Wang Na, Liu Zhe, Sun Yingying, Lu Nan, Luo Yuhu
Institute of Land Engineering and Technology, Shaanxi Provincial Land Engineering Construction Group Co., Ltd., Xi'an, 710021, China.
Shaanxi Provincial Land Engineering Construction Group Co., Ltd., Xi'an, 710075, China.
Sci Rep. 2024 Jan 27;14(1):2273. doi: 10.1038/s41598-024-52886-8.
The study specifically focused on the Hongliulin mining area, where a total of 40 soil samples were meticulously collected and analyzed from within a 1000 m radius extending from the tailings dam. The findings revealed that soil pH within the 0-1000 m range generally leaned towards the alkaline side. In terms of soil nutrient content, encompassing factors such as soil organic matter (SOM), total nitrogen (TN), total phosphorus (TP), total potassium (TK), alkali nitrogen (AK), available phosphorus (AP), and quick-acting potassium (AK), the variations fell within the following ranges: 2.23-13.58 g/kg, 0.12-0.73 g/kg, 0.18-1.15 g/kg, 9.54-35.82 g/kg, 2.89-6.76 mg/kg, 3.45-11.25 mg/kg, and 5.86-130.9 mg/kg. Collectively, these values indicate relatively low levels of soil nutrients. Within the 0-500 m range of soil samples, the average concentrations of Cd, Hg, Pb, and As were 0.778, 0.198, 24.87, and 17.92 mg/kg, respectively. These concentrations exceeded the established soil background values of Shaanxi Province and emerged as the primary pollutants in the study area. Within this same range, the mean values of eight toxic metals (Pi) were ranked in the following descending order: 1.726 (Hg), 1.400 (As), 1.129 (Cr), 1.109 (Pb), 0.623 (Zn), 0.536 (Cd), 0.309 (Cu), and 0.289 (Ni). With the exception of Hg, As, Cr, and Pb, which exhibited slight pollution, the other toxic metals were found to be within acceptable pollution limits for this sampling range, in line with the results obtained using the geo-accumulation index method. The average potential ecological risk index for the eight toxic metals in the study area stood at 185.0, indicating a moderate overall pollution level. When assessing individual elements, the proportions of ecological risk attributed to Hg, As, Pb, and Cd were 34.57%, 27.44%, 25.11%, and 23.11%, respectively. This suggests that the primary potential ecological risk elements in the study area are Hg and As, followed by Cd and Pb. Notably, toxic metals Hg and Pb, as well as As and Pb, exhibited significant positive correlations within the sampling area, suggesting a common source. An analysis of the relationship between soil physicochemical properties and toxic metals indicated that soil pH, SOM, TN, and TP were closely linked to toxic metal concentrations. The toxic metal elements in the research area's soil exhibit moderate variability (0.16 < CV < 0.36) to high variability (CV > 0.36). Within the range of 0-200 m, the CV values for Cd and Hg exceed 1, indicating a high level of variability. The coefficient of variation for SOM, TP, AP, AK and TK is relatively high with the of 2.93, 2.36, 2.36, 21.01, 7.54. The soil in the sampling area has undergone significant disturbances due to human activities, resulting in toxic metal pollution and nutrient deficiencies.
该研究特别聚焦于红柳林矿区,在尾矿坝周围半径1000米范围内精心采集并分析了40个土壤样本。研究结果显示,在0至1000米范围内,土壤pH值总体呈碱性。就土壤养分含量而言,包括土壤有机质(SOM)、全氮(TN)、全磷(TP)、全钾(TK)、碱解氮(AK)、有效磷(AP)和速效钾(AK)等因素,其变化范围如下:2.23 - 13.58克/千克、0.12 - 0.73克/千克、0.18 - 1.15克/千克、9.54 - 35.82克/千克、2.89 - 6.76毫克/千克、3.45 - 11.25毫克/千克以及5.86 - 130.9毫克/千克。总体而言,这些数值表明土壤养分水平相对较低。在0至500米范围内的土壤样本中,镉(Cd)、汞(Hg)、铅(Pb)和砷(As)的平均浓度分别为0.778毫克/千克、0.198毫克/千克、24.87毫克/千克和17.92毫克/千克。这些浓度超过了陕西省既定的土壤背景值,成为研究区域的主要污染物。在同一范围内,八种有毒金属(Pi)的平均值按以下降序排列:汞(Hg)为1.726、砷(As)为1.400、铬(Cr)为1.129、铅(Pb)为1.109、锌(Zn)为0.623、镉(Cd)为0.536、铜(Cu)为0.309、镍(Ni)为0.289。除了汞、砷、铬和铅表现出轻微污染外,其他有毒金属在此采样范围内的污染程度均在可接受范围内,这与地累积指数法的结果一致。研究区域内八种有毒金属的平均潜在生态风险指数为185.0,表明总体污染水平为中等。在评估单个元素时,汞、砷、铅和镉的生态风险比例分别为34.57%、27.44%、25.11%和23.11%。这表明研究区域内主要的潜在生态风险元素是汞和砷,其次是镉和铅。值得注意的是,有毒金属汞和铅以及砷和铅在采样区域内呈现出显著的正相关,表明它们有共同来源。对土壤理化性质与有毒金属之间关系的分析表明,土壤pH值、SOM、TN和TP与有毒金属浓度密切相关。研究区域土壤中的有毒金属元素表现出中等变异性(0.16 < CV < 0.36)至高变异性(CV > 0.36)。在0至200米范围内,镉和汞的CV值超过1,表明变异性较高。SOM、TP、AP、AK和TK的变异系数相对较高,分别为2.93、2.36、2.36以及21.01、7.54。采样区域的土壤因人类活动受到了显著干扰,导致有毒金属污染和养分缺乏。