Bauer J E, Capone D G
Chesapeake Biological Laboratory, University of Maryland, Solomons 20688-0038.
Appl Environ Microbiol. 1988 Jul;54(7):1649-55. doi: 10.1128/aem.54.7.1649-1655.1988.
Rates of polycyclic aromatic hydrocarbon (PAH) degradation and mineralization were influenced by preexposure to alternate PAHs and a monoaromatic hydrocarbon at relatively high (100 ppm) concentrations in organic-rich aerobic marine sediments. Prior exposure to three PAHs and benzene resulted in enhanced [14C]naphthalene mineralization, while [14C]anthracene mineralization was stimulated only by benzene and anthracene preexposure. Preexposure of sediment slurries to phenanthrene stimulated the initial degradation of anthracene. Prior exposure to naphthalene stimulated the initial degradation of phenanthrene but had no effect on either the initial degradation or mineralization of anthracene. For those compounds which stimulated [14C]anthracene or [14C]naphthalene mineralization, longer preexposures (2 weeks) to alternative aromatic hydrocarbons resulted in an even greater stimulation response. Enrichment with individual PAHs followed by subsequent incubation with one or two PAHs showed no alteration in degradation patterns due to the simultaneous presence of PAHs. The evidence suggests that exposure of marine sediments to a particular PAH or benzene results in the enhanced ability of these sediments to subsequently degrade that PAH as well as certain other PAHs. The enhanced degradation of a particular PAH after sediments have been exposed to it may result from the selection and proliferation of specific microbial populations capable of degrading it. The enhanced degradation of other PAHs after exposure to a single PAH suggests that the populations selected have either broad specificity for PAHs, common pathways of PAH degradation, or both.
在富含有机物的需氧海洋沉积物中,多环芳烃(PAH)的降解和矿化速率受到先前暴露于相对高浓度(100 ppm)的替代PAH和单环芳烃的影响。先前暴露于三种PAH和苯导致[14C]萘矿化增强,而[14C]蒽矿化仅受到苯和蒽预先暴露的刺激。沉积物浆液预先暴露于菲刺激了蒽的初始降解。先前暴露于萘刺激了菲的初始降解,但对蒽的初始降解或矿化均无影响。对于那些刺激[14C]蒽或[14C]萘矿化的化合物,更长时间(2周)暴露于替代芳烃会导致更大的刺激反应。用单个PAH进行富集,随后与一种或两种PAH一起孵育,结果表明由于PAH的同时存在,降解模式没有改变。证据表明,海洋沉积物暴露于特定的PAH或苯会导致这些沉积物随后降解该PAH以及某些其他PAH的能力增强。沉积物暴露于特定PAH后其降解增强可能是由于能够降解它的特定微生物种群的选择和增殖。暴露于单一PAH后其他PAH的降解增强表明所选择的种群对PAH具有广泛的特异性、PAH降解的共同途径或两者兼而有之。