Departamento de Química-Física, Facultad de Ciencias del Mar y Ambientales, Universidad de Cádiz, Campus de Excelencia Internacional del Mar (CEI·MAR), Campus de Río San Pedro s/n, 11510 Puerto Real, Cádiz, Spain.
Departamento de Química-Física, Facultad de Ciencias del Mar y Ambientales, Universidad de Cádiz, Campus de Excelencia Internacional del Mar (CEI·MAR), Campus de Río San Pedro s/n, 11510 Puerto Real, Cádiz, Spain.
Sci Total Environ. 2017 Jul 15;590-591:643-654. doi: 10.1016/j.scitotenv.2017.03.015. Epub 2017 Mar 11.
Poor removal of many pharmaceuticals and personal care products (PPCPs) in sewage treatment leads to their discharge into the receiving waters, where they may cause negative effects. Their elimination from the water column depends of several processes, including photochemical and biological degradation. We have focused this research on comparing the degradation kinetics of a wide number (n=33) of frequently detected PPCPs considering different types of water, pH and solar irradiation. For those compounds that were susceptible of photodegradation, their rates (k) varied from 0.02 to 30.48h at pH7, with the lowest values for antihypertensive and psychiatric drugs (t>1000h). Modification of the pH turned into faster disappearance of most of the PPCPs (e.g., k=0.072 and 0.066h for atenolol and carbamazepine at pH4, respectively). On the other hand, biodegradation was enhanced by marine bacteria in many cases, for example for mefenamic acid, caffeine and triclosan (k=0.019, 0.01 and 0.04h, respectively), and was faster for anionic surfactants. Comparing photodegradation and biodegradation processes, hydrochlorothiazide and diclofenac, both not biodegradable, were eliminated exclusively by irradiation (t=0.15-0.43h and t=0.14-0.17h, respectively). Salicylic acid and phenylbutazone were efficiently photo (t<3h) and biodegraded (t=116-158h), whereas some compounds such as ibuprofen, carbamazepine and atenolol had low degradation rates by any of the processes tested (t=23-2310h), making then susceptible to persist in the aquatic media.
污水处理中许多药品和个人护理产品(PPCPs)的去除效果不佳,导致它们被排放到受纳水体中,从而可能产生负面影响。它们从水柱中的消除取决于多个过程,包括光化学和生物降解。我们专注于研究在考虑不同类型的水、pH 值和太阳辐射的情况下,比较大量(n=33)经常检测到的 PPCPs 的降解动力学。对于那些易发生光降解的化合物,它们在 pH7 下的速率(k)从 0.02 到 30.48h 不等,降压药和精神药物的速率最低(t>1000h)。pH 值的改变导致大多数 PPCPs 的消失速度加快(例如,在 pH4 下,阿替洛尔和卡马西平的 k 值分别为 0.072 和 0.066h)。另一方面,海洋细菌在许多情况下增强了生物降解,例如,对于甲芬那酸、咖啡因和三氯生(k 值分别为 0.019、0.01 和 0.04h),并且阴离子表面活性剂的生物降解速度更快。比较光降解和生物降解过程,既不可生物降解的氢氯噻嗪和双氯芬酸仅通过照射消除(t=0.15-0.43h 和 t=0.14-0.17h,分别)。水杨酸和苯丁唑酮通过光(t<3h)和生物降解(t=116-158h)有效去除,而一些化合物,如布洛芬、卡马西平和阿替洛尔,通过任何一种测试过程的降解率都很低(t=23-2310h),因此容易在水生介质中持续存在。