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硅橡胶棒作为两种不同流速下农药的被动采样器的校准:水边界层和聚合物控制下采样速率的建模。

Calibration of silicone rubber rods as passive samplers for pesticides at two different flow velocities: Modeling of sampling rates under water boundary layer and polymer control.

机构信息

Irstea, UR MALY, Villeurbanne Cedex, France.

Institut des Sciences Analytiques, Université Claude Bernard Lyon, Villeurbanne, France.

出版信息

Environ Toxicol Chem. 2018 Apr;37(4):1208-1218. doi: 10.1002/etc.4050. Epub 2018 Feb 8.

Abstract

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.

摘要

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。

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