Guo Min, Xu Linyue, Guo Liguo, Hu Jie, Liu Ru
Ministry of Ecology and Environment, Nanjing Institute of Environmental Science, Nanjing 210042, China.
Toxics. 2025 Sep 15;13(9):780. doi: 10.3390/toxics13090780.
Degradation is a key natural attenuation mechanism governing the fate of PPCPs during anaerobic digestion (AD) and subsequent soil exposure. Nevertheless, the combined impact of this sequential treatment (AD followed by land application) remains poorly understood. This study evaluated the degradation characteristics of nine PPCPs during mesophilic AD in three distinct soil types. The concentration changes in the nine PPCPs were monitored after 0, 5, 10, 15, 20, 25, and 30 days of anaerobic incubation at 38 °C, as well as after 0, 2, 5, 8, 10, 12, 15, 20, and 30 days of dark incubation at 25 °C with humidity at 75% in three soils. AD effectively removed sulfamethoxydiazine, ciprofloxacin, and oxytetracycline (>80%). The removal efficiencies for carbamazepine, progesterone, triclosan, naproxen, and megestrol acetate were relatively poor, with the removal rates ranging from 50% to 80%, while gemfibrozil exhibited minimal degradation (<50%). The degradation behavior of nine PPCPs fits well with first-order kinetic equations. Calculated half-lives (days) in the three soils were as follows: sulfamethoxydiazine (20.39 to 23.10), carbamazepine (36.48 to 77.02), megestrol acetate (11.18 to 20.39), progesterone (6.08 to 23.90), ciprofloxacin (11.75 to 63.01), oxytetracycline (13.08 to 30.14), naproxen (7.79 to 40.77), gemfibrozil (8.45 to 30.14), and triclosan (14.75 to 46.21). The corresponding R values ranged from 0.8882 to 0.9320 for sulfamethoxydiazine, 0.8579 to 0.9248 for carbamazepine, 0.8745 to 0.9658 for megestrol acetate, 0.9026 to 0.9560 for progesterone, 0.8147 to 0.9571 for ciprofloxacin, 0.8136 to 0.9063 for oxytetracycline, 0.8961 to 0.9156 for naproxen, 0.8802 to 0.9497 for gemfibrozil, and 0.9099 to 0.9457 for triclosan. Soil physicochemical properties significantly influenced PPCP degradation rates. Gemfibrozil warrants immediate attention due to its poor degradation; the five PPCPs presenting moderate concern-namely carbamazepine, ciprofloxacin, oxytetracycline, naproxen, and triclosan-require further risk assessment, while sulfamethoxydiazine, megestrol acetate, and progesterone pose low persistence risk according to current evidence.
降解是控制厌氧消化(AD)及后续土壤暴露过程中持久性有机污染物(PPCPs)归宿的关键自然衰减机制。然而,这种序贯处理(AD后进行土地施用)的综合影响仍知之甚少。本研究评估了9种PPCPs在三种不同土壤类型的中温AD过程中的降解特性。在38℃厌氧培养0、5、10、15、20、25和30天后,以及在三种土壤中于25℃黑暗培养0、2、5、8、10、12、15、20和30天且湿度为75%后,监测了9种PPCPs的浓度变化。AD有效去除了磺胺二甲嘧啶、环丙沙星和土霉素(>80%)。卡马西平、孕酮、三氯生、萘普生和醋酸甲地孕酮的去除效率相对较差,去除率在50%至80%之间,而吉非罗齐的降解程度最小(<50%)。9种PPCPs的降解行为与一级动力学方程拟合良好。三种土壤中的计算半衰期(天)如下:磺胺二甲嘧啶(20.39至23.10)、卡马西平(36.48至77.02)、醋酸甲地孕酮(11.18至20.39)、孕酮(6.08至23.90)、环丙沙星(11.75至63.01)、土霉素(13.08至30.14)、萘普生(7.79至40.77)、吉非罗齐(8.45至30.14)和三氯生(14.75至46.21)。磺胺二甲嘧啶的相应R值范围为0.8882至0.9320,卡马西平为0.8579至0.9248,醋酸甲地孕酮为0.8745至0.9658,孕酮为0.9026至0.9560,环丙沙星为0.8147至0.9571,土霉素为0.8136至0.9063,萘普生为0.8961至0.9156,吉非罗齐为0.8802至0.9497,三氯生为0.9099至0.9457。土壤理化性质显著影响PPCP的降解速率。吉非罗齐因其降解性差而值得立即关注;卡马西平、环丙沙星、土霉素、萘普生和三氯生这五种PPCPs存在中度问题,需要进一步进行风险评估,而根据目前的证据,磺胺二甲嘧啶、醋酸甲地孕酮和孕酮的持久性风险较低。