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Overlooked risks of non-oxidizing antimicrobials (NOAMs) in water environments

抗菌剂 环境科学 水消毒 环境规划 风险分析(工程) 水质 业务 水污染 水传播病 风险评估 废物管理 环境卫生 抗感染药 水污染 环境工程 供水 污染 水处理 人类健康 地表水 安全饮用水法案 食品污染物
作者
Nan Huang,De‐Xiu Wu,Ye Du,Yanlin Chen,Qian-Yuan Wu,Hong‐Ying Hu
出处
期刊:Critical Reviews in Environmental Science and Technology [Taylor & Francis]
卷期号:55 (22): 1683-1706
标识
DOI:10.1080/10643389.2025.2563346
摘要

Non-oxidizing antimicrobials (NOAMs) provide long-lasting microbial control without reacting with other components or causing equipment corrosion, yet their environmental and health risks are often overlooked. Common NOAMs include quaternary ammonium compounds (QACs), aldehydes, isothiazolinones, azoles, and biguanides. They are widely used in households, healthcare, industry, water treatment, and agriculture, entering the environment through wastewater, hospital/industrial sources, and urban/agricultural runoff. NOAM concentrations can reach mg/L in hospital/industrial wastewater and reverse osmosis (RO) concentrate. NOAMs have been detected globally in surface waters, sediments, and sewage sludge, with median concentrations of 0.01–0.1 μg/L, 3.2–12 μg/kg, and 5–7562 μg/kg, respectively. Risks associated with NOAMs include increased antibiotic resistance, ecotoxicity to aquatic organisms, and potential health hazards. Exposure to sub-inhibitory concentrations of QACs, cetrimide, or chlorhexidine can enhance resistance to other NOAMs and antibiotics by 1.3 to over 100 times. NOAMs exhibit comparable or higher ecotoxicity to luminescent bacteria, algae, daphnids, and fish compared to personal care products (PPCPs) and disinfection by-products (DBPs). NOAMs like QACs, isothiazolinones, and carbendazim can cause skin allergies, liver inflammation, fibrosis, or neuronal damage via multiple exposure routes. Most NOAMs require several weeks or more for complete biodegradation. NOAMs and PPCPs show similar biodegradability, both being less biodegradable than DBPs. Ozone reacts with QACs, carbendazim, and chloromethylisothiazolinone (CMIT) at rates below 10 M−1s−1. Hydroxyl radicals react rapidly with NOAMs (>109 M−1s−1), while sulfate radical reactions with NOAMs are poorly understood. Future research requires expanded environmental monitoring, multi-endpoint toxicity assessments, resistance mechanisms under high NOAM pressure, and advanced disposal strategies.
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