Department of Environmental Sciences, University of California, Riverside, CA 92521, USA.
Biodegradation. 2011 Apr;22(2):297-307. doi: 10.1007/s10532-010-9399-z. Epub 2010 Aug 18.
Microbial degradation is the dominant pathway for natural attenuation of PAHs in environmental compartments such as sediments, which in turn depends on the bioavailability of PAHs. The bioavailability of PAHs has seldom been studied at the sediment particle size scale. We evaluated biodegradation of pyrene by Mycobacterium vanbaalenii PYR-1 as a function of sediment particle sizes, and investigated the relationship between the rate of degradation on sand, silt and clay particles with their individual desorption kinetics measured with the Tenax extraction method. Regression analysis showed that the total organic carbon (TOC), black carbon (BC), and specific surface area (SSA) of the specific particle size fractions, instead of the particle size scale itself, were closely related (P<0.01) with the mineralization rate. While the fraction in the rapid desorption pool (F (rapid)) ranged from 0.11 to 0.38 for the whole sediments and different size groups, the fractions mineralized after 336-h incubation (0.52 to 0.72) greatly surpassed the F (rapid) values, suggesting utilization of pyrene in the slow desorption pool (F (slow)). A biodegradation model was modified by imbedding a two-phase desorption relationship describing sequential Tenax extractions. Model analysis showed that pyrene sorbed on silt and clay aggregates was directly utilized by the degrading bacteria. The enhanced bioavailability may be attributed to the higher chemical concentration, higher TOC or larger SSA in the silt and clay fractions, which appeared to overcome the reduced bioavailability of pyrene due to sorption, making pyrene on the silt and clay particles readily available to degrading microbes. This conjecture merits further investigation.
微生物降解是环境介质(如沉积物)中多环芳烃自然衰减的主要途径,而这又取决于多环芳烃的生物可利用性。多环芳烃的生物可利用性在沉积物颗粒尺度上很少得到研究。我们评估了分枝杆菌 PYR-1 对苊的生物降解作用作为沉积物颗粒大小的函数,并研究了降解速率与砂、粉砂和粘土颗粒之间的关系,其各自的解吸动力学用 Tenax 提取法测量。回归分析表明,特定颗粒大小分数的总有机碳(TOC)、黑碳(BC)和比表面积(SSA)与矿化率密切相关(P<0.01),而不是颗粒大小本身。虽然整个沉积物和不同大小组的快速解吸池分数(F(rapid))范围为 0.11 到 0.38,但在 336 小时孵育后矿化的分数(0.52 到 0.72)大大超过了 F(rapid)值,表明缓慢解吸池(F(slow))中的苊被利用。通过嵌入描述顺序 Tenax 提取的两相解吸关系,对生物降解模型进行了修改。模型分析表明,被粘粒和粉砂团聚体吸附的苊被降解细菌直接利用。生物可利用性的增强可能归因于粘粒和粉砂分数中较高的化学浓度、较高的 TOC 或较大的 SSA,这似乎克服了由于吸附而导致的苊生物可利用性降低,使粘粒和粉砂颗粒上的苊容易被降解微生物利用。这一推测值得进一步研究。