Department of Process Engineering and Applied Science, Faculty of Engineering, Dalhousie University, Halifax, Nova Scotia, Canada.
Department of Engineering, Dalhousie University Faculty of Agriculture, PO Box 550, Truro, NS B2N 5E3, Canada.
Sci Total Environ. 2021 Feb 10;755(Pt 1):142520. doi: 10.1016/j.scitotenv.2020.142520. Epub 2020 Sep 24.
Land application of biosolids is one potential source of pharmaceuticals and personal care products (PPCPs) into agricultural soils. Degradation is an important natural attenuation pathway that affects the fate and transport of PPCPs in the soil system and biosolids application could alter the process. The present study assessed the effect of individual and mixture compound environments on the biodegradation rate and half-life of three non-steroidal anti-inflammatory drugs (NSAIDs), naproxen (NPX), ibuprofen (IBF), and ketoprofen (KTF), in a loamy sand textured agricultural soil receiving an alkaline treated biosolid (ATB) amendment. A prolonged half-life of the target NSAIDs was determined for sterile soils and shorter half-lives in unsterile soils, indicating the loss of target compounds in all treatments was mainly attributed to biodegradation and followed first-order kinetics. IBF and NPX showed low to moderate persistence in soil and ATB amended soil, with half-lives ranging from 4.9 to 14.8 days, while KTF appeared to be highly persistent with an average half-life of 33 days. The order in which the target NSAIDs disappeared in both soil and ATB amended soil was: IBF > NPX > KTF, for both individual and mixture compound treatments. Soils that received the ATB amendment demonstrated inhibited degradation of NPX in all treatments, as well as IBF and KTF in individual compound treatment over the 14-day incubation study. We also observed an inhibition effect from the ATB amendment in sterile soil treatments. In mixture compound treatments, IBF degradation was inhibited in both soil and ATB amended soil. The degradation rate of KTF in mixture compound environment in soil was lower, while the opposite effects were observed in ATB amended soils. For NPX, the degradation was enhanced in mixture compound environment in ATB amended soil, while the same degradation rate of NPX was calculated in soil.
土地应用生物固体是将药品和个人护理产品(PPCPs)进入农业土壤的潜在来源之一。降解是影响土壤系统中 PPCPs 归宿和迁移的重要自然衰减途径,而生物固体的应用可能会改变这一过程。本研究评估了单一和混合化合物环境对三种非甾体抗炎药(NSAIDs)萘普生(NPX)、布洛芬(IBF)和酮洛芬(KTF)在接受碱性处理生物固体(ATB)改良的粉质砂质农业土壤中生物降解率和半衰期的影响。无菌土壤中确定了目标 NSAIDs 的半衰期延长,而未无菌土壤中的半衰期较短,表明所有处理中目标化合物的损失主要归因于生物降解,并遵循一级动力学。IBF 和 NPX 在土壤和 ATB 改良土壤中的持久性较低,半衰期范围为 4.9 至 14.8 天,而 KTF 似乎具有高度持久性,平均半衰期为 33 天。在土壤和 ATB 改良土壤中,目标 NSAIDs 的消失顺序均为:IBF>NPX>KTF,无论是单一化合物处理还是混合化合物处理。接受 ATB 改良的土壤在所有处理中均表现出 NPX 的降解受到抑制,而在单一化合物处理中,IBF 和 KTF 的降解也受到抑制,在 14 天的孵育研究中。我们还观察到 ATB 改良对无菌土壤处理的抑制作用。在混合化合物处理中,IBF 在土壤和 ATB 改良土壤中的降解均受到抑制。KTF 在混合物环境中的降解速率在土壤中较低,而在 ATB 改良土壤中则观察到相反的效果。对于 NPX,在 ATB 改良土壤中的混合物环境中,NPX 的降解得到增强,而在土壤中计算出 NPX 的相同降解率。