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Effects of Ferric Oxyhydroxide on Anaerobic Microbial Dechlorination of Polychlorinated Biphenyls in Hudson and Grasse River Sediment Microcosms: Dechlorination Extent Preferences Ortho Removal and Its Enhancement

机译:羟基氧化铁对哈德逊河和格拉斯河沉积物缩影中多氯联苯厌氧微生物脱氯的影响:脱氯程度偏好邻位去除及其增强

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摘要

Microbial reductive dechlorination of polychlorinated biphenyls (PCBs) has been observed in many PCB-impacted sediments. However, this biodegradation is relatively site-specific and can be affected by PCB compositions and sediment geochemical conditions. To better understand the influence of a common competing electron acceptor, ferric oxyhydroxide (FeOOH), on dechlorination, two sediments (Hudson River and Grasse River sediments), and two PCB mixtures (PCB 5/12, 64/71, 105/114, and 149/153/170 in Mixture 1 and PCB 5/12, 64/71, 82/97/99, 144/170 in Mixture 2) were used for this microcosm study. The addition of 40 mmole/kg FeOOH completely inhibited PCB dechlorination in the Hudson sediment, but only moderately inhibited PCB dechlorination in the Grasse sediment with a 3-week longer lag time. The inhibitory effect in the Grasse sediment was mainly due to the loss of unflanked para dechlorination activity. Fe(II) analysis showed that dechlorination started prior to the consumption of Fe(III), which indicates PCB reduction and Fe(III) reduction were able to take place concurrently. Dehalococcoides 16S rRNA genes increased with the commencement of dechlorination in the Grasse sediment, but not in the completely inhibited Hudson sediment. Rare ortho dechlorination pathways were identified in FeOOH-amended Grasse sediment microcosms, dominated by transformations of PCB 25(24-3-CB) to PCB 13(3-4-CB) and PCB 28(24-4-CB) to PCB 15(4-4-CB). The addition of carbon sources (acetate or a fatty acid mixture with acetate, propionate, and butyrate) after 27 weeks of incubation reinitiated dechlorination in FeOOH-amended Hudson sediment microcosms. Also, the addition of carbon sources greatly enhanced ortho dechlorination in FeOOH-amended Grasse microcosms, indicating the utilization of acetate and/or the fatty acid mixture for ortho dechlorination-related microorganisms. A dechlorination pathway analysis approach revealed that para-flanked meta dechlorination was primarily preferred followed by ortho-/double-flanked meta dechlorination and single-/double-flanked para dechlorination in the Grasse sediment.
机译:在许多多氯联苯影响的沉积物中已观察到多氯联苯(PCBs)的微生物还原脱氯。但是,这种生物降解是相对特定于地点的,并且会受到PCB成分和沉积物地球化学条件的影响。为了更好地理解常见的竞争性电子受体羟基氧化铁(FeOOH)对脱氯,两种沉积物(哈德逊河和格拉斯河沉积物)和两种PCB混合物(PCB 5 / 12、64 / 71、105 / 114,混合物1中的149/153/170和混合物2中的PCB 5 / 12、64 / 71、82 / 97 / 99、144 / 170)用于此微观研究。添加40 mmole / kg FeOOH可以完全抑制Hudson沉积物中的PCB脱氯,但仅适度抑制格拉斯沉积物中的PCB脱氯,且延迟时间延长3周。对格拉斯沉积物的抑制作用主要是由于失去了侧翼的对氯脱氯活性。 Fe(II)分析表明脱氯是在消耗Fe(III)之前开始的,这表明PCB还原和Fe(III)还原能够同时发生。 Dehalococcoides 16S rRNA基因随着格拉斯沉积物中脱氯作用的开始而增加,但在完全抑制的哈德逊沉积物中却没有。在FeOOH修正的Grasse沉积物微观世界中确定了罕见的邻位脱氯途径,主要是将PCB 25(24-3-CB)转化为PCB 13(3-4-CB)和PCB 28(24-4-CB)转化为PCB 15 (4-4-CB)。孵育27周后,添加碳源(乙酸盐或与乙酸盐,丙酸和丁酸的脂肪酸混合物)会在FeOOH修正的哈德逊沉积物缩微缩图中重新开始脱氯。而且,碳源的添加大大增强了经FeOOH修正的Grasse微观世界的邻位脱氯,表明乙酸盐和/或脂肪酸混合物可用于邻位脱氯相关的微生物。脱氯途径分析方法表明,在格拉斯沉积物中,主要优选对位偏侧脱氯,其次是邻/双侧偏脱氯和单/双侧对脱氯。

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