Department of Environmental Health Sciences, University Medical Center Freiburg, Freiburg, Germany.
Chemosphere. 2011 Oct;85(5):765-73. doi: 10.1016/j.chemosphere.2011.06.057. Epub 2011 Jul 12.
Active pharmaceutical ingredients as well as personal care products are detected in increasing prevalence in different environmental compartments such as surface water, groundwater and soil. Still little is known about the environmental fate of these substances. The type II antidiabetic drug Metformin has already been detected in different surface waters worldwide, but concentrations were significantly lower than the corresponding predicted environmental concentration (PEC). In human and mammal metabolism so far no metabolites of Metformin have been identified, so the expected environmental concentrations should be very high. To assess the aerobic biodegradability of Metformin and the possible formation of degradation products, three Organisation of Economic Cooperation and Development (OECD) test series were performed in the present study. In the Closed Bottle test (OECD 301 D), a screening test that simulates the conditions of an environmental surface water compartment, Metformin was classified as not readily biodegradable (no biodegradation). In the Manometric Respiratory test (OEDC 301 F) working with high bacterial density, Metformin was biodegraded in one of three test bottles to 48.7% and in the toxicity control bottle to 57.5%. In the Zahn-Wellens test (OECD 302 B) using activated sludge, Metformin was biodegraded in both test vessels to an extent of 51.3% and 49.9%, respectively. Analysis of test samples by high performance liquid chromatography coupled to multiple stage mass spectrometry (HPLC-MS(n)) showed in the tests vessels were biodegradation was observed full elimination of Metformin and revealed Guanylurea (Amidinourea, Dicyandiamidine) as single and stable aerobic bacterial degradation product. In another Manometric Respiratory test Guanylurea showed no more transformation. Photodegradation of Guanylurea was also negative. A first screening in one of the greatest sewage treatment plant in southern Germany found Metformin with high concentrations (56.8 μg L⁻¹) in the influent (PEC=79.8 μg L⁻¹), but effluent concentration was much lower (0.76 μg L⁻¹) whereas Guanylurea was detected in a low influent and high effluent concentration (1.86 μg L⁻¹). These data support the experimental findings in the OECD tests and analytical results of other studies, that Metformin under aerobic conditions can bacterially be degraded to the stable dead-end transformation product Guanylurea.
越来越多的研究发现,活性药物成分和个人护理产品在地表水中、地下水中和土壤等不同的环境介质中都有检出。但这些物质在环境中的归趋仍然知之甚少。二甲双胍是一种 II 型抗糖尿病药物,已在世界范围内的不同地表水中检出,但浓度明显低于相应的预测环境浓度 (PEC)。在人和哺乳动物的新陈代谢中,尚未鉴定出二甲双胍的代谢物,因此预期的环境浓度应该非常高。为了评估二甲双胍的好氧生物降解性和可能形成的降解产物,本研究进行了三项经济合作与发展组织 (OECD) 测试系列。在密闭瓶测试(OECD 301D)中,模拟环境地表水的条件进行的筛选测试,二甲双胍被归类为不易生物降解(无生物降解)。在呼吸计测试(OECD 301F)中,使用高细菌密度,在三个测试瓶中的一个中,二甲双胍被生物降解至 48.7%,在毒性对照瓶中降解至 57.5%。在 Zahn-Wellens 测试(OECD 302B)中,使用活性污泥,在两个测试容器中,二甲双胍分别被生物降解至 51.3%和 49.9%。通过高效液相色谱-串联质谱(HPLC-MS(n))对测试样品进行分析表明,在观察到生物降解的测试容器中,二甲双胍完全消除,并揭示出胍基脲(氨甲酰脲,双氰胺)是单一且稳定的好氧细菌降解产物。在另一个呼吸计测试中,胍基脲没有进一步转化。胍基脲的光降解也是阴性的。在德国南部最大的污水处理厂之一进行的初步筛选发现,二甲双胍在进水(PEC=79.8μg/L)中浓度较高(56.8μg/L),而出水浓度则低得多(0.76μg/L),而胍基脲在进水浓度低、出水浓度高(1.86μg/L)的情况下被检出。这些数据支持 OECD 测试中的实验结果以及其他研究的分析结果,即在好氧条件下,二甲双胍可以被细菌降解为稳定的末端转化产物胍基脲。