Department of Sedimentology and Environmental Geology, Faculty of Geoscience and Geography, Georg-August-University Göttingen, Goldschmidtstr. 3, 37077, Göttingen, Germany.
Department of Environment and Resources Management, Faculty of Land Resources and Agricultural Environment, Hue University of Agriculture and Forestry, 102 Phung Hung Street, Hue City, Vietnam.
Environ Geochem Health. 2020 Jan;42(1):191-207. doi: 10.1007/s10653-019-00333-3. Epub 2019 May 28.
Thirty soil samples and 24 corresponding unpolished rice samples along the Red and Huong Rivers in northern and central Vietnam respectively, were analyzed in order to evaluate (a) soil geochemistry, (b) factors that determine the transfer of harmful and nutrient elements from soils into rice grains, (c) health risk to the local population through rice consumption. The concentrations of As, Bi, and U in the soils of this area are higher relative to those of average shale probably due to natural redox-related processes. Also, Zn, Ce, Th, La, Sn, Pb, and Cd are accumulated in some soils because of mining activities or industrial wastewater application. Arsenic concentrations exceed the Vietnamese allowable limit of 15 mg kg in 80% of the tested soils. Twelve percent of the unpolished rice grains surpass the permissible maximum concentration of 0.2 mg Cd kg grain dry matter by FAO/WHO and European Union, and all samples are below the Pb limit. The daily intake of As is within the range of the tolerable intake levels proposed by the European Food Safety Authority. Influences of soil parameters such as pH value, contents of soil organic matter, oxides/hydroxides of Al, Fe, and Mn cause a broad spread of transfer factors from soil to grains. Positive trends exist between the transfer factors within the groups (a) As, Sb, and U, (b) Co, Cu, Ni, and Zn, (c) Cd and Mn which indicate similar influences of soil parameters on their uptake. We propose that the allowable Cd maximum concentration for rice should be set to less than 0.2 mg kg. The analysis of As and Cd concentrations in soils and corresponding rice grains as well as the soil pH value should be made obligatory in order to prevent intoxication. In addition, critical elements from nonferrous metal mining and industrial areas should also be evaluated.
对越南北部和中部红河和湘江沿岸的 30 个土壤样本和 24 个相应的糙米样本进行了分析,以评估 (a) 土壤地球化学,(b) 决定有害和营养元素从土壤转移到水稻籽粒中的因素,(c) 通过食用大米对当地居民的健康风险。由于自然氧化还原相关过程,该地区土壤中的砷、铋和铀浓度相对平均页岩较高。此外,由于采矿活动或工业废水的应用,锌、铈、钍、镧、锡、铅和镉在一些土壤中积累。在测试的土壤中,有 80%的土壤砷浓度超过越南允许的 15mg/kg 限值。12%的糙米超过了 FAO/WHO 和欧盟允许的 0.2mg/kg 干物质最大限量,所有样品均低于铅限量。砷的日摄入量在欧洲食品安全局提出的可耐受摄入量范围内。土壤参数(如 pH 值、土壤有机质含量、Al、Fe 和 Mn 的氧化物/氢氧化物)对从土壤到谷物的迁移因子的广泛传播有影响。在 (a) 砷、锑和铀,(b) 钴、铜、镍和锌,(c) 镉和锰这三个组内,迁移因子之间存在正相关趋势,这表明土壤参数对它们的吸收有类似的影响。我们建议将大米中允许的镉最大浓度设定为小于 0.2mg/kg。为了防止中毒,应该强制分析土壤和相应糙米中的砷和镉浓度以及土壤 pH 值。此外,还应评估来自有色金属矿和工业区的关键元素。