Boonchan S, Britz M L, Stanley G A
Centre for Bioprocessing and Food Technology, Victoria University of Technology, Werribee Campus, Melbourne, Australia 8001.
Appl Environ Microbiol. 2000 Mar;66(3):1007-19. doi: 10.1128/AEM.66.3.1007-1019.2000.
This study investigated the biodegradation of high-molecular-weight polycyclic aromatic hydrocarbons (PAHs) in liquid media and soil by bacteria (Stenotrophomonas maltophilia VUN 10,010 and bacterial consortium VUN 10,009) and a fungus (Penicillium janthinellum VUO 10, 201) that were isolated from separate creosote- and manufactured-gas plant-contaminated soils. The bacteria could use pyrene as their sole carbon and energy source in a basal salts medium (BSM) and mineralized significant amounts of benzo[a]pyrene cometabolically when pyrene was also present in BSM. P. janthinellum VUO 10,201 could not utilize any high-molecular-weight PAH as sole carbon and energy source but could partially degrade these if cultured in a nutrient broth. Although small amounts of chrysene, benz[a]anthracene, benzo[a]pyrene, and dibenz[a,h]anthracene were degraded by axenic cultures of these isolates in BSM containing a single PAH, such conditions did not support significant microbial growth or PAH mineralization. However, significant degradation of, and microbial growth on, pyrene, chrysene, benz[a]anthracene, benzo[a]pyrene, and dibenz[a,h]anthracene, each as a single PAH in BSM, occurred when P. janthinellum VUO 10,201 and either bacterial consortium VUN 10,009 or S. maltophilia VUN 10,010 were combined in the one culture, i.e., fungal-bacterial cocultures: 25% of the benzo[a]pyrene was mineralized to CO(2) by these cocultures over 49 days, accompanied by transient accumulation and disappearance of intermediates detected by high-pressure liquid chromatography. Inoculation of fungal-bacterial cocultures into PAH-contaminated soil resulted in significantly improved degradation of high-molecular-weight PAHs, benzo[a]pyrene mineralization (53% of added [(14)C]benzo[a]pyrene was recovered as (14)CO(2) in 100 days), and reduction in the mutagenicity of organic soil extracts, compared with the indigenous microbes and soil amended with only axenic inocula.
本研究调查了从分别受杂酚油和人造煤气厂污染的土壤中分离出的细菌(嗜麦芽窄食单胞菌VUN 10,010和细菌联合体VUN 10,009)以及真菌(产黄青霉VUO 10,201)对液体介质和土壤中高分子量多环芳烃(PAHs)的生物降解情况。这些细菌在基础盐培养基(BSM)中能够将芘作为唯一的碳源和能源利用,并且当BSM中同时存在芘时,能够共代谢矿化大量的苯并[a]芘。产黄青霉VUO 10,201不能将任何高分子量PAH作为唯一的碳源和能源利用,但如果在营养肉汤中培养,则能够部分降解这些PAH。尽管在含有单一PAH的BSM中,这些分离菌株的无菌培养物能降解少量的屈、苯并[a]蒽、苯并[a]芘和二苯并[a,h]蒽,但这种条件下微生物生长不显著,PAH矿化也不明显。然而,当产黄青霉VUO 10,201与细菌联合体VUN 10,009或嗜麦芽窄食单胞菌VUN 10,010在同一培养物中混合,即真菌 - 细菌共培养时,在BSM中作为单一PAH存在的芘、屈、苯并[a]蒽、苯并[a]芘和二苯并[a,h]蒽均发生了显著降解且有微生物生长:在49天内,这些共培养物将25%的苯并[a]芘矿化为CO₂,同时高压液相色谱检测到中间产物有短暂积累和消失。与本地微生物以及仅接种无菌菌剂的土壤相比,将真菌 - 细菌共培养物接种到受PAH污染的土壤中,导致高分子量PAHs的降解显著改善,苯并[a]芘矿化(100天内添加的[(14)C]苯并[a]芘中有53%以(14)CO₂形式回收),并且有机土壤提取物的致突变性降低。