Meador James P, Yeh Andrew, Gallagher Evan P
Environmental and Fisheries Sciences Division, Northwest Fisheries Science Center, National Marine Fisheries Service, National Oceanic and Atmospheric Administration, 2725 Montlake Blvd. East, Seattle, WA 98112, USA; Department of Environmental and Occupational Health Sciences, School of Public Health, University of Washington, 4225 Roosevelt Way, Seattle, WA 98195, USA.
Department of Environmental and Occupational Health Sciences, School of Public Health, University of Washington, 4225 Roosevelt Way, Seattle, WA 98195, USA.
Environ Pollut. 2017 Nov;230:1018-1029. doi: 10.1016/j.envpol.2017.07.047. Epub 2017 Jul 26.
The Fish Plasma Model (FPM) was applied to water exposure and tissue concentrations in fish collected from two wastewater treatment plant impacted estuarine sites. In this study we compared predicted fish plasma concentrations to Cmax values for humans, which represents the maximum plasma concentration for the minimum therapeutic dose. The results of this study show that predictions of plasma concentrations for a variety of pharmaceutical and personal care products (PPCPs) from effluent concentrations resulted in 37 compounds (54%) exceeding the response ratio (RR = Fish [Plasma]/1%Cmax) of 1 compared to 3 compounds (14%) detected with values generated with estuarine receiving water concentrations. When plasma concentrations were modeled from observed whole-body tissue residues, 16 compounds out of 24 detected for Chinook (67%) and 7 of 14 (50%) for sculpin resulted in an RR value greater than 1, which highlights the importance of this dose metric over that using estuarine water. Because the tissue residue approach resulted in a high percentage of compounds with calculated response ratios exceeding a value of unity, we believe this is a more accurate representation for exposure in the field. Predicting plasma concentrations from tissue residues improves our ability to assess the potential for adverse effects in fish because exposure from all sources is captured. Tissue residues are also more likely to represent steady-state conditions compared to those from water exposure because of the inherent reduction in variability usually observed for field data and the time course for bioaccumulation. We also examined the RR in a toxic unit approach to highlight the importance of considering multiple compounds exhibiting a similar mechanism of action.
鱼类血浆模型(FPM)被应用于来自两个受废水处理厂影响的河口站点采集的鱼类的水暴露和组织浓度研究。在本研究中,我们将预测的鱼类血浆浓度与人类的Cmax值进行了比较,Cmax值代表最小治疗剂量下的最大血浆浓度。本研究结果表明,根据流出物浓度预测的多种药品和个人护理产品(PPCPs)的血浆浓度,有37种化合物(54%)超过了与河口接纳水浓度生成的值相比为1的响应比(RR = 鱼类[血浆]/1%Cmax),而检测到的3种化合物(14%)超过该值。当根据观察到的全身组织残留量对血浆浓度进行建模时,奇努克鲑检测到的24种化合物中有16种(67%)以及杜父鱼检测到的14种中有7种(50%)的RR值大于1,这突出了该剂量指标相对于使用河口水中该指标的重要性。由于组织残留方法导致计算出的响应比超过1的化合物比例很高,我们认为这更准确地反映了野外暴露情况。根据组织残留量预测血浆浓度提高了我们评估鱼类潜在不良反应的能力,因为捕获了所有来源的暴露情况。与水暴露相比,组织残留更有可能代表稳态条件,这是因为通常观察到野外数据的变异性固有降低以及生物累积的时间进程。我们还以毒性单位方法研究了RR,以突出考虑具有相似作用机制的多种化合物的重要性。