首页> 外文期刊>Environmental toxicology and chemistry >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
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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

机译:在两种不同流速下用作农药的无源取样器的硅橡胶棒的标定:水边界层和聚合物控制下的采样速率建模

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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-s), and partition coefficient between silicone rubber and water (K-sw) 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(-1). 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-sw of approximately 3.3. The PRC candidates were not fully relevant to correct the impact of water flow velocity on R-s. We therefore propose an alternative method based on an overall resistance to mass transfer model to adjust R-s from laboratory experiments to in situ hydrodynamic conditions. We estimated diffusion coefficients (D-s) and thickness of water boundary layer (delta(w)) as adjustable model parameters. Log D-s values ranged from -12.13 to -10.07 m(2) s(-1). The estimated delta(w) value showed a power function correlation with water flow velocity. (C) 2017 SETAC
机译:需要通过在环境水中进行被动采样来确定极性污染物(例如农药)的时间加权平均浓度。对于此类化合物,缺少基于硅橡胶的无源采样器的校准数据。在实验室校准系统中,经过14 d的2水流量,精确测定了23种农药和13种候选性能参考化合物(PRC)的校准数据,采样率(Rs)和硅橡胶与水之间的分配系数(K-sw)。速度为5和20 cm s(-1)。结果表明,原位暴露持续时间为7 d,使得在研究的19种农药的线性或曲线吸收期内,硅橡胶棒为被动采样器。对于log K-sw约为3.3的农药,观察到了从聚合物控制到水边界层控制的传输机理的变化。中国候选人与纠正流速对R-s的影响并不完全相关。因此,我们提出了一种基于整体抗传质模型的替代方法,以将实验室实验的R-s调整为原位流体动力条件。我们将扩散系数(D-s)和水边界层的厚度(delta(w))估算为可调模型参数。对数D-s值的范围是-12.13至-10.07 m(2)s(-1)。估计的delta(w)值显示出与水流速的幂函数相关性。 (C)2017年SETAC

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