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ObjectiveTo conduct comprehensive assessment of internal and external cadmium exposure and health risks for Shanghai residents. MethodsCadmium levels in food samples were calculated by employing two dietary exposure assessment methods， total diet study （TDS） and food frequency questionnaire （FFQ）， to estimate the daily dietary cadmium exposure of Shanghai residents. The provisional tolerable monthly intake （PTMI） of cadmium set by joint food and agriculture organization/WHO expert committee on food additives （JECFA） was applied to evaluate the health risk. Differences in dietary and urinary cadmium were compared by rank-sum test among different regions， age， gender， smoking status， and BMI groups， and the association between internal and external cadmium exposure was investigated by correlation analysis. ResultsThe mean value of urinary cadmium for 1 300 respondents was 0.542 μg·L-1. Urinary cadmium was higher in the population in central urban and urban-rural fringe areas than in the suburban area， higher in the older age group than in the younger age group， and higher in the smoking group than in the non-smoking group （all P<0.01）. The two assessment methods showed that the mean values of daily dietary cadmium exposure for Shanghai residents were 0.306 and 0.090 μg·kg-1， with 3.69% and 0.85% of Shanghai residents exceeding the PTMI， respectively. Correlation analyses showed that dietary exposure to cadmium based on the FFQ method was positively correlated with the urinary cadmium level when smoking status， age， gender， and BMI were adjusted. ConclusionDietary exposure to cadmium of Shanghai residents is mainly derived from vegetables， aquatic products， cereals and potatoes， and is overall at a low-risk level. Dietary exposure assessment based on FFQ and risk monitoring data can effectively estimate long-term cadmium exposure.
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Background Chloropropanol esters (MCPDE) have attracted much attention in recent years as a kind of new contaminant found in various refined oils. The pollution of 3-monochloropropane-1,2-diol esters (3-MCPDE) is the most prominent. 3-MCPDE is hydrolyzed in organisms to 3-monochloropropane-1,2-diol which has been shown to have reproductive toxicity, nephrotoxicity, and potential carcinogenicity. Infant formula powders can be polluted by 3-MCPDE when refined edible oils are added during production. Objective To assess the risk of exposure to 3-MCPDE related to the consumption of infant formula powders for children aged 0-3 years in Shanghai market using the food consumption data and the data of 3-MCPDE contamination in these foods. Methods Gas chromatography-mass spectrometry was used to determine 3-MCPDE in 133 samples of infant formula powders in Shanghai. Using a multistage stratified random sampling method, a total of 807 infants and toddlers aged 0-3 years were randomly selected from each district/rural/town in Shanghai, including 208 children aged 0-6 months, 276 children aged 6-12 months, and 323 children aged 12-36 months. The food consumption data was investigated using food frequency questionnaire (FFQ) distributed by combining telephone inquiries and face-to-face interviews among guardians. Population's probability distributions of 3-MCPDE exposure were assessed by @Risk 7.5 software and Monte Carlo simulation algorithm. According to the dietary intake assessment model and the tolerable daily intake (TDI) of 3-MCPDE of 2.00 μg·(kg·d)−1 proposed by the European Food Safety Authority (ESFA), a risk assessment of exposure to 3-MCPDE was conducted for infants and toddlers aged 0 to 3 years old in Shanghai who consumed 3-MCPDE via infant formula powders. Results The average concentration of 3-MCPDE in 133 samples of infant formula powders was 0.115 mg·kg−1 with a positive rate of 100.00%. Among different types of formula powders, infant formula powders for infants of 0-6 months had the highest concentrations of 3-MCPDE and fat [0.136 mg·kg−1 and 25.2 g (per 100 g sample) in average respectively]. There was a positive correlation between fat concentration and 3-MCPDE concentration in the samples (r=0.438, P<0.05). The average consumption of infant formula powders of 807 infants aged 0-3 years was 88.3 g·d−1. Among all investigated age groups, the average consumption of infant formula powders by infants aged 0-6, 6-12, and 12-36 months was 87.7, 98.3, and 80.1 g·d−1 respectively. The dietary exposure to 3-MCPDE from infant formula powders of infants aged 0-3 years averaged 0.83 μg·(kg·d)−1 for general intake level or valued 1.44 μg·(kg·d)−1 using the 95 percentile for high intake level. Exposure decreased with increasing age and was highest in infants 0-6 months of age, whose general and high intake levels were 1.41 and 2.34 μg·(kg·d)−1, respectively. The risk population defined with the exposure higher than the TDI proposed by EFSA were proportioned to be 13.90% and 0.50% in infants aged 0-6 months and 6-12 months respectively, indicating a risk that cannot be ignored, and no risk in infants aged 12-36 months. Conclusion Among the investigated infants aged 0-3 years in Shanghai, those aged 0-6 months are at a high risk of exposure to 3-MCPDE. In view of the sensitivity of infants to pollutant exposure, the risk of exposure to 3-MCPDE should be highly concerned.