NOAA Great Lakes Environmental Research Laboratory, 4840 South State Road, Ann Arbor, MI 48108, USA.
Department of Biological Sciences, Wayne State University, 5047 Gullen Mall, Detroit, MI 48202, USA.
Mar Drugs. 2011 Dec;9(12):2553-2571. doi: 10.3390/md9122553. Epub 2011 Dec 8.
Fish consumption is a potential route of human exposure to the hepatotoxic microcystins, especially in lakes and reservoirs that routinely experience significant toxic Microcystis blooms. Understanding the rates of uptake and elimination for microcystins as well as the transfer efficiency into tissues of consumers are important for determining the potential for microcystins to be transferred up the food web and for predicting potential human health impacts. The main objective of this work was to conduct laboratory experiments to investigate the kinetics of toxin accumulation in fish tissue. An oral route of exposure was employed in this study, in which juvenile yellow perch (Perca flavescens) were given a single oral dose of 5 or 20 μg of microcystin-LR (MC-LR) via food and accumulation in the muscle, liver, and tank water were measured over 24 h. Peak concentrations of the water soluble fraction of microcystin were generally observed 8-10 h after dosing in the liver and after 12-16 h in the muscle, with a rapid decline in both tissues by 24 h. Up to 99% of the total recoverable (i.e., unbound) microcystin was measured in the tank water by 16 h after exposure. The relatively rapid uptake and elimination of the unbound fraction of microcystin in the liver and muscle of juvenile yellow perch within 24 h of exposure indicates that fish consumption may not be a major route of human exposure to microcystin, particularly in the Great Lakes.
鱼类摄食是人类接触肝毒性微囊藻毒素的一种潜在途径,特别是在经常发生严重有毒微囊藻水华的湖泊和水库中。了解微囊藻毒素的吸收和消除率以及其向消费者组织中的转移效率,对于确定微囊藻毒素在食物网中转移的潜力以及预测潜在的人类健康影响非常重要。这项工作的主要目的是进行实验室实验,以研究鱼类组织中毒素积累的动力学。本研究采用口服途径,通过食物向幼年黄鲈(Perca flavescens)投喂 5 或 20 μg 的微囊藻毒素-LR(MC-LR),并在 24 小时内测量肌肉、肝脏和水箱水中的毒素积累。在肝脏中,水溶性微囊藻毒素的峰值浓度通常在给药后 8-10 小时观察到,在肌肉中则在 12-16 小时后观察到,24 小时内两个组织中的浓度迅速下降。暴露后 16 小时,水箱水中可回收(即未结合)微囊藻毒素的比例高达 99%。在暴露后 24 小时内,幼年黄鲈肝脏和肌肉中未结合的微囊藻毒素快速吸收和消除,这表明鱼类摄食可能不是人类接触微囊藻毒素的主要途径,尤其是在大湖地区。