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Environ Res. 2012 Apr;114:12-23. doi: 10.1016/j.envres.2012.02.004. Epub 2012 Mar 9.
2
Consumption patterns and risk assessment of crab consumers from the Newark Bay Complex, New Jersey, USA.美国新泽西州纽瓦克湾复杂区域蟹类消费者的消费模式和风险评估。
Sci Total Environ. 2011 Oct 1;409(21):4536-44. doi: 10.1016/j.scitotenv.2011.07.017. Epub 2011 Aug 24.
3
Disproportionate exposures in environmental justice and other populations: the importance of outliers.环境正义和其他人群中的不成比例暴露:离群值的重要性。
Am J Public Health. 2011 Dec;101 Suppl 1(Suppl 1):S53-63. doi: 10.2105/AJPH.2011.300121. Epub 2011 May 6.
4
Conceptual environmental justice model for evaluating chemical pathways of exposure in low-income, minority, native American, and other unique exposure populations.概念性环境公正模型,用于评估低收入、少数族裔、美国原住民和其他特殊暴露人群中的化学暴露途径。
Am J Public Health. 2011 Dec;101 Suppl 1(Suppl 1):S64-73. doi: 10.2105/AJPH.2010.300077. Epub 2011 May 6.
5
Mercury and selenium levels in 19 species of saltwater fish from New Jersey as a function of species, size, and season.新泽西州 19 种海水鱼的汞和硒含量随物种、大小和季节的变化。
Sci Total Environ. 2011 Mar 15;409(8):1418-29. doi: 10.1016/j.scitotenv.2010.12.034. Epub 2011 Feb 2.
6
Racial and geographic differences in fish consumption: the REGARDS study.鱼类摄入的种族和地域差异:REGARDS 研究。
Neurology. 2011 Jan 11;76(2):154-8. doi: 10.1212/WNL.0b013e3182061afb. Epub 2010 Dec 22.
7
Fish consumption and mercury exposure among Louisiana recreational anglers.路易斯安那州休闲垂钓者的鱼类消费和汞暴露情况。
Environ Health Perspect. 2011 Feb;119(2):245-51. doi: 10.1289/ehp.1002609. Epub 2010 Oct 27.
8
Fish consumption and prostate cancer risk: a review and meta-analysis.鱼类摄入与前列腺癌风险:综述与荟萃分析。
Am J Clin Nutr. 2010 Nov;92(5):1223-33. doi: 10.3945/ajcn.2010.29530. Epub 2010 Sep 15.
9
Hair mercury levels of women of reproductive age in Ontario, Canada: implications to fetal safety and fish consumption.加拿大安大略省育龄妇女的头发汞含量:对胎儿安全和鱼类消费的影响。
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10
Hair mercury levels, fish consumption, and cognitive development in preschool children from Granada, Spain .西班牙格拉纳达学龄前儿童的头发汞水平、鱼类摄入量与认知发育
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自捕鱼类在休闲渔民鱼类总消费率中的作用:某些物种的平均消费量超过了可接受摄入量。

Role of self-caught fish in total fish consumption rates for recreational fishermen: Average consumption for some species exceeds allowable intake.

作者信息

Burger Joanna

机构信息

Division of Life Sciences, and Environmental and Occupational Health Sciences Institute, Rutgers University, 604 Allison Road, Piscataway, NJ, USA.

出版信息

J Risk Res. 2013;16(8):1057-1075. doi: 10.1080/13669877.2013.788546.

DOI:10.1080/13669877.2013.788546
PMID:23914136
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC3728903/
Abstract

Studies of fish consumption focus on recreational or subsistence fishing, on awareness and adherence to advisories, consumption patterns, and contaminants in fish. Yet the general public obtains their fish from commercial sources. In this paper I examine fish consumption patterns of recreational fishermen in New Jersey to determine: 1) consumption rates for self-caught fish and for other fish, 2) meals consumed per year, 3) average meal size, and average daily intake of mercury, and 4) variations in these parameters for commonly-consumed fish, and different methods of computing intake. Over 300 people were interviewed at fishing sites and fishing clubs along the New Jersey shore. Consumption patterns of anglers varied by species of fish. From 2 to 90 % of the anglers ate the different fish species, and between 9 and 75 % gave fish away to family or friends. Self-caught fish made up 7 to 92 % of fish diets. On average, self-caught fish were eaten for only 2 to 6 months of the year, whereas other fish (commercial or restaurant) were eaten up to 10 months a year. Anglers consumed from 5 to 36 meals of different fish a year, which resulted in intake of mercury ranging from 0.01 to 0.22 ug/kg/day. Average intake of Mako shark, swordfish, and tuna (sushi, canned tuna, self-caught tuna) exceeded the U.S. Environmental Protection Agency's oral, chronic reference dose for mercury of 0.1 ug/kg/day. However, computing intake using consumption for the highest month results in average mercury intake exceeding the reference dose for striped bass and bluefish as well. These data, and the variability in consumption patterns, have implications for risk assessors, risk managers, and health professionals.

摘要

对鱼类消费的研究主要集中在休闲或自给性捕鱼、对相关建议的认知和遵守情况、消费模式以及鱼类中的污染物。然而,普通公众的鱼类来源是商业渠道。在本文中,我研究了新泽西州休闲渔民的鱼类消费模式,以确定:1)自捕鱼和其他鱼类的消费率;2)每年食用的餐数;3)平均每餐食量以及汞的日均摄入量;4)常见食用鱼类这些参数的变化情况,以及不同的摄入量计算方法。在新泽西海岸的捕鱼地点和钓鱼俱乐部对300多人进行了访谈。垂钓者的消费模式因鱼类品种而异。2%至90%的垂钓者食用不同的鱼类品种,9%至75%的垂钓者会将鱼送给家人或朋友。自捕鱼在鱼类饮食中占7%至92%。平均而言,自捕鱼一年仅食用2至6个月,而其他鱼类(商业捕捞或餐厅提供)一年食用时间长达10个月。垂钓者每年食用5至36餐不同的鱼类,汞摄入量在0.01至0.22微克/千克/天之间。马科鲨鱼、箭鱼和金枪鱼(寿司、罐装金枪鱼、自捕金枪鱼)的平均摄入量超过了美国环境保护局规定的汞的口服慢性参考剂量0.1微克/千克/天。然而,使用最高月份的消费量来计算摄入量,条纹鲈和蓝鳍金枪鱼的平均汞摄入量也会超过参考剂量。这些数据以及消费模式的变异性,对风险评估者、风险管理者和健康专业人员具有启示意义。

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