Fate and effects of triclosan in activated sludge

• Published in: Environmental toxicology and chemistry Vol. 21; no. 7; pp. 1330 - 1337
• Main Authors: Federle, Thomas W., Kaiser, Sandra K., Nuck, Barbara A.
• Format: Journal Article
• Language: English
• Published: Hoboken Wiley Periodicals, Inc 01.07.2002; SETAC
• Subjects: Anti-Infective Agents, Local - analysis; Anti-Infective Agents, Local - chemistry; Biodegradation; Biodegradation of pollutants; Biodegradation, Environmental; Biological and medical sciences; Biotechnology; Carbon Radioisotopes; Chromatography, High Pressure Liquid; Environment and pollution; Fundamental and applied biological sciences. Psychology; Industrial applications and implications. Economical aspects; Sewage - chemistry; Sewage - microbiology; Sewage treatment; Triclosan; Triclosan - analysis; Triclosan - chemistry; Water Pollutants, Chemical - analysis; Water Purification - methods; Freshwater environment; Biodegradation; Activated sludge; Pollutant behavior; Pollution control; Water pollution; Triclosan; Waste water purification; Antimicrobial agent
• ISSN: 0730-7268; 1552-8618
• DOI: 10.1002/etc.5620210702

Triclosan (TCS; 5‐chloro‐2‐[2,4‐dichloro‐phenoxy]‐phenol) is a widely used antimicrobial agent. To understand its fate during sewage treatment, the biodegradation and removal of TCS were determined in activated sludge. In addition, the effects of TCS on treatment processes were assessed. Fate was determined by examining the biodegradation and removal of TCS radiolabeled with 14C in the 2,4‐dichlorphenoxy ring in laboratory batch mineralization experiments and bench‐top continuous activated‐sludge (CAS) systems. In batch experiments with unacclimated sludge, TCS was mineralized to 14CO2, but the total yield varied as a function of test concentration. Systems that were redosed with TCS exhibited more extensive and faster mineralization, indicating that adaptation was a critical factor determining the rate and extent of biodegradation. In a CAS study in which the influent level of TCS was incrementally increased from 40 μg/L to 2,000 μg/L, removal of the parent compound exceeded 98.5% and removal of total radioactivity (parent and metabolites) exceeded 85%. Between 1.5 and 4.5% of TCS in the influent was sorbed to the wasted solids, whereas >94% underwent primary biodegradation and 81 to 92% was mineralized to CO2 or incorporated in biomass. Increasing levels of TCS in the influent had no major adverse effects on any wastewater treatment process, including chemical oxygen demand, biological oxygen demand, and ammonia removal. In a subsequent experiment, a CAS system, acclimated to TCS at 35 μg/L, received two separate 4‐h shock loads of 750 μg/L TCS. Neither removal of TCS nor treatment processes exhibited major adverse effects. An additional CAS study was conducted to examine the removal of a low level (10 μg/L) of TCS. Removal of parent equaled 94.7%, and biodegradation remained the dominant removal mechanism. A subsequent series of CAS experiments examined removal at four influent concentrations (7.5, 11, 20, and 50 μg/L) of TCS and demonstrated that removal of parent ranged from 98.2 to 99.3% and was independent of concentration. Although TCS removal across all experiments appeared unrelated to influent concentration, removal was significantly correlated (r2 = 0.87) with chemical oxygen demand removal, indicating that TCS removal was related to overall treatment efficiency of specific CAS units. In conclusion, the experiments show that TCS is extensively biodegraded and removed in activated‐sludge systems and is unlikely to upset sewage treatment processes at levels expected in household and manufacturing wastewaters.