Fraunhofer Institute for Molecular Biology and Applied Ecology (Fraunhofer IME), 57392 Schmallenberg, Germany.
Chemosphere. 2013 Jun;91(11):1517-24. doi: 10.1016/j.chemosphere.2012.12.030. Epub 2013 Jan 19.
A retrospective monitoring of triclosan (TCS; period 1994-2003 and 2008) and its potential transformation product methyl-triclosan (MTCS; period 1994-2008) was performed using archived fish samples from German rivers (16 sites, including Elbe and Rhine). At four of these sites suspended particulate matter (SPM) was also investigated covering the period 2005-2007. Samples were analyzed by GC/MS, either directly (MTCS) or after derivatization (TCS). TCS burdens of fish muscle tissue ranged from <0.2-3.4 ng g(-1) ww (wet weight; corresponding to <2-69 ng g(-1) lw, lipid weight) without apparent concentration trends over time. MTCS was detected at considerably higher concentrations in fish ranging from 1.0-33 ng g(-1) ww (47-1010 ng g(-1) lw) and increased until about 2003-2005. Thereafter, concentrations generally were lower, although at some sites single higher values were observed in recent years. In SPM, decreasing MTCS concentrations in the range 1-4 ng g(-1) dry weight were detected while TCS was always below the limit of quantification. Assuming that MTCS concentrations are correlated to TCS consumption, the observed decrease in MTCS levels may be partly a result of the voluntary renunciation of TCS use in detergents for, e.g., laundry or dishwashing declared by a manufacturers' association in 2001. Because of a lack of ecotoxicity studies for MTCS, a QSAR-derived predicted no effect concentration (PNEC) was compared to averaged ambient water concentrations of fish which were calculated from maximum tissue residues by applying an appropriate bioconcentration factor from literature. Since these calculated water concentrations were below the PNEC it is assumed that MTCS alone poses no immediate risk to aquatic organism. The conversion to a PNEC for SPM organisms and comparison with detected SPM levels of MTCS also revealed no risk.
采用 GC/MS 对德国河流(包括易北河和莱茵河在内的 16 个采样点)中 archived 鱼类样本进行了三氯生(TCS;1994-2003 年和 2008 年)及其潜在转化产物甲基三氯生(MTCS;1994-2008 年)的回顾性监测。其中四个采样点还对 2005-2007 年期间的悬浮颗粒物(SPM)进行了调查。样品可直接(MTCS)或衍生化后(TCS)进行 GC/MS 分析。鱼肌肉组织中 TCS 的含量范围为<0.2-3.4ng g(-1)ww(湿重;相应的<2-69ng g(-1) lw,脂重),随时间无明显浓度趋势。鱼体中 MTCS 的浓度明显较高,范围为 1.0-33ng g(-1)ww(47-1010ng g(-1) lw),并在 2003-2005 年左右增加。此后,浓度通常较低,但在近几年的一些采样点中观察到了单个较高值。在 SPM 中,检测到 MTCS 的浓度呈下降趋势,范围在 1-4ng g(-1)dw,而 TCS 一直低于定量限。假设 MTCS 浓度与 TCS 的消耗相关,那么 MTCS 水平的下降可能部分是由于制造商协会于 2001 年宣布自愿放弃在洗衣或洗碗洗涤剂中使用 TCS。由于缺乏 MTCS 的生态毒性研究,因此将基于定量结构活性关系(QSAR)得出的无效应浓度(PNEC)与通过文献中的适当生物浓缩因子从最大组织残留计算得出的鱼类环境水浓度进行了比较。由于这些计算得出的水浓度低于 PNEC,因此假设 MTCS 本身不会对水生生物造成直接风险。将其转换为 SPM 生物的 PNEC,并与检测到的 MTCS 的 SPM 水平进行比较,也未发现风险。