Zhang Long, Song Bo, Huang Feng-Yan, Xiao Nai-Chuan, Dun Meng-Jie
College of Environmental Science and Engineering, Guilin University of Technology, Guilin 541004, China.
Collaborative Innovation Center for Water Pollution Control and Water Safety Guarantee in Karst Area, Guilin 541004, China.
Huan Jing Ke Xue. 2022 Mar 8;43(3):1558-1566. doi: 10.13227/j.hjkx.202105162.
This study used 193 sets of farmland soil and agricultural product samples collected from around a tin mine in Hunan Province, China, to explore the antimony (Sb) content characteristics and pollution status of soil and agricultural products and to provide a scientific basis for the prevention and control of soil antimony pollution in antimony mining areas and the safe use of farmland. We analyzed the amount of antimony in the soil, basic physical and chemical properties, and antimony content in agricultural products; studied the characteristics of antimony migration and transformation in the soil-agricultural product system; and conducted safety assessments on soil and agricultural products. The results showed that the soil (Sb) in the central area of the mine, the southern area of the mine, the central township area, the urban-rural transfer area, and the northern area of the mine reached (2348±2165), (1298±884.1), (311.8±526.5), (302.5±355.9), and (215.6±183.2) mg·kg, and the exceeding multiples reached 65.22, 36.06, 8.66, 8.40, and 5.99 times, respectively. The antimony enrichment coefficients of lettuce, scallion, cabbage, water spinach, garlic, and pea seedlings in agricultural products were 0.01-0.1, which indicated good antimony absorption capacity. The antimony enrichment coefficients of loofah, asparagus lettuce, pepper, carrot, bitter gourd, corn, eggplant, cowpea, and celery were less than 0.01, and the antimony absorption capacity was relatively poor. The safety assessment results showed that roots, allium, and garlic vegetables had a high risk of antimony pollution; leafy vegetables and legumes had a higher risk of antimony pollution; and solanaceous vegetables, melons, and fruit vegetables and corn (cereals) had a high risk of antimony pollution. Therefore, it is urgent to take soil antimony pollution control measures in the mining area. At the same time, in order to realize the safe use of agricultural land in the mining area, the farmland far away from the low antimony content of the soil in the central area of the mine should be selected as the planting area, and the agricultural products with weak antimony absorption capacity should be planted first.
本研究采集了中国湖南省某锡矿周边193套农田土壤和农产品样本,以探究土壤和农产品中锑(Sb)的含量特征及污染状况,为锑矿区土壤锑污染防治及农田安全利用提供科学依据。我们分析了土壤中锑的含量、基本理化性质以及农产品中的锑含量;研究了锑在土壤 - 农产品系统中的迁移转化特征;并对土壤和农产品进行了安全性评价。结果表明,矿区中心区域、矿区南部区域、中心乡镇区域、城乡交接区域和矿区北部区域土壤中锑含量分别达到(2348±2165)、(1298±884.1)、(311.8±526.5)、(302.5±355.9)和(215.6±183.2)mg·kg,超标倍数分别达到65.22、36.06、8.66、8.40和5.99倍。农产品中生菜、葱、白菜、空心菜、大蒜和豌豆苗的锑富集系数为0.01 - 0.1,表明锑吸收能力良好。丝瓜、莴笋、辣椒、胡萝卜、苦瓜、玉米、茄子、豇豆和芹菜的锑富集系数小于0.01,锑吸收能力相对较差。安全性评价结果显示,根菜类、葱蒜类蔬菜锑污染风险高;叶菜类和豆类蔬菜锑污染风险较高;茄果类、瓜类和果菜类以及玉米(谷类)锑污染风险高。因此,矿区亟待采取土壤锑污染控制措施。同时,为实现矿区农田的安全利用,应选择远离矿区中心区域土壤锑含量低的农田作为种植区,并优先种植锑吸收能力弱的农产品。