Milliken C E, Meier G P, Watts J E M, Sowers K R, May H D
Department of Microbiology and Immunology, Medical University of South Carolina, Charleston, South Carolina 29425-2230, USA.
Appl Environ Microbiol. 2004 Jan;70(1):385-92. doi: 10.1128/AEM.70.1.385-392.2004.
The synthesis and degradation of anthropogenic and natural organohalides are the basis of a global halogen cycle. Chlorinated hydroquinone metabolites (CHMs) synthesized by basidiomycete fungi and present in wetland and forest soil are constituents of that cycle. Anaerobic dehalogenating bacteria coexist with basidiomycete fungi in soils and sediments, but little is known about the fate of these halogenated fungal compounds. In sediment microcosms, the CHMs 2,3,5,6-tetrachloro-1,4-dimethoxybenzene and 2,3,5,6-tetrachloro-4-methoxyphenol (TCMP) were anaerobically demethylated to tetrachlorohydroquinone (TCHQ). Subsequently, TCHQ was converted to trichlorohydroquinone and 2,5-dichlorohydroquinone (2,5-DCHQ) in freshwater and estuarine enrichment cultures. Screening of several dehalogenating bacteria revealed that Desulfitobacterium hafniense strains DCB2 and PCP1, Desulfitobacterium chlororespirans strain Co23, and Desulfitobacterium dehalogenans JW/DU1 sequentially dechlorinate TCMP to 2,3,5-trichloro-4-methoxyphenol and 3,5-dichloro-4-methoxyphenol (3,5-DCMP). After a lag, these strains demethylate 3,5-DCMP to 2,6-DCHQ, which is then completely dechlorinated to 1,4-dihydroquinone (HQ). 2,5-DCHQ accumulated as an intermediate during the dechlorination of TCHQ to HQ by the TCMP-degrading desulfitobacteria. HQ accumulation following TCMP or TCHQ dechlorination was transient and became undetectable after 14 days, which suggests mineralization of the fungal compounds. This is the first report on the anaerobic degradation of fungal CHMs, and it establishes a fundamental role for microbial reductive degradation of natural organochlorides in the global halogen cycle.
人为和天然有机卤化物的合成与降解是全球卤素循环的基础。担子菌纲真菌合成并存在于湿地和森林土壤中的氯代对苯二酚代谢物(CHMs)是该循环的组成部分。厌氧脱卤细菌与担子菌纲真菌共存于土壤和沉积物中,但对于这些卤代真菌化合物的归宿知之甚少。在沉积物微观世界中,CHMs 2,3,5,6-四氯-1,4-二甲氧基苯和2,3,5,6-四氯-4-甲氧基苯酚(TCMP)在厌氧条件下被脱甲基化为四氯对苯二酚(TCHQ)。随后,TCHQ在淡水和河口富集培养物中转化为三氯对苯二酚和2,5-二氯对苯二酚(2,5-DCHQ)。对几种脱卤细菌的筛选表明,哈氏脱硫肠杆菌菌株DCB2和PCP1、氯呼吸脱硫肠杆菌菌株Co23以及脱卤脱硫肠杆菌JW/DU1依次将TCMP脱氯为2,3,5-三氯-4-甲氧基苯酚和3,5-二氯-4-甲氧基苯酚(3,5-DCMP)。经过一段滞后期后,这些菌株将3,5-DCMP脱甲基化为2,6-DCHQ,然后2,6-DCHQ被完全脱氯为1,4-二氢醌(HQ)。在TCMP降解脱硫肠杆菌将TCHQ脱氯为HQ的过程中,2,5-DCHQ作为中间产物积累。TCMP或TCHQ脱氯后HQ的积累是短暂的,14天后就检测不到了,这表明真菌化合物发生了矿化。这是关于真菌CHMs厌氧降解的首次报道,它确立了微生物对天然有机氯化物的还原降解在全球卤素循环中的基本作用。