Department of Environmental Science (ACES), Stockholm University, 10691 Stockholm, Sweden.
Eawag, Swiss Federal Institute of Aquatic Science and Technology, 8600 Dübendorf, Switzerland.
Environ Sci Technol. 2020 Nov 17;54(22):14380-14392. doi: 10.1021/acs.est.0c04393. Epub 2020 Oct 26.
Assessment of micropollutant biodegradation is essential to determine the persistence of potentially hazardous chemicals in aquatic ecosystems. We studied the dissipation half-lives of 10 micropollutants in sediment-water incubations (based on the OECD 308 standard) with sediment from two European rivers sampled upstream and downstream of wastewater treatment plant (WWTP) discharge. Dissipation half-lives (DT50s) were highly variable between the tested compounds, ranging from 1.5 to 772 days. Sediment from one river sampled downstream from the WWTP showed the fastest dissipation of all micropollutants after sediment RNA normalization. By characterizing sediment bacteria using 16S rRNA sequences, bacterial community composition of a sediment was associated with its capacity for dissipating micropollutants. Bacterial amplicon sequence variants of the genera , , , and , which are known degraders of contaminants, were significantly more abundant in the sediment incubations where fast dissipation was observed. Our study illuminates the limitations of the OECD 308 standard to account for variation of dissipation rates of micropollutants due to differences in bacterial community composition. This limitation is problematic particularly for those compounds with DT50s close to regulatory persistence criteria. Thus, it is essential to consider bacterial community composition as a source of variability in regulatory biodegradation and persistence assessments.
评估微污染物的生物降解对于确定水生生态系统中潜在危险化学品的持久性至关重要。我们研究了 10 种微污染物在沉积物-水孵育中的消解半衰期(基于 OECD308 标准),所用沉积物取自污水处理厂(WWTP)排放口上下游的两条欧洲河流。测试化合物之间的消解半衰期(DT50)差异很大,范围从 1.5 到 772 天。WWTP 下游河流的沉积物在经过 RNA 标准化后,对所有微污染物的消解速度最快。通过使用 16S rRNA 序列对沉积物细菌进行特征描述,发现沉积物细菌群落组成与其消解微污染物的能力有关。属于已知污染物降解菌的属 、 、 、 的细菌扩增子序列变体在快速消解的沉积物孵育中明显更为丰富。本研究揭示了 OECD308 标准在考虑由于细菌群落组成差异导致的微污染物消解速率变化方面的局限性。对于那些 DT50 接近监管持久性标准的化合物,这种局限性尤其成问题。因此,在监管生物降解和持久性评估中,必须将细菌群落组成视为变异性的来源。