Department of Biological and Environmental Science, University of Jyväskylä, Finland.
Food Addit Contam Part A Chem Anal Control Expo Risk Assess. 2012;29(9):1475-88. doi: 10.1080/19440049.2012.694373. Epub 2012 Jul 6.
Food is contaminated by polychlorinated dibenzo-p-dioxins and furans (PCDD/F), polychlorinated biphenyls (PCB) and polybrominated diphenylethers (PBDE) worldwide. Previous data show elevated intakes in children. We determined intakes of POPs in Finnish children. Because no children-specific safe limit values exist, we used tolerable daily intakes (TDIs) set for adults by international expert bodies to examine the proportion of the study population that exceed those limits. We utilised dietary monitoring data with food consumption of Finnish boys and girls aged 1-6 years, measured the contaminant concentrations in all the main food items and calculated age-specific contaminant sum and congener-specific long-term daily intake levels. Our food intake and contaminant data correspond to years 2002-2005. The long-term upper-bound dioxin intakes ranged between 0.1 and 12.8 pg WHO(PCDD/F-PCB)-TEQ/kg bw/d (min and max). An immediate TDI for WHO(PCDD/F-PCB)-TEQs of 4.0 pg/kg bw/d were exceeded by 2.5%-7.5% of the children. PBDE long-term upper-bound intake was between 0.1 and 5.8 ng/kg bw/d (min and max). Congener-specific analyses indicated a typical Finnish adult exposure pattern of the children to PCDD/Fs, PCBs and PBDEs. The highest POP intakes were observed in children aged 3 years. Long-term daily PCDD/F, PCB and PBDE intakes among Finnish children varied greatly between individuals and ages. In each age group of the study population, there was a proportion of children with their WHO(PCDD/F-PCB)-TEQ intake exceeding considered safe limits set for adults. Based on the exposure profile reported herein, children should be clearly considered as a specific sub-population in food-mediated contaminant risk assessment.
全世界的食物都受到多氯二苯并对二恶英和呋喃(PCDD/F)、多氯联苯(PCB)和多溴二苯醚(PBDE)的污染。以前的数据显示,儿童摄入这些污染物的水平较高。我们确定了芬兰儿童的 POPs 摄入量。由于不存在针对儿童的安全限量值,我们使用国际专家机构为成年人设定的可耐受每日摄入量(TDI)来检查超过这些限量值的研究人群比例。我们利用了芬兰 1-6 岁男孩和女孩的饮食监测数据,测量了所有主要食物中污染物的浓度,并计算了年龄特异性污染物总和和同类物特异性长期每日摄入量水平。我们的食物摄入量和污染物数据与 2002-2005 年相对应。长期最高边界二恶英摄入量在 0.1 到 12.8 pg WHO(PCDD/F-PCB)-TEQ/kg bw/d(最小和最大)之间。儿童中有 2.5%-7.5%超过了 4.0 pg/kg bw/d 的 WHO(PCDD/F-PCB)-TEQ 的即时 TDI。PBDE 的长期最高边界摄入量在 0.1 到 5.8 ng/kg bw/d(最小和最大)之间。同类物特异性分析表明,儿童对 PCDD/Fs、PCBs 和 PBDEs 的暴露模式具有典型的芬兰成年人特征。3 岁儿童的 POP 摄入量最高。芬兰儿童长期每日 PCDD/F、PCB 和 PBDE 摄入量在个体和年龄之间差异很大。在研究人群的每个年龄组中,都有一部分儿童的 WHO(PCDD/F-PCB)-TEQ 摄入量超过了为成年人设定的认为安全的限值。基于本文报告的暴露情况,儿童在食物介导的污染物风险评估中应明确被视为一个特定的亚人群。