RECETOX, Masaryk University, Kamenice 753/5, 625 00, Brno, Czech Republic.
UFZ-Department of Ecological Chemistry, Helmholtz-Centre for Environmental Research, Permoserstraße 15, 04318, Leipzig, Germany.
Chemosphere. 2020 Jun;249:126183. doi: 10.1016/j.chemosphere.2020.126183. Epub 2020 Feb 13.
Diffusion coefficient (D) is an important parameter for prediction of micropollutant uptake kinetics in passive samplers. Passive samplers are nowadays commonly used for monitoring trace organic pollutants in different environmental matrices. Samplers utilising a hydrogel layer to control compound diffusion are gaining popularity. In this work we investigated diffusion of several perfluoroalkyl substances, currently used pesticides, pharmaceuticals and personal care products in 1.5% agarose hydrogel by measuring diffusion coefficients using two methods: a diffusion cell and a sheet stacking technique. Further, diffusion coefficients in water were measured using Taylor dispersion method. The sheet stacking method was used to measure D at 5, 12, 24, and 33 °C in order to investigate temperature effect on diffusion. Median D values ranged from 2.0 to 8.6 × 10 cm s and from 2.1 to 8.5 × 10 cm s for the diffusion cell and sheet stack methods respectively. For most compounds, the variability between replicates was higher than the difference between values obtained by the two methods. Rising temperature from 10 to 20 °C increases the diffusion rate by the factor of 1.41 ± 0.10 in average. In water, average D values ranged from 3.03 to 10.0 × 10 cm s and were comparable to values in hydrogel, but some compounds including perfluoroalkyl substances with a long aliphatic chain could not be evaluated properly due to sorptive interactions with capillary walls in the Taylor dispersion method. Sampling rates estimated using the measured D values were systematically higher than values estimated from laboratory sampler calibration in our previously published study, by the factor of 2.2 ± 1.0 in average.
扩散系数(D)是预测被动采样器中微量污染物摄取动力学的重要参数。被动采样器现在常用于监测不同环境基质中的痕量有机污染物。利用水凝胶层来控制化合物扩散的采样器越来越受欢迎。在这项工作中,我们通过使用两种方法(扩散池和薄片堆叠技术)测量扩散系数,研究了几种全氟烷基物质、目前使用的农药、药物和个人护理产品在 1.5%琼脂糖水凝胶中的扩散情况。此外,还使用泰勒分散法测量了水中的扩散系数。使用薄片堆叠法在 5、12、24 和 33°C 下测量 D,以研究温度对扩散的影响。中位数 D 值范围为 2.0 至 8.6×10 cm s 和 2.1 至 8.5×10 cm s,分别用于扩散池和薄片堆叠方法。对于大多数化合物,重复测量之间的变异性高于两种方法获得的值之间的差异。从 10°C 升高到 20°C 平均增加扩散速率 1.41±0.10 倍。在水中,平均 D 值范围为 3.03 至 10.0×10 cm s,与水凝胶中的值相当,但由于与泰勒分散法中毛细管壁的吸附相互作用,一些包括具有长脂肪链的全氟烷基物质在内的化合物无法得到适当评估。使用测量的 D 值估计的采样速率系统地高于我们之前发表的研究中从实验室采样器校准估计的值,平均高 2.2±1.0 倍。