2013—2024年浙江省金华市居民经市售食品膳食镉暴露风险

Risk of dietary cadmium exposure from commercially available foods among residents of Jinhua City of Zhejiang Province from 2013 to 2024

  • 摘要: 目的 了解金华市市售食品镉污染情况,评估金华市居民膳食镉暴露风险,为优化膳食建议和镉暴露风险管理提供科学依据。方法 收集金华市食品安全风险监测系统2013—2024年金华市9个县(市、区) 4434件15类市售食品,包括大米,谷物碾磨加工品,新鲜蔬菜1(叶菜、芹菜、黄花菜) ,新鲜蔬菜2(豆类蔬菜、块根和块茎蔬菜、除芹菜外的茎类蔬菜) ,新鲜蔬菜3(除新鲜蔬菜1、新鲜蔬菜2之外的其他蔬菜) ,新鲜水果,豆类及其制品,坚果及籽类,肉及肉制品,蛋及蛋制品,乳及乳制品,水产鱼类,水产甲壳类(海蟹、虾蛄除外) ,海蟹、虾蛄,其他水产类(双壳贝类、腹足类、头足类、棘皮类)等,检测镉污染情况。结合2023年金华市居民营养监测调查数据,用联合国粮农组织和世界卫生组织食品添加剂联合专家委员会(JECFA)推荐的每月耐受摄入量(PTMI)及安全限值(MOS)评价金华市不同年龄、性别居民的膳食镉暴露健康风险。MOS> 1表明居民经膳食镉暴露风险处于可接受水平; MOS≤1表明居民经膳食镉暴露风险较高。结果 食品中镉检出率为73.55%(3261/4434),超标率为4.06%(180/4434) ;检出率较高的食品主要集中在海蟹、虾蛄(98.59%),新鲜蔬菜1(94.92%),大米(87.93%),豆类及其制品(85.76%),谷物碾磨加工品(85.63%)。所有食品中镉质量分数的中位数为0.01 mg·kg-1;质量分数较高的食品种类有海蟹、虾蛄(0.644 mg·kg-1),大米(0.032 mg·kg-1) ,新鲜蔬菜1 (0.020mg·kg-1 )。居民营养监测调查共纳入2092人,所有食品每人每日平均摄入量为887.97g·d-1,其中新鲜蔬菜为342.17 g·d-1,肉及肉制品为141.29 g·d-1,大米为110.70 g·d-1。以镉质量分数的P50P95作为评价人群暴露风险的一般暴露水平和高暴露水平。在一般暴露水平下,人群镉的平均暴露量为5.15 μg·kg-1(以体重计,后同),MOS值为4.85;不同年龄、性别人群镉的平均暴露量范围为3.97~ 6.80 μg·kg-1,MOS均> 1,居民膳食镉暴露风险处于可接受水平。在高暴露水平下,人群镉的平均暴露量为36.02 μg·kg-1,MOS值为0.69;不同年龄、性别人群镉的平均暴露量范围为27.68~ 48.37 μg·kg-1,MOS范围为0.52~ 0.90,均< 1,居民膳食镉暴露风险较高。金华市居民膳食镉暴露主要食品为大米、新鲜蔬菜,贡献率均超过30%。6~ 17岁未成年人的膳食镉暴露量高于成年人,女性的膳食镉暴露量高于男性。结论 金华市市售食品存在不同程度的镉污染,镉污染水平较高的主要为海蟹、虾蛄等水产类,叶菜、芹菜、黄花菜等新鲜蔬菜和大米。金华市居民膳食镉暴露风险在一般暴露水平下处于可接受水平,在高暴露水平下存在健康风险。应加强对相关食品的镉监测,以及对6~ 17岁未成年人、女性等高风险人群的膳食指导。

     

    Abstract: Objective To investigate the cadmium contamination levels in commercially available foods in Jinhua City, assess the dietary cadmium exposure risk among Jinhua residents, and provide a scientific basis for optimizing dietary recommendations and managing cadmium exposure risks. Methods The detection date from 2013 to 2024, a total of 4434 samples of 15 categories of commercially available foods from the Jinhua Food Safety Risk Monitoring System, including rice, milled and processed grains, fresh vegetables 1 (leafy vegetables, celery, and daylily flowers), fresh vegetables 2 (legume vegetables, root and tuber vegetables, and stem vegetables other than celery), fresh vegetables 3 (all vegetables other than fresh vegetables 1 and fresh vegetables 2), fresh fruits, legumes and legume products, nuts and seeds, meat and meat products, eggs and egg products, milk and dairy products, fish, crustaceans (excluding sea crabs and mantis shrimp), sea crabs and mantis shrimp, other aquatic products (bivalves, gastropods, cephalopods, and echinoderms), were collected from 9 counties (cities and districts) in Jinhua City to assess their cadmium contamination levels. Combined these results with data from the 2023 Jinhua City Resident Nutrition Surveillance Survey, the health risks associated with dietary cadmium exposure among residents of different ages and genders in Jinhua City were assessed according to the Provisional Tolerable Monthly Intake (PTMI) and Maximum Allowable Level (MOS) recommended by the Joint FAO/WHO Expert Committee on Food Additives (JECFA). A MOS > 1 indicates that the risk of dietary cadmium exposure for residents is at an acceptable level; a MOS ≤ 1 indicates that the risk of dietary cadmium exposure for residents is relatively high. Results The cadmium detection rate in food was 73.55% (3261/4434), with 4.06% (180/4434) of samples exceeding the limit. Foods with a high cadmium detection rate were primarily concentrated in sea crabs and mantis shrimp (98.59%), fresh vegetables 1 (94.92%), rice (87.93%), legumes and theirproducts (85.76%), and milled grain products (85.63%). The median cadmium concentration was 0.01 mg·kg-1. Food categories with higher cadmium concentrations included sea crabs and mantis shrimp (0.644 mg·kg-1), rice (0.032 mg·kg-1), and fresh vegetables 1 (0.020 mg·kg-1). A total of 2092 individuals were included in the population nutrition surveillance survey, and the average daily per capita food consumption reached 887.97 g·kg-1, consisting of fresh vegetables (342.17 g·kg-1), meat and meat products (141.29 g·kg-1), and rice (110.70 g·kg-1). The P50 and P95 cadmium mass fractions were used to define general and high exposure levels for assessing population exposure risk. At the general exposure level, the monthly average cadmium exposure for the population was 5.15 μg·kg-1 (based on body weight; same applies below), with an MOS value of 4.85; the range of monthly average cadmium exposure across different age and gender groups was 3.97–6.80 μg·kg-1, with MOS values all >1, indicating that the dietary cadmium exposure risk for the population was at an acceptable level. At the high exposure level, the monthly average cadmium exposure for the population was 36.02 μg·kg-1, with an MOS value of 0.69; the monthly average cadmium exposure levels for different age and gender groups ranged from 27.68 to 48.37 μg·kg-1, with MOS values ranging from 0.52 to 0.90, all of which were < 1; indicating that the dietary cadmium exposure risk for residents was relatively high. Rice and fresh vegetables were the major foods contributing to dietary cadmium exposure among residents in Jinhua City, each accounting for more than 30% of the total exposure contribution. Dietary cadmium exposure among minors aged 6–17 years in Jinhua City was higher than that of adults, and dietary cadmium exposure among females was higher than that among males. Conclusion Commercially available foods in Jinhua City exhibit varying degrees of cadmium contamination, with higher levels primarily found in aquatic products such as sea crabs and mantis shrimp, fresh vegetables such as leafy greens, celery, and daylily buds, as well as rice. The dietary cadmium exposure risk for residents of Jinhua City is at an acceptable level under general exposure conditions but poses a health risk under high exposure conditions. Cadmium monitoring of relevant foods should be strengthened, and dietary guidance should be provided to high-risk groups including minors aged 6–17 years and women.

     

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