State Key Laboratory of Pollution Control and Resource Reuse, College of Environmental Science and Engineering, Tongji University, Shanghai 200092, China; Key Laboratory of Yangtze River Water Environment, Ministry of Education, Tongji University, Shanghai 200092, China.
Rays Computational Intelligence Laboratory, Beijing Inteliway Environmental Science & Technology, Ltd., Beijing 100191, China.
Water Res. 2021 Oct 1;204:117567. doi: 10.1016/j.watres.2021.117567. Epub 2021 Aug 15.
Effluent organic matter (EfOM) from wastewater treatment plants (WWTP) constitutes an important source of dissolved organic matter in receiving waters. Photodegradation may alter the properties of WWTP EfOM, thereby impacting its biodegradability and microbial respiration. However, whether and how natural sunlight exposure of EfOM affects its biodegradability and microbial oxygen consumption in the receiving waters are unclear. To address these knowledge gaps, incubation experiments of biodegradation, photodegradation, and bio-photodegradation were conducted with the effluent samples from a tertiary WWTP in Heifei, China. The quantity and quality of the EfOM were examined during the incubations to interpret changes in its lability and composition. The results showed that photodegradation facilitated and accelerated the EfOM biodegradation. After natural sunlight exposure, the EfOM degradation rate was significantly enhanced from 0.004 d to 0.065 d measured by dissolved organic carbon (DOC). Correspondingly, the DOC concentration of EfOM was reduced by 64.2% (26.6% by photodegradation and 37.5% by bio-photodegradation), while the concentration was only reduced by 5.3% in the direct biodegradation. Sunlight exposure of EfOM resulted in lower molecular weight, less aromatic, lower humified, more bleached photoproducts. These substances could be readily metabolized by the native microbial community in the receiving water, stimulating microbial respiration. Correspondingly, the oxygen consumption rate of EfOM increased from almost 0.11 mg L d in the direct biodegradation to 2.17 mg L d in the bio-photodegradation. This study highlights that after EfOM is discharged to the receiving water, its post-processing by sunlight can enhance biodegradability. The existence of the coupled photochemical and biological process is suggested to be considered when determining EfOM fate and managing effluent discharge in receiving waters.
污水处理厂(WWTP)的出水有机物(EfOM)是受纳水体中溶解有机物的重要来源。光降解可能会改变 WWTP EfOM 的性质,从而影响其可生物降解性和微生物呼吸。然而,EfOM 受自然阳光照射后是否以及如何影响受纳水体中的可生物降解性和微生物耗氧量尚不清楚。为了解决这些知识空白,在中国合肥的一个三级 WWTP 进行了 EfOM 的生物降解、光降解和生物-光降解的培养实验。在培养过程中检查了 EfOM 的数量和质量,以解释其不稳定性和组成的变化。结果表明,光降解促进并加速了 EfOM 的生物降解。在自然阳光照射后,EfOM 的降解率从通过溶解有机碳(DOC)测量的 0.004 d 显著提高到 0.065 d。相应地,EfOM 的 DOC 浓度降低了 64.2%(光降解降低了 26.6%,生物-光降解降低了 37.5%),而直接生物降解只降低了 5.3%。EfOM 暴露于阳光下会产生分子量更低、芳香度更低、腐殖化程度更低、漂白程度更高的光产物。这些物质可以被受纳水体中原生微生物群落轻易代谢,刺激微生物呼吸。相应地,EfOM 的耗氧率从直接生物降解中的几乎 0.11 mg L d 增加到生物-光降解中的 2.17 mg L d。本研究强调,EfOM 排放到受纳水体后,阳光的后处理可以提高其可生物降解性。在确定 EfOM 归宿和管理受纳水体中的污水排放时,建议考虑到光化学和生物过程的耦合。