Coates J D, Woodward J, Allen J, Philp P, Lovley D R
Department of Microbiology, Southern Illinois University, Carbondale 62901, USA.
Appl Environ Microbiol. 1997 Sep;63(9):3589-93. doi: 10.1128/aem.63.9.3589-3593.1997.
Although polycyclic aromatic hydrocarbons (PAHs) have usually been found to persist under strict anaerobic conditions, in a previous study an unusual site was found in San Diego Bay in which two PAHs, naphthalene and phenanthrene, were oxidized to carbon dioxide under sulfate-reducing conditions. Further investigations with these sediments revealed that methylnaphthalene, fluorene, and fluoranthene were also anaerobically oxidized to carbon dioxide in these sediments, while pyrene and benzo[a]pyrene were not. Studies with naphthalene indicated that PAH oxidation was sulfate dependent. Incubating the sediments with additional naphthalene for 1 month resulted in a significant increase in the oxidation of [14C]naphthalene. In sediments from a less heavily contaminated site in San diego Bay where PAHs were not readily degraded, naphthalene degradation could be stimulated through inoculation with active PAH-degrading sediments from the most heavily contaminated site. Sediments from the less heavily contaminated site that had been adapted for rapid anaerobic degradation of high concentrations of benzene did not oxidize naphthalene, suggesting that the benzene- and naphthalene-degrading populations were different. When fuels containing complex mixtures of alkanes were added to sediments from the two sites, there was significant degradation in the alkanes. [14C]hexadecane was also anaerobically oxidized to 14CO2 in these sediments. Molybdate, a specific inhibitor of sulfate reduction, inhibited hexadecane oxidation. These results demonstrate that a wide variety of hydrocarbon contaminants can be degraded under sulfate-reducing conditions in hydrocarbon-contaminated sediments, and they suggest that it may be possible to use sulfate reduction rather than aerobic respiration as a treatment strategy for hydrocarbon-contaminated dredged sediments.
尽管通常发现多环芳烃(PAHs)在严格的厌氧条件下会持续存在,但在之前的一项研究中,在圣地亚哥湾发现了一个不同寻常的地点,在硫酸盐还原条件下,两种多环芳烃萘和菲被氧化成了二氧化碳。对这些沉积物的进一步研究表明,甲基萘、芴和荧蒽在这些沉积物中也被厌氧氧化成了二氧化碳,而芘和苯并[a]芘则没有。对萘的研究表明,多环芳烃的氧化依赖于硫酸盐。用额外的萘孵育沉积物1个月导致[14C]萘的氧化显著增加。在圣地亚哥湾污染较轻的一个地点的沉积物中,多环芳烃不容易降解,通过接种来自污染最严重地点的活性多环芳烃降解沉积物,可以刺激萘的降解。来自污染较轻地点且已适应高浓度苯快速厌氧降解的沉积物不会氧化萘,这表明降解苯和萘的菌群不同。当将含有复杂烷烃混合物的燃料添加到这两个地点的沉积物中时,烷烃有显著降解。[14C]十六烷在这些沉积物中也被厌氧氧化成了14CO2。钼酸盐是硫酸盐还原的一种特异性抑制剂,它抑制了十六烷的氧化。这些结果表明,在受烃类污染的沉积物中,在硫酸盐还原条件下,多种烃类污染物可以被降解,并且它们表明有可能使用硫酸盐还原而不是有氧呼吸作为处理受烃类污染的疏浚沉积物的一种处理策略。