Suppr超能文献

泰国西北部镉污染地区基于镉的日均摄入量和尿排泄量的推荐大米摄入量水平。

Recommended Rice Intake Levels Based on Average Daily Dose and Urinary Excretion of Cadmium in a Cadmium-Contaminated Area of Northwestern Thailand.

作者信息

La-Up Aroon, Wiwatanadate Phongtape, Pruenglampoo Sakda, Uthaikhup Sureeporn

机构信息

Department of Community Medicine, Faculty of Medicine, Chiang Mai University, Chiang Mai, Thailand.

Research Institute for Health Sciences, Chiang Mai University, Chiang Mai, Thailand.

出版信息

Toxicol Res. 2017 Oct;33(4):291-297. doi: 10.5487/TR.2017.33.4.291. Epub 2015 Oct 15.

Abstract

This study was performed to investigate the dose-response relationship between average daily cadmium dose (ADCD) from rice and the occurrence of urinary cadmium (U-Cd) in individuals eating that rice. This was a retrospective cohort designed to compare populations from two areas with different levels of cadmium contamination. Five-hundred and sixty-seven participants aged 18 years or older were interviewed to estimate their rice intake, and were assessed for U-Cd. The sources of consumed rice were sampled for cadmium measurement, from which the ADCD was estimated. Binary logistic regression was used to examine the association between ADCD and U-Cd (cut-off point at 2 μg/g creatinine), and a correlation between them was established. The lowest estimate was ADCD = 0.5 μg/kg bw/day [odds ratio (OR) = 1.71; with a 95% confidence interval (CI) 1.02-2.87]. For comparison, the relationship in the contaminated area is expressed by ADCD = 0.7 μg/kg bw/day, OR = 1.84; [95 % CI, 1.06-3.19], while no relationship was found in the non-contaminated area, meaning that the highest level at which this relationship does not exist is ADCD = 0.6 μg/kg bw/day [95% CI, 0.99-2.95]. Rice, as a main staple food, is the most likely source of dietary cadmium. Abstaining from or limiting rice consumption, therefore, will increase the likelihood of maintaining U-Cd within the normal range. As the recommended maximum ADCD is not to exceed 0.6 μg/kg bw/day, the consumption of rice grown in cadmium-contaminated areas should not be more than 246.8 g/day. However, the exclusion of many edible plants grown in the contaminated area from the analysis might result in an estimated ADCD that does not reflect the true level of cadmium exposure among local people.

摘要

本研究旨在调查食用大米的人群中,大米平均每日镉摄入量(ADCD)与尿镉(U-Cd)发生情况之间的剂量反应关系。这是一项回顾性队列研究,旨在比较来自两个镉污染水平不同地区的人群。对567名18岁及以上的参与者进行访谈,以估计他们的大米摄入量,并对其尿镉进行评估。采集所食用大米的样本进行镉含量测定,并据此估算平均每日镉摄入量。采用二元逻辑回归分析平均每日镉摄入量与尿镉(以2μg/g肌酐为临界值)之间的关联,并确定二者之间的相关性。最低估计值为平均每日镉摄入量=0.5μg/kg体重/天[比值比(OR)=1.71;95%置信区间(CI)为1.02 - 2.87]。作为对比,污染地区的关系表示为平均每日镉摄入量=0.7μg/kg体重/天,OR = 1.84;[95%CI,1.06 - 3.19],而在未受污染地区未发现这种关系,这意味着不存在这种关系的最高水平为平均每日镉摄入量=0.6μg/kg体重/天[95%CI,0.99 - 2.95]。大米作为主要主食,是膳食镉最可能的来源。因此,不吃或限制大米消费将增加使尿镉维持在正常范围内的可能性。由于建议的平均每日镉摄入量最大不超过0.6μg/kg体重/天,在镉污染地区种植的大米消费量不应超过246.8克/天。然而,分析中排除了许多在污染地区种植的可食用植物,这可能导致所估算的平均每日镉摄入量无法反映当地居民真实的镉暴露水平。

相似文献

3
Human health risk assessment of cadmium exposure through rice consumption in cadmium-contaminated areas of the Mae Tao sub-district, Tak, Thailand.
Environ Geochem Health. 2020 Aug;42(8):2331-2344. doi: 10.1007/s10653-019-00410-7. Epub 2019 Sep 9.
5
Applying Cadmium Relative Bioavailability to Assess Dietary Intake from Rice to Predict Cadmium Urinary Excretion in Nonsmokers.
Environ Sci Technol. 2017 Jun 20;51(12):6756-6764. doi: 10.1021/acs.est.7b00940. Epub 2017 Jun 7.
6
Effects of low-dose cadmium exposure on biological examinations.
Sci Total Environ. 2003 Jun 1;308(1-3):49-62. doi: 10.1016/S0048-9697(02)00646-0.
7
Cadmium exposure via diet and its implication on the derivation of health-based soil screening values in China.
J Expo Sci Environ Epidemiol. 2015 Jul-Aug;25(4):433-42. doi: 10.1038/jes.2015.5. Epub 2015 Mar 4.
10
Cadmium induced renal dysfunction among residents of rice farming area downstream from a zinc-mineralized belt in Thailand.
Toxicol Lett. 2010 Sep 15;198(1):26-32. doi: 10.1016/j.toxlet.2010.04.023. Epub 2010 May 11.

本文引用的文献

1
Is Urinary Cadmium a Biomarker of Long-term Exposure in Humans? A Review.
Curr Environ Health Rep. 2016 Dec;3(4):450-458. doi: 10.1007/s40572-016-0107-y.
2
Cadmium Exposure and Potential Health Risk from Foods in Contaminated Area, Thailand.
Toxicol Res. 2016 Jan;32(1):65-72. doi: 10.5487/TR.2016.32.1.065. Epub 2016 Jan 31.
5
Biomonitoring of mercury, cadmium, and lead exposure in Japanese children: a cross-sectional study.
Environ Health Prev Med. 2015 Jan;20(1):18-27. doi: 10.1007/s12199-014-0416-4. Epub 2014 Oct 8.
6
Cadmium transport and tolerance in rice: perspectives for reducing grain cadmium accumulation.
Rice (N Y). 2012 Feb 27;5(1):5. doi: 10.1186/1939-8433-5-5. eCollection 2012.
7
Differences in urine cadmium associations with kidney outcomes based on serum creatinine and cystatin C.
Environ Res. 2011 Nov;111(8):1236-42. doi: 10.1016/j.envres.2011.07.012. Epub 2011 Aug 25.
8
Current status of cadmium as an environmental health problem.
Toxicol Appl Pharmacol. 2009 Aug 1;238(3):201-8. doi: 10.1016/j.taap.2009.04.020. Epub 2009 May 3.
9
Update of US FDA's Total Diet Study food list and diets.
J Expo Sci Environ Epidemiol. 2007 Sep;17(6):573-82. doi: 10.1038/sj.jes.7500554. Epub 2007 Apr 4.

文献AI研究员

20分钟写一篇综述,助力文献阅读效率提升50倍。

立即体验

用中文搜PubMed

大模型驱动的PubMed中文搜索引擎

马上搜索

文档翻译

学术文献翻译模型,支持多种主流文档格式。

立即体验