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本文引用的文献

1
Inorganic arsenic and basal cell carcinoma in areas of Hungary, Romania, and Slovakia: a case-control study.匈牙利、罗马尼亚和斯洛伐克地区无机砷与基底细胞癌的病例对照研究。
Environ Health Perspect. 2012 May;120(5):721-6. doi: 10.1289/ehp.1103534. Epub 2012 Jan 31.
2
Arsenic, organic foods, and brown rice syrup.砷、有机食品和糙米糖浆。
Environ Health Perspect. 2012 May;120(5):623-6. doi: 10.1289/ehp.1104619. Epub 2012 Feb 16.
3
Pancreatic cancer risk and levels of trace elements.胰腺癌风险与微量元素水平。
Gut. 2012 Nov;61(11):1583-8. doi: 10.1136/gutjnl-2011-301086. Epub 2011 Dec 19.
4
Critical windows of exposure for arsenic-associated impairment of cognitive function in pre-school girls and boys: a population-based cohort study.砷相关认知功能损害的幼儿暴露关键期:基于人群的队列研究。
Int J Epidemiol. 2011 Dec;40(6):1593-604. doi: 10.1093/ije/dyr176.
5
Rice consumption contributes to arsenic exposure in US women.食用大米会导致美国女性砷暴露。
Proc Natl Acad Sci U S A. 2011 Dec 20;108(51):20656-60. doi: 10.1073/pnas.1109127108. Epub 2011 Dec 5.
6
Variation in grain arsenic assessed in a diverse panel of rice (Oryza sativa) grown in multiple sites.在多个地点种植的多种水稻(Oryza sativa)品种中评估的谷物砷变异性。
New Phytol. 2012 Feb;193(3):650-664. doi: 10.1111/j.1469-8137.2011.03983.x. Epub 2011 Dec 5.
7
Humans seem to produce arsenobetaine and dimethylarsinate after a bolus dose of seafood.人体摄入大量海鲜后似乎会产生砷甜菜碱和二甲基砷酸盐。
Environ Res. 2012 Jan;112:28-39. doi: 10.1016/j.envres.2011.11.007. Epub 2011 Dec 2.
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Human exposure to arsenic through foodstuffs cultivated using arsenic contaminated groundwater in areas of West Bengal, India.印度西孟加拉邦部分地区使用受砷污染地下水种植的食物导致人体砷暴露。
J Environ Sci Health A Tox Hazard Subst Environ Eng. 2011;46(11):1259-65. doi: 10.1080/10934529.2011.598810.
9
Speciation of arsenic in rice and estimation of daily intake of different arsenic species by Brazilians through rice consumption.砷在大米中的形态分析及巴西人通过食用大米对不同砷形态摄入量的评估。
J Hazard Mater. 2011 Jul 15;191(1-3):342-8. doi: 10.1016/j.jhazmat.2011.04.087. Epub 2011 Apr 27.
10
Arsenic and manganese exposure and children's intellectual function.砷和锰暴露与儿童智力功能。
Neurotoxicology. 2011 Aug;32(4):450-7. doi: 10.1016/j.neuro.2011.03.009. Epub 2011 Mar 29.

美国儿童的大米摄入量与尿液砷浓度。

Rice consumption and urinary arsenic concentrations in U.S. children.

机构信息

Institute for Quantitative Biomedical Sciences, Geisel School of Medicine at Dartmouth, Hanover, New Hampshire 03756, USA.

出版信息

Environ Health Perspect. 2012 Oct;120(10):1418-24. doi: 10.1289/ehp.1205014. Epub 2012 Sep 24.

DOI:10.1289/ehp.1205014
PMID:23008276
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC3491944/
Abstract

BACKGROUND

In adult populations, emerging evidence indicates that humans are exposed to arsenic by ingestion of contaminated foods such as rice, grains, and juice; yet little is known about arsenic exposure among children.

OBJECTIVES

Our goal was to determine whether rice consumption contributes to arsenic exposure in U.S. children.

METHODS

We used data from the nationally representative National Health and Nutrition Examination Survey (NHANES) to examine the relationship between rice consumption (measured in 0.25 cups of cooked rice per day) over a 24-hr period and subsequent urinary arsenic concentration among the 2,323 children (6-17 years of age) who participated in NHANES from 2003 to 2008. We examined total urinary arsenic (excluding arsenobetaine and arsenocholine) and dimethylarsinic acid (DMA) concentrations overall and by age group: 6-11 years and 12-17 years.

RESULTS

The median [interquartile range (IQR)] total urinary arsenic concentration among children who reported consuming rice was 8.9 μg/L (IQR: 5.3-15.6) compared with 5.5 μg/L (IQR: 3.1-8.4) among those who did not consume rice. After adjusting for potentially confounding factors, and restricting the study to participants who did not consume seafood in the preceding 24 hr, total urinary arsenic concentration increased 14.2% (95% confidence interval: 11.3, 17.1%) with each 0.25 cup increase in cooked rice consumption.

CONCLUSIONS

Our study suggests that rice consumption is a potential source of arsenic exposure in U.S. children.

摘要

背景

在成年人群体中,有新的证据表明,人类通过摄入受污染的食物,如大米、谷物和果汁,会接触到砷;然而,人们对儿童接触砷的情况知之甚少。

目的

我们的目标是确定食用大米是否会导致美国儿童接触砷。

方法

我们利用来自具有全国代表性的国家健康和营养调查(NHANES)的数据,考察了在 24 小时内食用 0.25 杯煮熟的大米(以每 0.25 杯为单位)与 2003 年至 2008 年期间参与 NHANES 的 2323 名儿童(6-17 岁)的后续尿液砷浓度之间的关系。我们检测了总尿液砷(不包括砷甜菜碱和砷胆碱)和二甲基砷酸(DMA)浓度,总体以及按年龄组(6-11 岁和 12-17 岁)进行了检测。

结果

报告食用大米的儿童的中位数[四分位距(IQR)]总尿液砷浓度为 8.9μg/L(IQR:5.3-15.6),而不食用大米的儿童为 5.5μg/L(IQR:3.1-8.4)。在调整了潜在的混杂因素后,并将研究限制在过去 24 小时内未食用海鲜的参与者中,总尿液砷浓度随着每增加 0.25 杯煮熟的大米摄入量而增加 14.2%(95%置信区间:11.3,17.1%)。

结论

我们的研究表明,食用大米是美国儿童砷暴露的一个潜在来源。