首页> 外文期刊>Archives of Environmental Contamination and Toxicology >A survey of dietary intake of polychlorinated dibenzo-p-dioxins, polychlorinated dibenzofurans, and dioxin-like coplanar polychlorinated biphenyls from food during 2000-2002 in Osaka City, Japan.
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A survey of dietary intake of polychlorinated dibenzo-p-dioxins, polychlorinated dibenzofurans, and dioxin-like coplanar polychlorinated biphenyls from food during 2000-2002 in Osaka City, Japan.

机译:日本大阪市2000-2002年间食物中多氯二苯并-对-二恶英,多氯二苯并呋喃和类二恶英共平面多氯联苯的饮食摄入量调查。

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Studies of the dietary intake of polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs), and dioxin-like coplanar polychlorinated biphenyls (dioxin-like PCBs), collectively referred as dioxins, were conducted using the total diet study (TDS) method with food purchased in Osaka City, Japan during 2000-2002. The daily intake of dioxin-TEQ (toxic equivalent) from food per adult person was estimated respectively as 104.24 pg TEQ/person/day in 2000, 72.73 pg TEQ/person/day in 2001, and 87.28 pg TEQ/person/day in 2002, corresponding to 2.08, 1.45, and 1.74 pg TEQ/kg body weight (bw)/day for an adult weighing 50 kg. The highest contribution ratio to the total intake of dioxin-TEQ was from fish and shellfish (group 10) in each year, accounting for 77-92%. The next highest contributor was meat and eggs (groups 11-A and 11-B). An annual decrease of the intake of dioxin-TEQ was not observed clearly. Otherwise, the dietary intake of non-2,3,7,8-substituted PCDDs/PCDFs were estimated together. The intake of 1,3,6,8-TeCDD came mostly from intake of fish and shellfish (group 10), green vegetable (group 7), and the other vegetables, including mushrooms and seaweed (group 8). In addition, the intake of 1,3,6,8-TeCDF, which reportedly antagonizes 2,3,7,8-TeCDD-mediated aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) induction activities, was an insufficient amount to suppress 2,3,7,8-TeCDD-mediated activities. Furthermore, we discussed different TEQ compositions of PCDDs/PCDFs to dioxin-like PCBs from food intake and in human samples and inferred that the difference was caused by low bioaccumulation properties of 3,3',4,4',5-PeCB (PCB 126).
机译:使用总饮食研究(TDS)对多氯二苯并对二恶英(PCDD),多氯二苯并呋喃(PCDF)和类二恶英共平面多氯联苯(类二恶英PCB)的饮食摄入进行了研究。 )方法,使用2000-2002年在日本大阪市购买的食物。 2000年每个成年人每天从食物中摄入的二恶英-TEQ(有毒当量)分别为2001年的104.24 pg TEQ /人/天,2001年的72.73 pg TEQ /人/天和2002年的87.28 pg TEQ /人/天。 ,相当于体重为50公斤的成年人每天的2.08、1.45和1.74 pg TEQ /公斤体重(bw)/天。每年来自鱼类和贝类(第10组)的二恶英-TEQ总摄入量贡献率最高,占77-92%。第二大贡献者是肉和蛋(11-A和11-B组)。没有清楚地观察到二恶英-TEQ的摄入量逐年减少。否则,应一起估算非2,3,7,8取代的PCDD / PCDF的饮食摄入量。 1,3,6,8-TeCDD的摄入主要来自鱼类和贝类(第10组),绿色蔬菜(第7组)以及其他蔬菜(包括蘑菇和海藻)(第8组)的摄入。此外,据报道摄入的1,3,6,8-TeCDF拮抗2,3,7,8-TeCDD介导的芳烃羟化酶(AHH)和乙氧基试卤灵O-脱乙基酶(EROD)的诱导活性。抑制2,3,7,8-TeCDD介导的活性。此外,我们讨论了食物摄入量和人体样品中PCDDs / PCDFs与二恶英样PCBs不同的TEQ组成,并推断出差异是由于3,3',4,4',5-PeCB(PCB)的低生物累积特性引起的126)。

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