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本文引用的文献

1
Dehalogenation: a novel pathway for the anaerobic biodegradation of haloaromatic compounds.脱卤作用:卤代芳香族化合物厌氧生物降解的新途径。
Science. 1982 Dec 10;218(4577):1115-7. doi: 10.1126/science.218.4577.1115.
2
Anaerobic biodegradation of 2,4,5-trichlorophenoxyacetic Acid in samples from a methanogenic aquifer: stimulation by short-chain organic acids and alcohols.产甲烷含水层中 2,4,5-三氯苯氧乙酸的厌氧生物降解:短链有机酸和醇的刺激作用。
Appl Environ Microbiol. 1990 Jun;56(6):1825-32. doi: 10.1128/aem.56.6.1825-1832.1990.
3
Reductive dehalogenation of a nitrogen heterocyclic herbicide in anoxic aquifer slurries.在缺氧含水层泥浆中,一种含氮杂环类除草剂的还原脱卤作用。
Appl Environ Microbiol. 1990 Jan;56(1):292-4. doi: 10.1128/aem.56.1.292-294.1990.
4
Anaerobic Degradation of Chloroaromatic Compounds in Aquatic Sediments under a Variety of Enrichment Conditions.在各种富化条件下,水体沉积物中氯代芳烃化合物的厌氧降解。
Appl Environ Microbiol. 1989 Jun;55(6):1466-71. doi: 10.1128/aem.55.6.1466-1471.1989.
5
Isolation and partial characterization of bacteria in an anaerobic consortium that mineralizes 3-chlorobenzoic Acid.在一个能够使 3-氯苯甲酸矿化的厌氧生物群落中分离和部分鉴定细菌。
Appl Environ Microbiol. 1984 Oct;48(4):840-8. doi: 10.1128/aem.48.4.840-848.1984.
6
Reductive dehalogenations of halobenzoates by anaerobic lake sediment microorganisms.厌氧湖底沉积物微生物对卤代苯甲酸的还原脱卤作用。
Appl Environ Microbiol. 1983 May;45(5):1459-65. doi: 10.1128/aem.45.5.1459-1465.1983.
7
Extrapolation of biodegradation results to groundwater aquifers: reductive dehalogenation of aromatic compounds.生物降解结果外推至地下水含水层:芳香族化合物的还原脱卤作用
Appl Environ Microbiol. 1986 Oct;52(4):681-8. doi: 10.1128/aem.52.4.681-688.1986.
8
Microbial metabolism of homocyclic and heterocyclic aromatic compounds under anaerobic conditions.厌氧条件下,同环和杂环芳香族化合物的微生物代谢。
Microbiol Rev. 1987 Mar;51(1):43-59. doi: 10.1128/mr.51.1.43-59.1987.
9
Anaerobic degradation of m-cresol in anoxic aquifer slurries: carboxylation reactions in a sulfate-reducing bacterial enrichment.缺氧含水层泥浆中间甲酚的厌氧降解:硫酸盐还原菌富集培养中的羧化反应
Appl Environ Microbiol. 1991 Jun;57(6):1689-95. doi: 10.1128/aem.57.6.1689-1695.1991.
10
Reductive dechlorination of high concentrations of tetrachloroethene to ethene by an anaerobic enrichment culture in the absence of methanogenesis.在不发生甲烷生成的情况下,通过厌氧富集培养将高浓度四氯乙烯还原脱氯为乙烯。
Appl Environ Microbiol. 1991 Aug;57(8):2287-92. doi: 10.1128/aem.57.8.2287-2292.1991.

脒类除草剂绿麦隆的还原脱氯。

Reductive dechlorination of the nitrogen heterocyclic herbicide picloram.

机构信息

Department of Botany and Microbiology and Department of Chemistry and Biochemistry, The University of Oklahoma, Norman, Oklahoma 73019.

出版信息

Appl Environ Microbiol. 1993 Jul;59(7):2251-6. doi: 10.1128/aem.59.7.2251-2256.1993.

DOI:10.1128/aem.59.7.2251-2256.1993
PMID:16348997
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC182265/
Abstract

The anaerobic biodegradation of picloram (3,5,6-trichloro-4-amino-2-pyridinecarboxylic acid) in freshwater sediment was favored under methanogenic conditions but not when sulfate or nitrate was available as a terminal electron acceptor. Under the former conditions, more than 85% of the parent substrate (340 muM) was removed from nonsterile incubations in 30 days, following a 50-day acclimation period. Concomitant with substrate decay, an intermediate transiently accumulated in the sediment slurries. By liquid chromatography-mass spectrometry, the intermediate was identified as an isomer of dichloro-4-amino-2-pyridinecarboxylic acid. Proton nuclear magnetic resonance evidence suggested that a chlorine was reductively removed from the parent substrate at the position meta to the nitrogen heteroatom. Upon continued incubation, the dechlorinated product was transformed into an unidentified compound which accumulated and resisted further decay. The addition of sulfate or bromoethanesulfonic acid to sediment slurries inhibited picloram dehalogenation, but molybdate reversed the inhibitory effect of sulfate on pesticide metabolism. These findings help clarify the fate of a halogenated nitrogen heterocyclic herbicide in anaerobic environments.

摘要

在产甲烷条件下, picloram(3,5,6-三氯-4-氨基-2-吡啶羧酸)在淡水沉积物中的厌氧生物降解得到促进,但在硫酸盐或硝酸盐可用作末端电子受体时则不然。在前一种情况下,在 50 天的适应期后,30 天内未灭菌培养物中超过 85%的母体基质(340 μM)被去除。伴随着基质的衰减,一种中间产物在沉积物悬浮液中短暂积累。通过液相色谱-质谱联用仪,鉴定出中间产物是二氯-4-氨基-2-吡啶羧酸的异构体。质子核磁共振证据表明,母体底物上位于氮杂原子间位的氯被还原去除。随着进一步的孵育,脱氯产物被转化为一种未知的化合物,该化合物积累并抵制进一步降解。向沉积物悬浮液中添加硫酸盐或溴乙磺酸盐会抑制 picloram 脱卤,但钼酸盐会逆转硫酸盐对农药代谢的抑制作用。这些发现有助于阐明卤代含氮杂环除草剂在厌氧环境中的命运。