Formerly: Sustainable Chemistry and Material Resources, Institute of Sustainable Environmental Chemistry, Leuphana University Lüneburg, C13, DE-21335 Lüneburg, Germany.
Sustainable Chemistry and Material Resources, Institute of Sustainable Environmental Chemistry, Leuphana University Lüneburg, C13, DE-21335 Lüneburg, Germany.
Sci Total Environ. 2017 Apr 1;583:36-52. doi: 10.1016/j.scitotenv.2016.12.184. Epub 2017 Jan 23.
Pharmaceuticals do not occur isolated in the environment but in multi-component mixtures and may exhibit antagonist, synergistic or additive behavior. Knowledge on this is still scarce. The situation is even more complicated if effluents or potable water is treated by oxidative processes or such transformations occur in the environment. Thus, determining the fate and effects of parent compounds, metabolites and transformation products (TPs) formed by transformation and degradation processes in the environment is needed. This study investigated the fate and preliminary ecotoxicity of the phenothiazine pharmaceuticals, Promazine (PRO), Promethazine (PRM), Chlorpromazine (CPR), and Thioridazine (THI) as single and as components of the resulting mixtures obtained from their treatment by Fenton process. The Fenton process was carried out at pH7 and by using 0.5-2mgL of [Fe] and 1-12.5mgL of [HO] at the fixed ratio [Fe]:[HO] of 1:10 (w:w). No complete mineralization was achieved. Constitutional isomers and some metabolite-like TPs formed were suggested based on their UHPLC-HRMS data. A degradation pathway was proposed considering interconnected mechanisms such as sulfoxidation, hydroxylation, N-dealkylation, and dechlorination steps. Aerobic biodegradation tests (OECD 301 D and OECD 301 F) were applied to the parent compounds separately, to the mixture of parent compounds, and for the cocktail of TPs present after the treatment by Fenton process. The samples were not readily biodegradable. However, LC-MS analysis revealed that abiotic transformations, such hydrolysis, and autocatalytic transformations occurred. The initial ecotoxicity tested towards Vibrio fischeri as individual compounds featured a reduction in toxicity of PRM and CPR by the treatment process, whereas PRO showed an increase in acute luminescence inhibition and THI a stable luminescence inhibition. Concerning effects of the mixture components, reduction in toxicity by the Fenton process was predicted by concentration addition and independent action models.
药品并非孤立存在于环境中,而是存在于多组分混合物中,并可能表现出拮抗、协同或相加作用。但目前我们对这方面的了解还很匮乏。如果废水或饮用水经过氧化处理,或者在环境中发生此类转化,情况会更加复杂。因此,需要确定母体化合物、代谢物和转化产物(TPs)在环境中通过转化和降解过程的归宿和效应。本研究调查了吩噻嗪类药物普罗嗪(PRO)、苯海拉明(PRM)、氯丙嗪(CPR)和硫利达嗪(THI)作为单一药物以及作为芬顿工艺处理后得到的混合物的组成部分的归宿和初步生态毒性。芬顿工艺在 pH7 下进行,使用 0.5-2mgL 的 [Fe] 和 1-12.5mgL 的 [HO],[Fe]与[HO]的固定比值为 1:10(w:w)。但未达到完全矿化。根据超高效液相色谱-高分辨率质谱(UHPLC-HRMS)数据,推测形成了结构异构体和一些类似代谢物的 TPs。考虑到相互关联的机制,如氧化脱硫、羟化、N-脱烷基化和脱氯步骤,提出了一条降解途径。分别对母体化合物、母体化合物混合物以及芬顿工艺处理后的 TPs 混合物进行了好氧生物降解试验(OECD 301 D 和 OECD 301 F)。这些样品不易生物降解。然而,LC-MS 分析表明,存在非生物转化,如水解和自动催化转化。单独测试时,各化合物对发光菌(Vibrio fischeri)的初始生态毒性表现出 PRM 和 CPR 毒性降低,而 PRO 则表现出急性发光抑制增加,THI 则表现出稳定的发光抑制。就混合物成分的影响而言,浓度加和和独立作用模型预测芬顿工艺处理会降低毒性。