Irstea, UR MALY, Villeurbanne Cedex, France.
Talanta. 2013 May 15;109:61-73. doi: 10.1016/j.talanta.2013.01.058. Epub 2013 Feb 14.
The literature increasingly reports sampling rates (Rs) for Polar Organic Chemical Integrative Samplers (POCIS) but the data obtained come from various calibration systems that are not always well-defined (agitation, temperature, measured micropollutant concentrations in water,…). In order to obtain accurate laboratory Rs for priority and emerging substances, POCIS need to be exposed in a robust and well-defined calibration system. Thus, we built a flow-through calibration system containing tap water spiked with 56 organic micropollutants (alkylphenols and phenols, hormones, pesticides, pharmaceuticals, UV filter). POCIS were immersed for up to 28 days. Tap water micropollutant concentrations and additional parameters (temperature, pH, conductivity, dissolved organic carbon, flow velocities) were kept constant and controlled throughout the calibration experiment. Based on the observed uptake kinetics, we distinguished four types of micropollutant accumulation patterns: curvilinear accumulation (30 molecules, group 1), accumulation with an inflexion point (13 molecules, group 2), random accumulation (eight molecules, group 3), and no or very low accumulation (five molecules, group 4). Rs was calculated for 43 out of 56 micropollutants (groups 1 and 2). Calculated Rs values ranged from 0.030 L/d to 0.398 L/d. POCIS can supply TWA concentrations for hormones, pesticides, several pharmaceuticals, a few alkylphenols, and the UV filter. Our Rs results are generally less than two fold-different (higher or lower depending on target molecule) to the literature data using the same type of calibration system or for micropollutants with log Kow>2.65. We found a quadratic correlation between Rs and log D for betablockers, herbicides and hormones.
文献中越来越多地报告了极性有机化学整合采样器(POCIS)的采样速率(Rs),但获得的数据来自各种校准系统,这些系统并不总是定义明确的(搅拌、温度、水中测量的微量污染物浓度,...)。为了获得优先和新兴物质的准确实验室 Rs,POCIS 需要在稳健且定义明确的校准系统中暴露。因此,我们构建了一个流动校准系统,其中包含用 56 种有机微量污染物(烷基酚和酚类、激素、农药、药品、紫外线过滤器)加标的自来水。POCIS 浸泡时间长达 28 天。自来水中的微量污染物浓度和其他参数(温度、pH 值、电导率、溶解有机碳、流速)在整个校准实验过程中保持恒定并得到控制。根据观察到的吸收动力学,我们区分了四种类型的微量污染物积累模式:曲线积累(30 种分子,第 1 组)、有拐点的积累(13 种分子,第 2 组)、随机积累(8 种分子,第 3 组)和无或极低积累(5 种分子,第 4 组)。我们为 56 种微量污染物中的 43 种(第 1 组和第 2 组)计算了 Rs。计算得到的 Rs 值范围为 0.030 L/d 至 0.398 L/d。POCIS 可为激素、农药、几种药品、一些烷基酚和紫外线过滤器提供 TWA 浓度。我们的 Rs 结果与使用相同类型的校准系统或对于 log Kow>2.65 的微量污染物的文献数据相比,一般相差不到两倍(取决于目标分子,更高或更低)。我们发现 Rs 与 betablockers、除草剂和激素的 log D 之间存在二次相关性。