Irstea, UR MALY, Villeurbanne Cedex, France.
Institut des Sciences Analytiques, Université Claude Bernard Lyon, Villeurbanne, France.
Environ Toxicol Chem. 2018 Apr;37(4):1208-1218. doi: 10.1002/etc.4050. Epub 2018 Feb 8.
There is a need to determine time-weighted average concentrations of polar contaminants such as pesticides by passive sampling in environmental waters. Calibration data for silicone rubber-based passive samplers are lacking for this class of compounds. The calibration data, sampling rate (R ), and partition coefficient between silicone rubber and water (K ) were precisely determined for 23 pesticides and 13 candidate performance reference compounds (PRCs) in a laboratory calibration system over 14 d for 2 water flow velocities, 5 and 20 cm s . The results showed that an in situ exposure duration of 7 d left a silicone rubber rod passive sampler configuration in the linear or curvilinear uptake period for 19 of the pesticides studied. A change in the transport mechanism from polymer control to water boundary layer control was observed for pesticides with a log K of approximately 3.3. The PRC candidates were not fully relevant to correct the impact of water flow velocity on R . We therefore propose an alternative method based on an overall resistance to mass transfer model to adjust R from laboratory experiments to in situ hydrodynamic conditions. We estimated diffusion coefficients (D ) and thickness of water boundary layer (δ ) as adjustable model parameters. Log D values ranged from -12.13 to -10.07 m s . The estimated δ value showed a power function correlation with water flow velocity. Environ Toxicol Chem 2018;37:1208-1218. © 2017 SETAC.
需要通过被动采样来确定环境水中极性污染物(如农药)的时间加权平均浓度。对于此类化合物,硅橡胶基被动采样器的校准数据尚不完善。在实验室校准系统中,针对 23 种农药和 13 种候选性能参考化合物(PRC),在两种水流速度(5 和 20 cm/s)下进行了 14 天的实验,精确确定了校准数据、采样速率(R)和硅橡胶与水之间的分配系数(K)。结果表明,对于研究的 19 种农药中的 7d 原位暴露时间,硅橡胶棒被动采样器的配置处于线性或曲线吸收期。对于 log K 约为 3.3 的农药,观察到从聚合物控制到水边界层控制的传输机制发生变化。PRC 候选物并不能完全纠正水流速度对 R 的影响。因此,我们提出了一种替代方法,基于总体传质阻力模型,将实验室实验中的 R 调整到现场水动力条件。我们将扩散系数(D)和水边界层厚度(δ)估计为可调节模型参数。log D 值范围从-12.13 到-10.07 m/s。估计的 δ 值与水流速度呈幂函数关系。Environ Toxicol Chem 2018;37:1208-1218。©2017 SETAC。