La-Up Aroon, Wiwatanadate Phongtape, Pruenglampoo Sakda, Uthaikhup Sureeporn
Department of Community Medicine, Faculty of Medicine, Chiang Mai University, Chiang Mai, Thailand.
Research Institute for Health Sciences, Chiang Mai University, Chiang Mai, Thailand.
Toxicol Res. 2017 Oct;33(4):291-297. doi: 10.5487/TR.2017.33.4.291. Epub 2015 Oct 15.
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.
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。