淡水鱼中恩诺沙星的残留量及其暴露评估

Distribution and exposure assessment of enrofloxacin residues in freshwater fish

  • 摘要:
    目的 了解淡水鱼中恩诺沙星残留的分布情况,评估上海地区消费者食用淡水鱼后恩诺沙星的暴露风险,为控制淡水鱼抗生素残留提供参考。
    方法 采集上海市草鱼、鳊鱼、泥鳅、黄鳝并进行恩诺沙星给药喂养后,按淡水鱼种类和重量共分为42组,分别采集鱼肉、鱼皮进行恩诺沙星残留量检验。另在市场随机购买44组鳊鱼、泥鳅、黄鳝,按带皮鱼肉、不带皮鱼肉分别检测恩诺沙星残留量,并进行暴露风险评估。
    结果 42组给药喂养后的淡水鱼鱼皮恩诺沙星残留量平均水平高于鱼肉(M=659.38 μg·kg-1M=460.83 μg·kg-1z=-2.212,P=0.027)。44组市售淡水鱼带皮鱼肉和不带皮鱼肉恩诺沙星超标率为36.36%和29.55%。上海市成人和儿童通过食用淡水鱼的带皮鱼肉摄入恩诺沙星的暴露量中位数、P95、最大值均大于食用不带皮鱼肉。儿童在食用带皮鱼肉摄入恩诺沙星最大暴露安全限值(MOS)>1,其余情况儿童和成人的MOS<1。
    结论 淡水鱼鱼皮恩诺沙星含量普遍高于鱼肉。上海地区淡水鱼恩诺沙星残留量风险在总体可控范围内,但儿童食用带皮鱼肉的恩诺沙星急性暴露下存在一定风险。

     

    Abstract:
    Objective To understand the distribution of enrofloxacin (ENR) residues in freshwater fish, to evaluate the dietary exposure risk to ENR for consumers through the consumption of different freshwater fish in Shanghai, and to provide a reference for controlling antibiotic residues in freshwater fish.
    Methods Grass carp, Wuchang bream, pond loach, and Asian swamp eels were purchased from the markets in Shanghai. After being fed with ENR, the fish were divided into 42 batches according to their species and weight, and thereafter ENR residues in the muscles and skin of the fish were measured. In addition, a total of 44 batches of Wuchang bream, pond loach, Asian swamp eels were purchased from the markets, and the ENR residues in the muscles with or without the fish skin were measured, and the exposure risk was evaluated.
    Results The average residues of ENR in skin of the freshwater fish after being fed with drugs in the 42 groups were higher than those in muscles (M=659.38 μg·kg-1, M=460.83 μg·kg-1; z=-2.212, P=0.027). The over-standard rates of ENR residues in the muscles with or without skin 44 batches of freshwater fish of sold in Shanghai were 36.36% and 29.55%, respectively. The median exposure, P95 exposure, and maximum exposure to ENR through the consumption of the muscles with the skin for adults and children in Shanghai were higher than those through the consumption of muscles without the skin. For children, the margin of safety (MOS) for the max exposure to ENR by consuming the muscles with the skin was more than 1, while the MOS was less than 1 in all other cases for both children and adults.
    Conclusion The ENR residues in the skin of freshwater fish are generally higher than those in the muscles. The risk of ENR residues in freshwater fish sold in Shanghai is within a controllable range. However, there might be a certain risk of acute exposure to ENR for children by consuming muscles with the skin of freshwater fish.

     

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