Heavy metal contamination of agricultural soils around a chromite mine in Vietnam

Abstract

In Vietnam, the Co Dinh mine is the largest chromite mine in the country. Mining, ore dressing and disposal of the tailings provide obvious sources of heavy metal contamination in the mine area. The present study examined the influence of chromite mining activities on the adjacent lowland paddy field by investigating heavy metal and As levels in the mine tailings, sediments, paddy soils and water. At paddy fields located near the mine tailings, the total contents of Cr, Co and Ni were 5,750, 375 and 5,590?mg?kg^?1, and the contents of their water-extractable form were 12.7, 1.16 and 32.3?mg?kg^?1, respectively. These results revealed severe contamination of lowland paddy soils with Cr, Co and Ni as a result of mining activity, suggesting serious health hazards through agricultural products, including livestock in this area. The principal source of the pollution was sediment inflow owing to the collapse of the dike, which was poorly constructed by heaping up soil. Moreover, water flowing out from the mining area was also polluted with Cr and Ni (15.0–41.0 and 20.0–135?μg?L^?1, respectively). This might raise another problem of heavy metal pollution of watercourses in the area, indicating the need for further investigation and monitoring of fluctuations of water quality with seasonal changes.     

Heavy metal pollution of agricultural soils and sediments in Liaoning Province,China

Heavy metal pollution of soils and sediments in Liaoning Province, Northeast China, was investigated. Fifty seven samples of agricultural soils and 8 samples of sediments were collected in 1996 from paddy or upland fields and irrigation channels, respectively, in Shenyang, Fushun, Liaoyang, Anshan, and Tieling regions, and concentrations of total and 0.1 mol L^-1 HCI-extractable Cd, Cu, Pb, and Zn were analyzed using ICP spectrometry. Seventeen samples of unpolished rice were also collected from selected paddy fields and total concentrations of the four elements were determined.–

Both paddy and upland soils were polluted with Cd: average total concentration was 0.70, 0.57, and 0.53 mg kg^-1 in the western and southern parts of Shenyang, and Anshan, respectively, and significantly higher than the background level of 0.32 mg kg^-1. Cd concentrations of four samples exceeded even 1 mg kg^-1, which corresponds to the critical level of Cd contamination in China. About 65% of the total Cd was extracted with 0.1 mol L^-1 HCI, suggesting that Cd was relatively mobile compared with other metals. The level of Cd pollution was, however, lower than that previously reported and serious polIution was not observed for Cu, Pb, and Zn. Accordingly, Cd concentration in upland rice was within the range of the unpolluted level in this study. Nevertheless, Cd concentration in a sediment of irrigation channels in the western part of Shenyang exceeded 16 mg kg^-1, indicating the possibility of further contamination of agricultural soils. In conclusion, soils and sediments were still polluted with Cd in the southern part of Shenyang, Anshan, and especially in the western part of Shenyang, and further countermeasures are urgently required to ensure safe food production in these regions.     

中国太原市农业土壤的重金属污染状况

To evaluate the current state of the environmental quality of agricultural soils in Taiyuan City, a hotspot for China’s industrial development, the concentrations of 8 heavy metals in soils were investigated by means of extensive sampling in farmlands, forestlands, and grasslands in the city. Statistical analyses and spatial distribution maps were used to identify the most significant heavy metal pollutants. The mean concentrations of As, Cd, Cu, Hg, Pb, Zn, Ni, and Cr were slightly higher than their background values in Taiyuan’s topsoil, but were lower than the maximum permissible concentrations in the Chinese Environmental Quality Standard for agricultural soils. Farmland soils in Taiyuan had the highest average Cd, Cu, Hg, Pb, Zn, and Cr concentrations, but the As and Ni concentrations did not differ significantly among the farmland, forestland, and grasslands. Soil contamination by Cd, Cu, Hg, Pb, Zn, and Cr was mainly derived from farming practices, especially the use of sewage water for irrigation. In contrast, As and Ni might derive mainly from the soil parent material. The identification of heavy metal sources in agricultural soils may provide a basis for taking appropriate action to protect soil quality.     

肥料重金属含量状况及施肥对土壤和作物重金属富集的影响

本文对肥料中重金属的含量状况以及施肥对土壤和农作物重金属累积影响的研究进展进行了系统分析和总结。过磷酸钙中锌（Zn）、 铜（Cu）、 镉（Cd）、 铅（Pb）含量高于氮肥、 钾肥和三元复合肥,有机-无机复混肥料中的Pb含量高于其他化肥。有机肥如畜禽粪便、 污泥及其堆肥中的重金属含量高于化肥,猪粪中的Cu、 Zn、 砷（As）、 Cd含量明显高于其他有机废弃物,鸡粪中铬（Cr）含量高;污泥和垃圾堆肥中Pb或汞（Hg）含量高。商品有机肥Zn、 Pb和镍（Ni）含量高于堆肥,Hg含量高于畜禽粪便。多数研究表明,氮磷钾配施与不施肥相比土壤Cd和Pb含量增加,施用有机肥比不施肥提高土壤Cu、 Zn、 Pb、 Cd含量。施用化肥对农作物重金属富集的影响不明确,而施用有机肥可提高作物可食部位Cu、 Zn、 Cd、 Pb 的含量,影响大小与有机肥种类、 用量、 土壤类型和pH以及作物种类等有很大关系。在今后的研究中应着重以下几个方面, 1）典型种植体系下土壤重金属的投入/产出平衡; 2）不同种植体系下长期不同施肥措施对土壤重金属含量、 有效性影响的动态趋势; 3）典型种植体系和施肥措施下土壤对重金属的最高承载年限; 4）现有施肥措施下肥料中重金属的最高限量标准。     

Survey on the metal contamination of agricultural soils in Georgia

There is only sparse information on the metal contamination of agricultural soils in the former Soviet Union and the development of impacts during the process of transformation to a private structure of production. In this study a first overview on the metal load (Pb, Zn, Cu, Cr, Mn) of agricultural soils in central and eastern regions of Georgia is given using 251 subsamples from 106 profiles on 37 plots. While the data sets for lead (Pb) and chromium (Cr) are rather homogeneous and range only within narrow limits, the contents of zinc (Zn) and copper (Cu) vary much more. Additionally, manganese (Mn) was tested. Here the data vary largely, which is probably due to the natural soil loads. Very low loads for all investigated metals are typical for communally used pastures (Allmende) and especially for a biologically managed farm. On the contrary, Cu loads frequently exceed the median by more than five to ten times (the maximum value is 1023 mg kg⁻¹) in vineyards. The comparison of complete soil profiles proves that this is due to the application of copper sulphate for pest control. In the Bolnisi region south of Tbilisi extremely high loads in the upper soil horizons are found not only for Cu, but for Zn as well, ranging up to 794 mg kg⁻¹. Compared to all other data, the loads for Pb and Cr are also high in several samples. Cu, Zn and Pb are significantly correlated to one another in the Bolnisi region. This striking situation most probably results from the frequent irrigation of the plots by industrially contaminated water from the Mashawera River. Due to economic deficiencies the application of chemicals in Georgian agriculture has dropped heavily since 1990. Consequently, the metal contamination of agricultural soils in general is rather low, being far below western European tolerance limits. Intensive pasturing might even cause values close to the natural loads due to erosion and/or the export by the way of plants and livestock. On the other hand, some specific types of land use cause serious environmental problems. This is especially true for vineyards and plots that are irrigated with contaminated water. Overgrazed plots tend to soil erosion. Copyright © 1999 John Wiley & Sons, Ltd.     

重金属污染对水稻田土壤硫酸盐还原菌种群数量及其活性的影响

在实验室条件下,采用重金属Cd2+、As5+、Cu2+、Pb2+和Cr3+处理黄松稻田土壤、紫色稻田土壤和红壤稻田土,28d后分析重金属污染对水稻田土壤的硫酸盐还原菌(SRB)种群数量和硫酸盐还原活性(SRA)的影响。结果表明,在每千克干土中加入200mgPb2+时,对稻田土壤的SRB种群数量和SRA有促进作用;当加入的Cd2+、As5+、Cu2+、Pb2+和Cr3+每千克干土分别超过1.0、30、500、400和200mg时,对稻田土壤SRB种群数量和SRA有明显抑制作用。随着加入量的增加,重金属对水稻田土壤的SRB种群数量和SRA的抑制作用越来越强,水稻田土壤通过自身来恢复SRB种群数量和SRA所需的时间也越长。同一种重金属元素对不同土壤的SRB种群数量和SRA抑制的污染临界值也有差异。     

Heavy metal contamination of soils in a mining area in South Africa and its impact on some biotic systems

In soils, animals and plants from selected sites in the Rustenburg mining area, a part of the South African ore belt, the heavy metal burden was examined. These sites belong to different soil types and are characterized by different land-use (agriculture, grassland). The heavy metal contamination of the soil samples is relatively high and is dominated by chromium and nickel, metals, which are extracted in the mine near the sampling sites. These high heavy metal concentrations had no clear inhibitory influence on micro-organisms or the enzyme activity of soils. It appears that the high clay content of the soils may counteract the influence of heavy metals. On the other hand, tolerant microbial populations may have been established. In addition, the investigated culture plants there was no correlation between the heavy metal content of the soils and the concentrations in roots and shoots. The dangerous, potential contamination of organs in humans seems to be modest, with the exception of tobacco leaves. The heavy metal content of tissues in the examined animals reflect the environmental habitat in situ with no obvious influence on the health of the animals.     

重金属迁移与土壤性质的关系

Cu, Zn, Pb and Hg runoff from yellow limestone soil and purple soils and the relationships between the mobility of the heavy metals and the soil characteristics were studied in laboratory using a rainfall simulator. The results showed that the concentrations of soluble Zn in surface runoff were significantly negatively correlated with the contents of < 0.002 mm particles and CEC of the soils, indicating that Zn was mostly adsorbed by clays in the soils. The contents of Cu and Hg in surface runoff were positively related to their contents in the soils. The amounts of Cu, Zn, Pb and Hg removed by surface runoff were influenced by the amounts of soil and water losses and their contents in the soils, and were closely related to the contents of soil particles 1~0.02 mm in size.     

基于局部离群指数的土壤重金属污染评价方法

为评价土壤重金属污染,该文提出了一种局部离群指数方法。局部离群指数方法计算监测样点的局部离群指数,监测样点的局部离群指数越大,则该样点是污染样点的趋势越大。为确保算法的准确性,定义了深度离群点以及广度离群点;为减少算法处理海量数据的计算复杂性,开发了基于密度取样的数据过滤方法,以过滤数据分布致密的数据点而保留稀疏区域的数据点。以京郊农田重金属监测数据为实例,比较局部离群指数方法与内梅罗污染指数方法的评价结果的准确性,结果显示局部离群指数方法的评价结果与内梅罗污染指数方法的结果吻合,表明局部离群指数方法可作为一种有效的重金属污染评价方法。     

黄骅市土壤重金属空间变异特征及污染评价

为研究工业和经济高速发展对环渤海滨海生态脆弱区土壤质量的影响,以黄骅市为研究区,利用地统计学方法对黄骅市表层土壤中的Pb,Hg,Cd,Cr,As,Cu,Zn,Ni共8种重金属空间分布特点和污染状况进行了分析。结果表明:（1）Pb,Cd,Cu元素样点平均含量超过河北省土壤背景值,其他元素含量平均值均未超过,所有元素含量平均值都在国家土壤质量二级标准的范围内。（2）根据变异函数拟合发现,Pb,Hg,Cd,Cr,As,Cu共6种元素拟合于指数模型,Zn,Ni两种元素拟合于球状模型;Pb,Cd,Zn基底效应值为25%～75%,空间自相关程度一般,其空间分布格局受到一定外界干扰。其他元素基底效应值均在25%以下,空间自相关性比较强,空间分布格局受外部影响相对较小。（3）根据克里格内插预测发现,Pb,Cd,Cu整体含量高,区域离散分布;Cr,Zn,Ni整体含量低,连续集中分布;As元素成岛状分布,分布集中于几个区域;Hg成散点状分布于黄骅全县。（4）通过计算内梅罗污染指数可知,黄骅市土壤内梅罗污染指数大部分处于1.0～2.0,属于轻度污染状态;吕桥镇中部和齐家务乡西部污染指数最高,属于污染最严重的地区。工业生产和地质环境是影响土壤重金属元素空间分布的主要原因。     

区域尺度的城市灰尘重金属分布

根据47个城市的灰尘重金属Cd,Cr,Cu,Hg,Pb,Zn,Ni的监测资料,分析了重金属在区域尺度的分布规律。结果表明,灰尘重金属浓度分为5个等级,并在1～4倍的标准差内变化,在空间上呈西高东低,南高北低,自西南向东北减少的特征。各地区灰尘重金属含量依次呈：西南〉西北〉华南〉华东〉华北〉华中〉东北,且某些元素的空间分布还与我国阶梯地势相吻合。自然背景和人类活动都是重要的影响因素,前者对华北、华中和东北地区影响较大,后者对西北、西南和华南地区作用程度较高。另外,各重金属元素受人类活动的作用强度也不同,受影响强度依次呈：Cd〉Hg〉Zn〉Pb〉Cu〉Ni〉Cr。     

用模糊综合评判法评价土壤重金属污染程度

通过对南宁市郊 1 2个主要菜区土壤中重金属 ( Cu、Zn、Cd、Pb)含量的调查和分析测定 ,采用模糊综合评判方法对土壤重金属污染状况进行评价。结果表明 :南宁市郊部分蔬菜区土壤不同程度地受到Cu、 Zn、 Pb、 Cd的污染 ,污染程度依次是 :Cd>Pb>Zn>Cu。 1 2个样点污染程度依次为 n2 =n6 =n1 1 >n7=n8=n9>n1 =n4 >n5>n1 2 >n3=n1 0     

污泥和水溶性重金属盐的植物有效性比较研究

采用盆栽方法研究了污泥中重金属的植物有效性,并与等量重金属盐进行了比较。结果表明,施用污泥50 g/kg土和100 g/kg土能明显增加番茄和玉米苗期地上部Zn、Cu、As的含量,对Cr、Ni、Pb含量影响不大。施用污泥可以降低玉米苗期地上部Cd的含量。施用污泥与施用等量水溶性重金属盐比较,污泥重金属有效性低于水溶性重金属盐的有效性。在土壤污泥施用量为50 g/kg时,污泥重金属在番茄苗期的Zn、Cu有效系数分别为80.9%和54.8%;玉米苗期Zn、Cu的有效系数分别为53.4%和70.3%;污泥用量为100 g/kg土时,污泥重金属在玉米苗期的Zn、As有效系数分别为74.5%和64.4%。     

A novel automated method for the adjustment of ionic metal concentrations in soil extracts

A novel method is proposed for correcting metal fraction concentrations remaining within the sediment containing the solid residue of the sequentially extracted fraction. An easy‐to‐use Excel spreadsheet was prepared to assist adjustment of concentration in each fraction and demonstrate the difference between adjusted and non‐adjusted metal concentration of the fraction. The demonstration of a calculation of the modified BCR protocol data showed that this difference may reach 10–15% of the result value. The spreadsheet is available to download at: http://departments.agri.huji.ac.il/zabam/Rosen_Chen_Fraction_Adjustment_Formulae.xls     

Heavy metal concentrations and correlations in rain‐fed farm soils of Sifangwu village,central Gansu Province,China

Concentrations of copper (Cu), lead (Pb), cadmium (Cd), chromium (Cr), mercury (Hg), arsenic (As), organic carbon (abbreviated to OC) content and pH were measured in rain‐fed farm soils collected in Sifangwu Village which is located central Gansu Province, Northwest China. Concentrations of Cu, Pb, Cd, Hg and As are higher than the background values in grey calcareous soil. Cd concentration exceeds the Threshold of Secondary Environmental Quality Standard for Soil in China by 261 per cent. By bivariate analysis, it was found that OC does not correlate with heavy metal in the village. This is due to the semiarid conditions and agricultural activities. Principal component analysis (PCA) was used to assess the soil data, applying varimax rotation with Kaiser Normalization. The result shows that the data set is defined for three latent components. 1) PC1, which consists of Cu and Cr, and what is characterized as a component subject to strong lithological influence. 2) PC2, dominantly loaded by OC, Pb and Cd, is linked to agricultural influence, i.e. fertilization and cultivation. 3) PC3, the heavy metals Hg and As, in this component are from aerial deposition, thus this PC is named the atmospheric factor. Because PC1 explains 45·026 per cent of total variance, the source of the heavy metal in topsoil in the study area is assumed to be mainly derived from the lithology. Copyright © 2006 John Wiley & Sons, Ltd.     

苏南地区土壤重金属向蔬菜的迁移研究

Vegetable fields in peri-urban areas receive large amounts of extraneous heavy metals because of rapid urbanization and industrialization in China. The concentrations of Cu, Zn, and Pb in 30 soil samples and 32 vegetable samples, collected from 30 different sites in southern Jiangsu Province of China, were measured and their transfer from soil to vegetable was determined. The results showed that the soil samples had wide ranges of pH (4.25-7.85) and electrical conductivity (EC) (0.24-3.42 dS m^-1). Among the soil samples, there were four soil samples containing higher Cu and two soil samples containing higher Zn concentrations than those specified in the Chinese Soil Environmental Quality Standard II. However, no vegetable sample was found to contain a high level of Cu or Zn. In contrast, one vegetable sample contained 0.243 mg Pb kg^-1 FW, which was above the Chinese Food Hygiene Standard, whereas the corresponding soil Pb concentration was lower than the Chinese Soil Environmental Quality Standard II. The transfer coefficients of Cu of all vegetable samples exceeded the suggested coefficient range, implying that extraneous Cu had high mobility and bioavailability to vegetables. There was no significant correlation between extractable soil heavy metal concentrations with four kinds of extractants and soil pH, EC, heavy metal concentrations in vegetables and soils, except that soil pH correlated well with the extractable soil Cu, Zn, and Pb concentrations with 1.0 mol L^-1 NH₄NO₃. Moreover, diethylenetriamine pentaacetic acid (DTPA) extraction method was a more effcient method of extracting heavy metals from the soils independent of soil pH and EC than other three methods used.     

Heavy Metal Concentrations,Partitioning, and Storage in Slovak Forest and Arable Soils Along a Deposition Gradient

Along a heavy metal deposition gradient, caused by a Cu smelter, heavy metal concentrations, partitioning, and storage in forest and arable soils were examined. We sampled organic and mineral soil horizons (0—50 cm) at ten pairs of forest and arable sites derived from the same parent material. A-horizons were extracted with a seven-step sequence; O- and subsoil horizons were digested with strong acids (HNO₃/HClO₄). We found high concentrations of Cd (up to 17.38 mg kg^—1 in the O horizons/up to 2.44 mg kg^—1 in the A horizons), Cu (8437/415), Pb (3343/126), and Zn (1482/637) which decreased exponentially with distance from the smelter and with soil depth. The metal concentrations in the organic layers indicate that the average transport distance decreases in the order Cd > Zn > Pb > Cu. With regard to metal partitioning, NH₄NO₃- + NH₄OAc-extractable forms in the A horizons were most affected by the deposition being more pronounced under forest. In the uppermost 50 cm of the four soils nearest to the smelter two to four times higher Cd, Cu, Pb, and Zn storages were found in forest than in arable soils. At greater distance, the higher deposition onto forest soils due to the scavenging effect of the canopy obviously was compensated by stronger leaching.     

高效栽培雷竹林土壤重金属含量的分析研究

雷竹(Phyllostachyspraecox)是最近十几年发展起来的优良笋用竹种,近年来以重施肥和冬季地表覆盖增温为核心的高效栽培技术在生产上得到了大面积推广。为了解高效栽培雷竹林土壤重金属含量现状,采集了浙江省雷竹主产区40个样点土壤样品,利用ICP法分析了土壤重金属含量。结果表明,雷竹林土壤重金属镉(Cd)、铬(Cr)、铜(Cu)、铅(Pb)和锌(Zn)全量含量分别为0.23±0.11,68.23±25.61,23.26±6.61,12.47±2.86,108.50±54.92mg/kg,所有样点5种重金属全量均未出现超标现象。Cd、Cr、Cu、Pb和Zn有效态含量分别为0.028±0.025,0.150±0.102,3.482±1.304,1.636±1.022,10.814±9.767mg/kg,5种重金属有效态含量变异均明显大于全量。重金属Cd、Cu、Pb和Zn有效态含量占全量百分比较高。从不同栽培历史雷竹土壤重金属含量变化来看,Cu、Pb、Zn3种元素随着栽培历史延长,土壤中全量含量显著上升,其中Cu上升量最大,栽培历史从2～3年延长到8～10年,Cu含量增加了1.39倍。重金属Cd、Cu、Zn全量与有效态含量间具有显著或极显著相关性。     

Heavy metal contamination and risk assessment of human exposure near an e-waste processing site

Environmental pollution due to uncontrolled e-waste recycling activities has been reported in a number of locations in China. In this study, heavy metal pollution from primitive e-waste processing facilities was investigated. The pollution is due to high concentrations of metals present in the surrounding soils and vegetables. The highest enrichment factor values due to e-waste wastewater and waste discharges were found at Anqiaotou Village and Beian Village. Vegetables from the vicinity of the e-waste processing sites were found to have higher heavy metal pollution index values in comparison with those from the background site. The bioaccessibilities of heavy metals were decreased in the order of Cd?>?Pb?>?Sn?>?Zn?>?Ni?>?Cr. The e-waste processing site was badly polluted by Cd, Pb, Zn, Ni and Cr, with its pollution level decreased in the following order: Cd?>?Pb?>?Cr?>?Ni?>?Zn?>?Sn. Additionally, the greatest risk among six metals in the e-waste processing areas is caused by Cd and Pb. The risks associated with the consumption of contaminated vegetables grown in e-waste processing regions may be a potential health concern.