4.6 Article

Fate of four Different Classes of Chemicals Under Aerobic and Anaerobic Conditions in Biological Wastewater Treatment

Journal

FRONTIERS IN ENVIRONMENTAL SCIENCE
Volume 9, Issue -, Pages -

Publisher

FRONTIERS MEDIA SA
DOI: 10.3389/fenvs.2021.700245

Keywords

environmental fate; biodegradation; micropollutants; wastewater treatment; effluent quality prediction

Funding

  1. Engineering and Physical Science Research Council (EPSRC) [EP/I025782/1]

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The study investigated the removal mechanisms and degradation rates of 28 chemicals in different biological treatment systems, finding that biodegradation was the main removal mechanism in activated sludge and WSP WWTPs. Photodegradation of the chemicals was also observed, with estrogens degrading faster under light conditions while triclosan degraded faster in the dark. All chemicals were resistant to anaerobic degradation with UASB sludge. Importantly, the predicted effluent concentrations based on the degradation rates showed good agreement with measured effluent concentrations from a previous study.
The removal mechanisms and extent of degradation of 28 chemicals (triclosan, fifteen polycyclic aromatic hydrocarbons, four estrogens, and eight polybrominated diphenyl ether congeners) in different biological treatment systems [activated sludge, up-flow anaerobic sludge blanket reactor (UASB) and waste stabilization pond (WSP)] was investigated to provide insights into the limits of engineered biological treatment systems. This was done through degradation experiments with inhibition and abiotic controls in static reactors under aerobic and anaerobic conditions. Estrogens showed higher first order degradation rates (0.1129 h(-1)) under aerobic conditions with activated sludge inocula followed by low molecular weight (LMW) PAHs (0.0171 h(-1)), triclosan (0.0072 h(-1)), middle (MMW) (0.0054 h(-1)) and high molecular weight PAHs (HMW) (0.0033 h(-1)). The same trend was observed under aerobic conditions with a facultative inoculum from a WSP, although at a much slower rate. Biodegradation was the major removal mechanism for these chemicals in the activated sludge and WSP WWTPs surveyed. Photodegradation of these chemicals was also observed and varied across the group of chemicals (estrogens (light rate = 0.4296 d(-1); dark = 0.3900 d(-1)) degraded faster under light conditions while reverse was the case for triclosan (light rate = 0.0566 d(-1); dark = 0.1752 d(-1)). Additionally, all the chemicals were resistant to anaerobic degradation with UASB sludge, which implies that their removal in the UASB of the surveyed WWTP was most likely via sorption onto solids. Importantly, the first order degradation rate determined in this study was used to estimate predicted effluent concentrations (PECs). The PECs showed good agreement with the measured effluent concentrations from a previous study for these treatment systems.

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