Great Lakes Institute for Environmental Research, University of Windsor, 401 Sunset Avenue, Windsor, Ontario, N9B 3P4, Canada; College of Resources and Environment, Southwest University, No.1 Tiansheng Road, Beibei, Chongqing, 400715, China; National Base of International S&T Collaboration on Water Environmental Monitoring and Simulation in TGR Region (WEMST), No.1 Tiansheng Road, Beibei, Chongqing, 400715, China.
Great Lakes Institute for Environmental Research, University of Windsor, 401 Sunset Avenue, Windsor, Ontario, N9B 3P4, Canada; National Base of International S&T Collaboration on Water Environmental Monitoring and Simulation in TGR Region (WEMST), No.1 Tiansheng Road, Beibei, Chongqing, 400715, China.
Environ Pollut. 2018 Dec;243(Pt A):152-162. doi: 10.1016/j.envpol.2018.08.067. Epub 2018 Aug 24.
This study evaluated the effect of growth of different tissue compartments on the bioaccumulation of mercury (Hg) and polychlorinated biphenyls (PCBs) in Silver Carp (Hypophthalmichthys molitrix) and Bighead Carp (Hypophthalmichthys nobilis) from the Three Gorges Reservoir (TGR), China. A non-steady state bioenergetics/toxicokinetic model was developed to simulate PCB and Hg concentrations in these two species and compared with field data. Simulations using constant whole body growth rate and constant tissue to whole body weight ratios were contrasted against simulations adopting age specific whole body and tissue/age specific growth rates for their goodness of fit to field data. The simulations using age/tissue specific growth rates demonstrated better fit to field data for PCBs compared to the constant growth rate models (22% improved R), while both models explained similar variation in Hg concentration data. Both species demonstrated higher growth rates of lipids (on a daily basis) relative to whole body and protein contributing to higher growth dilution of PCBs compared to Hg. Although stable isotope data indicated some degree of diet and/or habitat shift, simulations assuming a constant diet concentration explained between 36 and 40% of the variation in fish concentrations for both contaminants and fish species. This study demonstrates that differences in the bioaccumulation rate of PCBs and Hg by Asian carp can be partially explained by differences in the growth rates of key tissue storage compartments associated with each contaminant. These differences in chemical-specific growth dilution subsequently contribute to differences in chemical retention and bioaccumulation patterns of Hg and PCBs by fish.
本研究评估了不同组织隔室生长对三峡水库(TGR)草鱼(Hypophthalmichthys molitrix)和大头鱼(Hypophthalmichthys nobilis)体内汞(Hg)和多氯联苯(PCBs)生物累积的影响。建立了一个非稳态生物能量/毒动学模型,以模拟这两种鱼类体内的 PCB 和 Hg 浓度,并与现场数据进行比较。模拟采用恒定的全身生长率和恒定的组织与体重比与采用年龄特异性全身和组织/年龄特异性生长率的模拟进行对比,以评估其对现场数据的拟合程度。与恒定生长率模型相比,采用年龄/组织特异性生长率的模拟更能拟合 PCB 的现场数据(拟合优度提高了 22%),而这两种模型都能解释 Hg 浓度数据的相似变化。与 Hg 相比,两种鱼类的脂质(按日计)生长率相对全身和蛋白质的生长率更高,这导致了 PCB 的生长稀释率更高。尽管稳定同位素数据表明存在一定程度的饮食和/或栖息地变化,但模拟假设恒定的饮食浓度可以解释两种污染物和鱼类物种中鱼类浓度变化的 36%至 40%。本研究表明,亚洲鲤鱼对 PCBs 和 Hg 的生物累积率的差异可以部分解释为与每种污染物相关的关键组织储存隔室的生长率差异。这种化学物质特异性生长稀释的差异随后导致 Hg 和 PCBs 在鱼类体内的保留和生物累积模式的差异。