

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