云南蛇纹岩发育土壤与植被中重金属含量的分析

对云南蛇纹岩发育土壤进行了植物和土壤的重金属含量调查和分析.结果表明,Ni、Co为土壤中的主要污染金属,在土壤中的含量范围分别为565~4844mg/kg和69~481mg/kg,Cu、Zn含量则在正常范围内;土壤中Ni、Co生物可利用态的含量均较低.统计分析显示,土壤中Ni、Co含量之间存在显著正相关(R=0.794,P<0.01).调查蛇纹岩发育土壤上隶属21科的42种高等植物,并分析其重金属含量,发现植物体内Ni、Co含量也存在显著相关,可能受到土壤因素的影响所致.调查并未发现Ni、Co的超累积植物,但发现此区域存在较多的Ni、Co耐性植物,对Ni矿废弃地的植被重建有一定的研究意义.图1表6参8     

南京城市土壤中重金属的化学形态分布

采取Tessier连续提取法，研究了南京市不同城区表层土壤中Fe,Mn,Cr,Ni,Co,V,Cu,Zn,Pb的化学形态分布。结果表明，南京城市土壤中Fe,Mn,Cr,Ni,Co,V,Zn,Pb以残渣晶格态为主，可交换态比例极低；Cu在城市道路旁的土壤中有机物结合态所占的比例最高，其他区域残渣晶格态所占的比例最高，与非城区自然土壤相比，主要来源于人为输入的Mn,Cu,Zn,Pb残渣晶格态所占的比例低，活性态比例大；Cr和主要来源于原土壤物质的Fe,Ni,Co,V在城市土壤与非城区自然土壤中各形态所占的比例相似，残渣晶格态比例大，活性态比例极低。     

东莞市不同区域菜地土壤重金属污染状况研究

对东莞市及其不同区域菜地土壤重金属污染情况进行了调查和分析，参照国家土壤环境质量标准，运用单因子污染指数法和综合污染指数法对上述土壤质量进行了评价。结果表明，全市和各区土壤受到了不同程度的重金属污染，具体表现为：全市土壤Cd、Cu、Ni和Pb的超标率分别为4．9％，6．6％，3．3％和95．1％，均处于轻污染状态，以Pb污染最严重；土壤Cr未有超标，仅西北区域达到了警戒级水平。全市土壤重金属含量各样点间变异较大(Zn、Cr、Pb、Cd、Cu、Ni和有效Cu、Zn的变异系数分别为51．5％，54．1％，37．5％，48．8％，60．2％，57．3％和85．3％，64．7％)，但对各重金属元素而言却存在着不同程度的区域差异。     

上海化学工业区土壤重金属元素形态分析

选取上海化学工业区土壤背景值样品，采用Tessier A连续提取法研究土壤中6种重金属元素的形态分布。研究结果表明，在该化工区土壤中，Cd主要以可交换态和铁锰氧化物结合态为主，分别占总量的41．5％和36．7％，说明元素Cd较活泼，具有潜在的环境影响能力，应该给予更多的关注；Cr、Cu、Ni和Zn等4种元素主要以有机结合态和残余态为主，两者分别占总量的41．4％、58．9％、31．4、32．5％和45．9％、31．5％、57．4％、52．3％；而Pb则主要以有机结合态形式存在，其占总量的87．8％；元素形态分析表明Cr、Cu、Ni、Zn和Pb这5种元素相对比较稳定。     

EDTA和柠檬酸对污染土壤中Cd、Ni活化的影响

以新乡市蓄电池厂周围的Cd、Ni污染土壤为研究对象,研究了不同浓度的EDTA、柠檬酸对Cd、Ni活化的影响。结果表明:在供试污染土壤中,Cd、Ni的活化量随着EDTA、柠檬酸浓度的增大而增大,EDTA对Cd、Ni的活化效果大于柠檬酸。在浓度为10.0mmol/L时,EDTA和柠檬酸对Cd、Ni的活化量都达到最大。EDTA和柠檬酸对Cd、Ni活化速度特性不同,EDTA对土壤Cd的活化速率大于柠檬酸,EDTA对土壤Ni的活化速率略大于柠檬酸。供试污染土壤中Ni不易被活化。     

不同使用年限蔬菜大棚土壤重金属含量变化

调查了1、5．8、11a棚龄蔬菜大棚土壤中重金属元素As、Cd、Co．Cr、Cu、Hg、Fe、Mn、Mo、Ni、Pb和Zn的含量。结果表明：同一使用年限的蔬菜大棚0-40cm土层内重金属元素含量差异很小；与棚外土壤相比，除la棚龄的土壤外，多数土壤重金属含量随大棚使用年限的延长而有所增加；研究地区的蔬菜大棚土壤尚未发生重金属污染超标现象；大量施肥(复合肥)可能是导致蔬菜大棚土壤中重金属含量升高的主要原因。     

有机酸对根际土壤中铅形态及其生物毒性的影响

采用根袋盆栽试验和连续浸提方法研究外源柠檬酸、EDTA对根际土壤中Pb形态转化及其生物毒性的影响。结果表明，有机酸能明显活化根际土壤中的Pb，高浓度(3mmol／L)比低浓度(0．5mmol／L)的柠檬酸对Pb的活化能力强；EDTA在低浓度(0．5mmol／L)时对Pb的活化能力就很强。柠檬酸、EDTA能增强土壤Pb的毒性，提高小麦根部对Pb的吸收，并促进Pb由根部向地上部转移。     

PM_(10)中重金属的提取方法及生物可利用性研究

分别运用模拟生物提取法与化学连续提取法对PM10标准参考样品城市源(NIST-1648A)和工业源(BCR-038)中6种重金属(Cd、Co、Cu、Mn、Ni、Pb)质量分数及赋存形态进行分析。其目标是验证2种提取大气固体颗粒物中重金属方法的有效性,并比较2种方法的优缺点,为将来提取PM10中重金属的方法选取提供依据。模拟生物提取法中,使用Gamble溶液模拟人体肺液对PM10样品进行溶解,实验方法操作较为简单快捷;化学连续提取法中,不同溶解步骤则可确定重金属的不同赋存形态。在需要快速确定PM10中某种重金属总量时,应优先使用模拟生物提取法。化学连续提取结果表明,城市源PM10中重金属赋存形态分布没有统一规律,工业源PM10中重金属多以残渣态存在。通过对2种来源的PM10样品中重金属生物可利用性分析,城市源的大气颗粒物对人体的毒性更大,其中标准参考样品城市源PM10中生物可利用性较高的是重金属Cd(BIBio为61.65%±3.45%;BISE为69.02%±3.82%)和Cu,最低的是重金属Co和Pb;标准参考样品工业源PM10中重金属的生物可利用性最高的是Cd(BIBio为27.66%±1.52%;BISE为15.05%±2.13%),而Ni、Co和Pb的生物可利用性较低。     

内蒙古中东部大针茅群落土壤线虫多样性研究

2003年在内蒙古西乌旗大针茅草原，根据土壤深度0～10cm、1020cm、20～30cm分层采样，定量分析土壤线虫群落的多度，并对土壤线虫群落多样性和群落内线虫营养类型进一步分析．结果表明，该群落中土壤线虫包括50属和24科，其中矮化属、拟盘旋属、丽突属为优势属，特别是矮化属线虫数量异常高．土壤线虫群落的垂直分布呈现表聚型．就功能类群而言，植食性线虫在各层中的比例最高，为69．4％～81．3％，食真菌类线虫的比例最低，为0．9％～2．4％，而食细菌类线虫比例为13．9％-20．9％，食真菌类线虫和食细菌类线虫的比值为0．067～0．133．表6参29     

禹州市煤矿区周边土壤和农作物重金属污染状况及健康风险评价

为全面了解河南省禹州市煤矿周边土壤和农作物中的重金属污染现状.对禹州市的某3个典型矿区(下文称为A、B和C矿区)周围土壤和主要谷类农作物(玉米和小麦)进行了调研和采样分析,并采用电感耦合等离子体质谱仪(ICP-MS)测定其重金属含量,同时通过单因子指数法和内梅罗综合指数法评价了煤矿周围土壤的污染状况,并利用MMSOILS风险评价模型评价了食用当地谷类农作物对成人和儿童造成的重金属健康风险.结果表明:研究区土壤受到了重金属不同程度的污染,污染程度排序:小麦地玉米地,且就单个重金属污染程度来说, Cd Cu Co Ni Zn Cr;内梅罗综合污染指数分析结果表明,玉米地的污染程度为安全,小麦地的污染程度为重污染,均以Cd对污染指数P_(综合)值的贡献最大;研究区农作物玉米籽粒中Cr、Co、Ni、Cu、Zn和Cd的平均含量分别为25.03、0.54、2.87、21.52、118.68、1.97 mg·kg~(-1);小麦籽粒中Cr、Co、Ni、Cu、Zn和Cd的平均含量分别为1.04、0.11、1.17、9.55、61.51、0.06 mg·kg~(-1).Cr、Co、Ni、Cu、Zn和Cd富集系数大小的顺序均为玉米小麦;健康风险评价表明,研究区农作物籽粒中存在高重金属污染风险,尤其以Cd最为明显,食用当地谷类农作物对人体造成健康风险的顺序依次为Co Cd Cu Zn Ni Cr,其中Co、Cd对成人风险较高,Co、Cu、Zn、Cd对儿童风险较高,对儿童造成的健康风险要明显高于成人;土壤重金属含量与谷类农作物可食部分重金属含量间无明显相关性.     

Heavy metals in soils and crops in Southeast Asia

In a reconnaisance soil geochemical and plant survey undertaken to study the heavy metal uptake by major food crops in Malaysia, 241 soils were analysed for cation exchange capacity (CEC), organic carbon (C), pH, electrical conductivity (EC) and available phosphorus (P) using appropriate procedures. These soils were also analysed for arsenic (As), cadmium (Cd), cobalt (Co), chromium (Cr), copper (Cu), mercury (Hg), nickel (Ni), lead (Pb) and zinc (Zn) using aqua regia digestion, together with 180 plant samples using nitric acid digestion. Regression analysis between the edible plant part and aqua regia soluble soil As, Cd, Cr, Cu, Hg, Ni, Pb and Zn concentrations sampled throughout Peninsular Malaysia, indicated a positive relationship for Pb in all the plants sampled in the survey (R2 = 0.195, p < 0.001), for Ni in corn (R2 = 0.649, p < 0.005), for Cu in chili (R2 = 0.344, p < 0.010) and for Zn in chili (R2 = 0.501, p < 0.001). Principal component analysis of the soil data suggested that concentrations of Co, Ni, Pb and Zn were strongly correlated with concentrations of Al and Fe, which is suggestive of evidence of background variations due to changes in soil mineralogy. Thus the evidence for widespread contamination of soils by these elements through agricultural activities is not strong. Chromium was correlated with soil pH and EC, Na, S, and Ca while Hg was not correlated with any of these components, suggesting diffuse pollution by aerial deposition. However As, Cd, Cu were strongly associated with organic matter and available and aqua regia soluble soil P, which we attribute to inputs in agricultural fertilisers and soil organic amendments (e.g. manures, composts).     

Compost and sulfur affect the mobilization and phyto-availability of Cd and Ni to sorghum and barnyard grass in a spiked fluvial soil

Soil reclamation via additives can cause contradictory effects on the mobilization of toxic elements in soils under dry and wet conditions. Therefore, our aim was to investigate the impact of compost and sulfur in two rates (1.25 and 2.5%) on fractionation, mobilization, and phyto-availability of cadmium (Cd) and nickel (Ni) to sorghum (dry soil) and barnyard grass (wet soil) in a fluvial soil spiked with 25 mg Cd or 200 mg Ni/kg soil. Compost decreased the solubility and mobilization of Cd (especially in dry soil) and Ni (in both soils). Sulfur increased the solubility of Cd (31% in dry soil—49% in wet soil) and Ni (4.6% in wet soil—8.7% in dry soil). Sulfur altered the carbonate fraction of Cd to the soluble fraction and the residual fraction of Cd and Ni to the non-residual fraction. Compost decreased Cd and increased Ni in sorghum, but enhanced Cd and degraded Ni in grass. Sulfur increased Cd and Ni in both plants, and the increasing rate of Cd was higher in grass than in sorghum, while Ni was higher in sorghum than in grass. These results suggest that compost can be used as an immobilizing agent for Cd in the dry soil and Ni in the wet soil; however, it might be used as mobilizing agent for Cd in the wet soil and Ni in the dry soil. Sulfur (with rate 2.5%) can be used for enhancing the phyto-extraction of Cd and Ni (especially Cd) from contaminated alkaline soils.     

Cytogenetic and epigenetic alterations by cobalt and nickel on Zea mays L

Changes in DNA methylation in Zea mays plantlets in response to cobalt and nickel (5, 10, 20, and 40 mmol L^?1) evaluated by the coupled restriction enzyme digestion-random amplification technique revealed dose-related increases in hypermethylation. The effects on mitotic index and phytohormone levels were also determined. Co and Ni caused a decrease in mitotic index and an attenuation in the growth-promoting hormones gibberellic acid, zeatin, and indole acetic acid, while abscisic acid levels rose. These findings have shown that the increase in abscisic acid levels and DNA methylation depend on the concentrations of Co and Ni.     

PM10中重金属的提取方法及生物可利用性研究

分别运用模拟生物提取法与化学连续提取法对PM10标准参考样品城市源（NIST-1648A）和工业源（BCR-038）中6种重金属（Cd、Co、Cu、Mn、Ni、Pb）质量分数及赋存形态进行分析。其目标是验证2种提取大气固体颗粒物中重金属方法的有效性,并比较2种方法的优缺点,为将来提取PM10中重金属的方法选取提供依据。模拟生物提取法中,使用Gamble溶液模拟人体肺液对 PM10样品进行溶解,实验方法操作较为简单快捷;化学连续提取法中,不同溶解步骤则可确定重金属的不同赋存形态。在需要快速确定 PM10中某种重金属总量时,应优先使用模拟生物提取法。化学连续提取结果表明,城市源PM10中重金属赋存形态分布没有统一规律,工业源PM10中重金属多以残渣态存在。通过对2种来源的PM10样品中重金属生物可利用性分析,城市源的大气颗粒物对人体的毒性更大,其中标准参考样品城市源 PM10中生物可利用性较高的是重金属Cd（BIBio为61.65%±3.45%;BISE为69.02%±3.82%）和Cu,最低的是重金属Co和Pb;标准参考样品工业源PM10中重金属的生物可利用性最高的是Cd（BIBio为27.66%±1.52%;BISE为15.05%±2.13%）,而Ni、Co和Pb的生物可利用性较低。     

Determination trace amounts of copper, nickel, cobalt and manganese ions in water samples after simultaneous separation and preconcentration

In the present article, a simple, rapid, sensitive and economical method has been developed for the simultaneous separation and preconcentration of the trace amounts of copper, nickel, cobalt and manganese in water samples by using modified XAD-4 resins. The sorption was quantitative in the pH range 6.0–9.0, whereas quantitative desorption occurred instantaneously with 5.0 mL of 2 M HNO₃, and selected elements have been determined by using flame atomic absorption spectrometry. Dynamic ranges were 0.04–3.5, 0.1–6.0, 0.04–4.5 and 0.04–4.0 μg/mL for copper, nickel, cobalt and manganese, respectively. The detection limits were 9.2, 28.6, 12.3 and 5.7 ng/mL for Cu(II), Ni(II), Co(II) and Mn(II), respectively. The effects of the experimental parameters, including the sample pH, eluent type, interference ions and breakthrough volume, were studied for separation and preconcentration of Cu(II), Ni(II), Co(II) and Mn(II) ions. Determination of these ions in standard samples confirmed that the proposed method has good accuracy. The proposed method was used for the determination of these ions in water samples.     

Heavy metals in soils and crops in Southeast Asia 2. Thailand

A reconnaissance soil geochemical and concomitant plant survey based on 318 soil (0-15 cm) and 122 plant samples was used for the assessment of heavy metal pollution of agricultural soils and crops of Thailand. Arsenic (As), cadmium (Cd), cobalt (Co), chromium (Cr), copper (Cu), mercury (Hg), nickel (Ni), lead (Pb) and zinc (Zn) were determined in soils using aqua regia digestion, and in plants using nitric acid digestion. Organic carbon (C), pH, electrical conductivity (EC) and available phosphorus (P) were determined on the soil samples using appropriate procedures. Results indicated that concentrations of heavy metals varied widely among the different regions of Thailand. Regression analysis between the concentrations of metals in soil (aqua regia extractable) and edible plant parts indicated a small but positive relationship for Cd in all the plants sampled in the survey (R2 = 0.081, p < 0.001). There was also a positive relationship between soil and plant Cd concentrations in rice (R2 = 0.242, p < 0.010), and negative relationships for Zn in rice (R2 = 0.385, p < 0.001), and Cu (R2 = 0.355, p < 0.001) and Zn (R2 = 0.122, p < 0.026) in glutinous rice. Principal component analysis of the soil data suggested that concentrations of As, Co, Cr, Cu, Hg, Ni and Pb were strongly correlated with concentrations of Al and Fe, which is suggestive of evidence of background variations due to changes in soil mineralogy. Thus, the evidence for widespread contamination of soils by these elements through agricultural activities is not strong. On the other hand, Cd and Zn were strongly correlated with organic matter and concentrations of available and aqua regia extractable P. This is attributed to input of contaminants in agricultural fertilisers and soil amendments (e.g. manures, composts).     

Quantification of transition metals in biological samples and its possible impact on ferro-alloy workers

Increased risk of ill-health and diseases has been associated with employment in the ferro-alloy factory. Since measurement of transition metals in human blood and hair along with respective exposure rates, provides a means of assessing individual risk, it has been the most important part of the study. In the study majority of the elements in the transition series, such as, vanadium (V), chromium (Cr), iron (Fe), manganese (Mn), cobalt, (Co) nickel (Ni), copper (Cu), zinc (Zn), molybdenum (Mo) and cadmium (Cd) were considered which are randomly emitted from the source, that is, manganese ore (used during ferro-alloy manufacturing process). The commonly available transition, metals, observed in biological samples of ferro-alloy workers, were found to be Fe, Zn, Co, Ni, Cu, Cr, Cd, V Mn and Mo in blood, while in hair, Mn, Fe, Zn, Co, Ni, Cu, Cr, Cd, V and Mo were present in decreasing order Surveillance of bio-concentration of these metals in workers, exposed to close proximity of the coke-ovens and smelting furnaces, revealed that the workers were prone to several physical disorders.     

Heavy metals in soils and crops in Southeast Asia

In a reconnaissance soil geochemical and plant survey undertaken to study the heavy metal uptake by major food crops in Malaysia, 241 soils were analysed for cation exchange capacity (CEC), organic carbon (C), pH, electrical conductivity (EC) and available phosphorus (P) using appropriate procedures. These soils were also analysed for arsenic (As), cadmium (Cd), cobalt (Co), chromium (Cr), copper (Cu), mercury (Hg), nickel (Ni), lead (Pb) and zinc (Zn) using aqua regia digestion, together with 180 plant samples using nitric acid digestion. Regression analysis between the edible plant part and aqua regia soluble soil As, Cd, Cr, Cu, Hg, Ni, Pb and Zn concentrations sampled throughout Peninsular Malaysia, indicated a positive relationship for Pb in all the plants sampled in the survey (R ² = 0.195, p < 0.001), for Ni in corn (R ² = 0.649, p < 0.005), for Cu in chilli (R ² = 0.344, p < 0.010) and for Zn in chilli (R ² = 0.501, p < 0.001). Principal component analysis of the soil data suggested that concentrations of Co, Ni, Pb and Zn were strongly correlated with concentrations of Al and Fe, which is suggestive of evidence of background variations due to changes in soil mineralogy. Thus the evidence for widespread contamination of soils by these elements through agricultural activities is not strong. Chromium was correlated with soil pH and EC, Na, S, and Ca while Hg was not correlated with any of these components, suggesting diffuse pollution by aerial deposition. However As, Cd, Cu were strongly associated with organic matter and available and aqua regia soluble soil P, which we attribute to inputs in agricultural fertilisers and soil organic amendments (e.g. manures, composts).     

Efficient removal of heavy metals from electroplating wastewater using polymer ligands

Poly(hydroxamic acid)-poly(amidoxime) chelating ligands were synthesized from poly(methyl acrylate-co-acrylonitrile) grafted acacia cellulose for removing toxic metal ions from industrial wastewaters. These ligands showed higher adsorption capacity to copper (2.80 mmol?g⁻¹) at pH 6. In addition, sorption capacities to other metal ions such as iron, zinc, chromium, and nickel were also found high at pH 6. The metal ions sorption rate (t_1/2) was very fast. The rate of adsorption of copper, iron, zinc, chromium, nickel, cobalt, cadmium and lead were 4, 5, 7, 5, 5, 8, 9 and 11 min, respectively. Therefore, these ligands have an advantage to the metal ions removal using the column technique. We have successfully investigated the known concentration of metal ions using various parameters, which is essential for designing a fixed bed column with ligands. The wastewater from electroplating plants used in this study, having chromium, zinc, nickel, copper and iron, etc. For chromium wastewater, ICP analysis showed that the Cr removal was 99.8% and other metal ions such as Cu, Ni, Fe, Zn, Cd, Pb, Co and Mn removal were 94.7%, 99.2%, 99.9%, 99.9%, 99.5%, 99.9%, 95.6% and 97.6%, respectively. In case of cyanide wastewater, the metal removal, especially Ni and Zn removal were 96.5 and 95.2% at higher initial concentration. For acid/alkali wastewater, metal ions removing for Cd, Cr and Fe were 99.2%, 99.5% and 99.9%, respectively. Overall, these ligands are useful for metal removal by column method from industrial wastewater especially plating wastewater.     

植物吸收修复对土壤镍及其主要化学性质的影响

采用室内盆栽试验方法,研究了外源镍污染土壤的植物吸收修复对土壤镍形态和土壤主要化学性质的影响。试验用水稻土添加NiSO4·6H2O(100～1600mgkg-1)经过12周的驯化培养后,种植了镍超累积植物Alyssu mmurale,110 d后收获植物并进行了试验土壤镍的形态和主要化学性质的分析,采用再分配系数和结合强度系数对植物修复效果进行了定量分析。结果表明,根区土壤中DTPA提取态镍的数量明显减少,根区土壤DTPA-Ni与非根区土壤DTPA-Ni之比的范围在0.33～0.61之间。每盆植物提取镍量为6.61～31.18mg,植物提取量随着添加镍量增加而增加,地上部分最大镍含量达到12454.1mgkg-1。根区的再分配系数在2.17～4.19之间,而非根区的再分配系数在6.87～15.91之间,再分配系数随着镍添加量的增加而增大;根区的结合强度系数为0.84～0.39,而非根区的则为0.88～0.26,随着土壤中镍添加量的增加,结合强度系数逐渐减小。植物吸收修复后,根区土壤镍的再分配系数降低、结合强度系数增大,表明土壤镍各形态之间的稳定性增加,因此植物修复可以加快外源镍在土壤中的稳定。试验结果也表明,根区土壤中pH随着镍添加量的增加呈下降趋势、但较非根区土壤的高;根区土壤有机碳亦较非根区的高。