College of Natural Resources and Environment, Joint Institute for Environmental Research & Education, South China Agricultural University, Guangzhou, 510642, China.
Department of Civil and Environmental Engineering, University of Maryland at College Park, MD, 20742, USA.
J Environ Manage. 2019 Nov 1;249:109425. doi: 10.1016/j.jenvman.2019.109425. Epub 2019 Aug 22.
In the present study, the biodegradation behaviors of petroleum hydrocarbons under various reducing conditions were investigated. n-Alkanes and polycyclic aromatic hydrocarbons (PAHs) were degraded with NO, Fe, SO, or HCO as terminal electron acceptors (TEAs), which link to four typical reducing conditions (i.e., nitrate-reducing, ferric-reducing, sulfate-reducing and methanogenic conditions, respectively) in sediment. The fastest degradation rates were achieved under sulfate-reducing conditions with half-lives of 49.51 days for n-alkanes and 58.74 days for PAHs. For short-chain n-alkanes and low-molecular weight (LMW) PAHs, relatively higher removal efficiencies were achieved under nitrate- and ferric-reducing conditions. The degradation of long-chain n-alkanes and high-molecular weight (HMW) PAHs coupled to methanogenesis was the most favored as compared with other reducing conditions. Carboxylation was found to be the principle mechanism for regulating n-alkane degradation coupled to denitrification, while the activation of n-alkanes by the addition of fumarate was the principle mechanism for the n-alkane degradation under sulfate-reducing conditions. The anaerobic metabolism of n-alkanes may not proceed via fumarate addition or carboxylation under ferric-reducing and methanogenic conditions. Illumina HiSeq sequencing revealed dissimilar structures of the microbial communities under various reducing conditions. It is hypothesized that the utilization of different TEAs for n-alkane and PAH degradation resulted in distinct microbial community structures, which were highly correlated with the varied degradation behaviors of petroleum hydrocarbons in sediment. The current results may provide reference value on better understanding the biodegradation behaviors of n-alkanes and PAHs in association with the induced microbial communities in sedimentary environments under the four typical reducing conditions.
在本研究中,研究了各种还原条件下石油烃的生物降解行为。正烷烃和多环芳烃(PAHs)在 NO、Fe、SO或 HCO 作为末端电子受体(TEAs)的条件下被降解,这些 TEAs 分别与沉积物中四种典型的还原条件(即硝酸盐还原、铁还原、硫酸盐还原和产甲烷条件)相联系。在硫酸盐还原条件下,正烷烃和 PAHs 的半衰期分别为 49.51 天和 58.74 天,达到了最快的降解速率。对于短链正烷烃和低分子量(LMW)PAHs,在硝酸盐和铁还原条件下实现了相对较高的去除效率。与其他还原条件相比,与产甲烷作用偶联的长链正烷烃和高分子量(HMW)PAHs 的降解是最有利的。发现羧化作用是调控与反硝化作用偶联的正烷烃降解的主要机制,而富马酸盐的添加激活正烷烃是硫酸盐还原条件下正烷烃降解的主要机制。在铁还原和产甲烷条件下,正烷烃的厌氧代谢可能不会通过富马酸盐添加或羧化作用进行。Illumina HiSeq 测序揭示了不同还原条件下微生物群落的不同结构。据推测,不同 TEAs 用于正烷烃和 PAH 降解导致了不同的微生物群落结构,这与沉积物中不同还原条件下石油烃的降解行为密切相关。本研究结果可能为更好地理解与四种典型还原条件下沉积物中诱导的微生物群落相关的正烷烃和 PAHs 的生物降解行为提供参考价值。