Urban Water Systems Engineering, Technische Universität München, Am Coulombwall, 85748, Garching, Germany,
Environ Sci Pollut Res Int. 2014 Feb;21(4):2795-804. doi: 10.1007/s11356-013-2199-3. Epub 2013 Oct 18.
The intensive use of benzotriazoles as corrosion inhibitors for various applications and their application in dishwasher detergents result in an almost omnipresence of benzotriazole (BTri), 4-methyl- and 5-methyl-benzotriazole (4-TTri and 5-TTri, respectively) in aquatic systems. This study aims on the evaluation of the biodegradation potential of activated sludge communities (ASCs) toward the three benzotriazoles regarding aerobic, anoxic, and anaerobic conditions and different nutrients. ASCs were taken from three wastewater treatment plants with different technologies, namely, a membrane bioreactor (MBR-MH), a conventional activated sludge plant CAS-E (intermittent nitrification/denitrification), and CAS-M (two-stage activated sludge treatment) and used for inoculation of biodegradation setups. All ASCs eliminated up to 30 mg L(-1) 5-TTri and BTri under aerobic conditions within 2-7 and 21-49 days, respectively, but not under anoxic or anaerobic conditions. 4-TTri was refractory at all conditions tested. Significant differences were observed for BTri biodegradation with non-acclimated ASCs from MBR-MH with 21 days, CAS-E with 41 days, and CAS-M with 49 days. Acclimated ASCs removed BTri within 7 days. Furthermore, different carbon and nitrogen concentrations revealed that nitrogen was implicitly required for biodegradation while carbon showed no such effect. The fastest biodegradation occurred for 5-TTri with no need for acclimatization, followed by BTri. BTri showed sludge-specific biodegradation patterns, but, after sludge acclimation, was removed with the same pattern, regardless of the sludge used. Under anaerobic conditions in the presence of different electron acceptors, none of the three compounds showed biological removal. Thus, presumably, aerobic biodegradation is the major removal mechanism in aquatic systems.
苯并三唑作为各种应用的腐蚀抑制剂被大量使用,并且其还应用于洗碗机洗涤剂中,这导致苯并三唑(BTri)、4-甲基苯并三唑(4-TTri)和 5-甲基苯并三唑(5-TTri)在水系统中几乎无处不在。本研究旨在评估好氧、缺氧和厌氧条件以及不同营养物质下活性污泥(ASCs)对这三种苯并三唑的生物降解潜力。ASCs 取自三个具有不同技术的污水处理厂,即膜生物反应器(MBR-MH)、传统活性污泥厂 CAS-E(间歇硝化/反硝化)和 CAS-M(两段式活性污泥处理),并用于生物降解装置的接种。所有 ASCs 在好氧条件下可在 2-7 和 21-49 天内消除高达 30mg/L 的 5-TTri 和 BTri,但在缺氧或厌氧条件下则无法消除。在所有测试条件下,4-TTri 均难以生物降解。在用未驯化的 MBR-MH 活性污泥进行 21 天、用 CAS-E 活性污泥进行 41 天和用 CAS-M 活性污泥进行 49 天的 BTri 生物降解试验中,观察到了显著差异。驯化后的 ASCs 可在 7 天内消除 BTri。此外,不同的碳氮浓度表明,生物降解需要氮,而碳则没有这种影响。5-TTri 的生物降解速度最快,无需驯化,其次是 BTri。BTri 表现出特定于污泥的生物降解模式,但在污泥驯化后,无论使用何种污泥,其去除模式都相同。在存在不同电子受体的厌氧条件下,这三种化合物均未显示出生物去除。因此,有氧生物降解可能是水系统中主要的去除机制。