Kharey Gurpreet S, Palace Vince, Whyte Lyle, Greer Charles W
Department of Natural Resource Sciences, McGill University, 21111 Lakeshore Rd Ste-Anne-de-Bellevue, Quebec, H9X 3V9, Canada.
International Institute for Sustainable Development - Experimental Lakes Area, Pine Rd, Kenora, Unorganized Ontario, P0V 2V0, Canada.
FEMS Microbiol Ecol. 2024 Apr 10;100(5). doi: 10.1093/femsec/fiae055.
With the increase in crude oil transport throughout Canada, the potential for spills into freshwater ecosystems has increased and additional research is needed in these sensitive environments. Large enclosures erected in a lake were used as mesocosms for this controlled experimental dilbit (diluted bitumen) spill under ambient environmental conditions. The microbial response to dilbit, the efficacy of standard remediation protocols on different shoreline types commonly found in Canadian freshwater lakes, including a testing of a shoreline washing agent were all evaluated. We found that the native microbial community did not undergo any significant shifts in composition after exposure to dilbit or the ensuing remediation treatments. Regardless of the treatment, sample type (soil, sediment, or water), or type of associated shoreline, the community remained relatively consistent over a 3-month monitoring period. Following this, metagenomic analysis of polycyclic aromatic and alkane hydrocarbon degradation mechanisms also showed that while many key genes identified in PAH and alkane biodegradation were present, their abundance did not change significantly over the course of the experiment. These results showed that the native microbial community present in a pristine freshwater lake has the prerequisite mechanisms for hydrocarbon degradation in place, and combined with standard remediation practices in use in Canada, has the genetic potential and resilience to potentially undertake bioremediation.
随着加拿大原油运输量的增加,原油泄漏到淡水生态系统的可能性增大,因此需要在这些敏感环境中开展更多研究。在一个湖泊中搭建大型围隔作为中宇宙,用于在环境条件下进行此次受控的实验性稀释沥青泄漏模拟。评估了微生物对稀释沥青的反应、标准修复方案对加拿大淡水湖泊常见的不同类型湖岸线的修复效果,包括对一种湖岸清洗剂的测试。我们发现,原生微生物群落暴露于稀释沥青或后续的修复处理后,其组成没有发生任何显著变化。无论处理方式、样本类型(土壤、沉积物或水)或相关湖岸线类型如何,在为期3个月的监测期内,群落保持相对稳定。在此之后,对多环芳烃和烷烃降解机制的宏基因组分析还表明,虽然在多环芳烃和烷烃生物降解中鉴定出的许多关键基因都存在,但在实验过程中它们的丰度没有显著变化。这些结果表明,原始淡水湖泊中的原生微生物群落具备进行碳氢化合物降解的先决机制,结合加拿大现行的标准修复措施,具有进行生物修复的遗传潜力和恢复力。