5个蓖麻品种对土壤中镉富集的差异

为了评价能源作物蓖麻对污染农田中重金属镉(Cd)的富集修复能力,本研究以5个蓖麻品种为试验材料,通过大田试验对比了不同蓖麻品种在Cd污染农田中的生长情况、对Cd的富集和转运能力以及对Cd污染土壤的修复能力。结果表明,5个蓖麻品种在Cd污染农田中生长良好,其中滇蓖2号的株高、茎粗及单株产量显著高于其他品种,分别为440.78 cm、5.04 cm以及338.85 g。5个蓖麻品种根、茎、叶及果实的Cd含量、Cd积累量和富集系数均存在显著差异,其中经作蓖麻1号根、茎和果实的Cd含量最高,分别为1.40、1.14和0.33 mg·kg^-1。污染修复能力方面,滇蓖2号Cd的积累量达3.38 mg/株,提取率为5.34%,显著高于其他品种。经作蓖麻1号尽管富集能力最强,但由于其生物量最小,其Cd积累量及年提取效率均最低。综上可知,蓖麻对土壤中重金属Cd的富集能力较强,可用于修复云南个旧地区的Cd污染土壤,且种植滇蓖2号可以获得较好的修复效果。本研究结果为云南Cd污染土壤治理提供了理论基础和参考依据。     

蓖麻种子吸水和萌发过程对盐分胁迫条件的响应

为确定盐分对蓖麻的影响,设置0 mM和100 mM 2个盐分浓度NaCl,研究了4个蓖麻品种种子的吸水和萌发特性.在吸水开始的18h内,种子吸水快速增加,18 h后增加缓慢,48 h后在0 mM NaCl水平下种子吸水呈快速增加趋势,而在100 mM NaCl水平下吸水很少.汾蓖10号和淄蓖7号的吸水量和吸水速率显著高于淄蓖5号和淄蓖8号.与0 mM NaCl相比,同一品种在100 mM NaCl下的吸水量和吸水速率明显较低.100mM NaCl处理对种子萌发具有明显的抑制作用,表现为延迟种子萌发,降低发芽率,抑制芽长和芽粗.综合发芽率、芽长和芽粗相对盐害率,淄蓖5号耐盐能力最强,其次是汾蓖10号,淄蓖7号和淄蓖8号耐盐能力相对较差.本试验通过研究不同蓖麻品种的吸水和萌发特性,为采用外源措施提高种子吸水能力,促进种子萌发和出苗奠定基础.     

不同高粱种质对污染土壤中重金属吸收的研究

利用重金属含量较高的污水污染土壤,以未污染土壤作对照,种植8个甜高粱品种、2个饲用高粱品种和1个粒用高粱品种,检测8种重金属在高粱植物体内不同器官的含量,以研究不同高粱种质对重金属的吸收特性。结果表明:甜高粱对汞(Hg)、镉(Cd)、锰(Mn)和锌(Zn)的吸收在两种土壤间差异显著,对钴(Co)、铬(Cr)、铅(Pb)和铜(Cu)的吸收差异不显著。Mn在甜高粱体内含量表现为未污染土壤高于污染土壤;而Zn含量在不同器官之间存在差异,未污染土壤叶中含量远高于穗,穗中含量远高于茎和根。不同重金属在甜高粱体内的储存部位不同,污染土壤上Hg、Cd、Co、Cr和Zn在根中积累量较高,Cu、Mn和Pb在穗中的积累量较高。甜高粱、饲用高粱和粒用高粱对重金属的吸收、运输及储存在品种之间差异较大,同一品种对不同重金属的吸收也存在差异。饲用高粱表现为叶部对Cr和Zn的储存量较高,而粒用高粱‘晋中0823’则显示了茎对多种重金属的储存能力。高粱根对土壤中重金属的富集系数较高,为0.02(Pb)~0.23(Cd),转移系数变幅为0.21(Co)~3.42(Pb)。对同一种重金属的吸收量品种间差异较大,甜高粱‘西蒙’根对Co、Cr、Cu、Mn、Pb和Zn具有高富集系数,粒用高粱‘晋中0823’茎对Hg、Cd、Mn、Pb和Zn富集系数较高。高粱对重金属的吸收能力与转移能力不同步,甜高粱‘绿能1号’具有对多种重金属的高转移能力,粒用高粱‘晋中0823’只对Zn有较高的转移能力。因此本文认为甜高粱对不同重金属的吸收和转移有选择性。对Zn吸收并转移到地上部后,首先储存在叶和穗中,当吸收量足够大时,茎和根也成为储存器官;对Mn的吸收与其他重金属的吸收存在竞争作用,Hg吸收后很少向地上部转移;而对Cu、Mn和Pb吸收后在穗部的储存量较大。饲用高粱与甜高粱相比对重金属的吸收未显示明显的不同,甜高粱‘西蒙’根对多种重金属具有强储存能力,而粒用高粱‘晋中0823’的茎秆显示了比甜高粱更强的储存能力,甜高粱‘绿能1号’对多种重金属的转移能力较强。所以,选择富集和转移能力均强的高粱品种能更有效地吸收土壤中的重金属,达到修复污染土壤的目的。     

土壤pH值与镉含量对水稻产量和不同器官镉累积的影响

为探明水稻产量与镉积累分配对土壤pH值和镉含量的响应,以3个籽粒Cd含量差异明显的晚稻品种(天优华占,TY;星2号,X2;湘晚籼13号,XW)为试验材料,分别于不同pH值稻田研究土壤镉(Cd)含量对水稻产量和不同器官Cd累积的影响,并比较了品种间差异。结果表明,水稻产量因土壤pH值下降而下降,且品种间降幅差异明显,以X2最大(21.72%33.81%),XW最小(3.05%17.71%);添加0.5 mg·kg^-1Cd时水稻减产不显著,但添加1.0 mg·kg^-1Cd时各品种均显著减产,且其降幅与品种和土壤pH值有关,X2和XW在酸化条件下降幅较大,而TY在正常pH条件下降幅较大。植株(整株)Cd含量存在品种间差异,各品种植株Cd含量均随着土壤Cd浓度的提高与土壤pH值的下降而显著提高,且植株Cd含量峰值因土壤酸化而提前。水稻器官间Cd含量依次表现根>茎>穗>叶,各器官Cd含量均随着土壤Cd浓度提高而显著增大,但增大倍数存在器官间差异;品种间器官Cd含量差异明显,营养器官表现为X2>TY>XW,而稻穗表现为TY>X2>XW。水稻各器官及全株Cd累积量均随着土壤Cd浓度提高和土壤pH值降低而显著增大,成熟期累积量表现为茎>穗>根>叶;品种间Cd累积量差异明显,营养器官和整株Cd累积量表现为X2>XW>TY,而穗Cd累积量表现为TY>X2>XW。Cd分配比例一般以茎为最高,叶最低,土壤酸化使茎、叶所占比例增大,根、穗所占比例降低;品种间Cd分配比例存在一定差异,穗Cd所占比例表现为TY>X2>XW。可见,水稻产量与器官间Cd累积分配规律受到土壤Cd含量和pH值的影响显著,同时也具有明显的品种间差异。本研究为不同水稻品种在不同pH值与Cd含量稻田上的应用提供了理论依据。     

不同基因型玉米品种对Pb的富集特征

为了研究不同基因型玉米品种对Pb的富集特征,选用2个Pb低富集玉米品种(曲辰11号、曲辰3号)和2个Pb高富集玉米品种(靖丰8号、旭玉1446),开展Pb胁迫(2 000 mg·kg-1)下的大田试验,研究了玉米植株生物量的变化、各部位Pb含量、Pb总吸收量、富集与转运规律、土壤p H值及有效态Pb含量。结果表明:(1)与对照相比,Pb胁迫导致4个玉米品种根、茎、叶和籽粒生物量不同程度的下降,总生物量下降9.65%~20.46%,但低富集玉米品种生物量的下降程度小于高富集玉米品种;(2)玉米各部位的Pb含量分配规律为根叶茎籽粒,分别为95.39~121.02、25.56~43.21、14.06~25.41、2.52~5.38 mg·kg-1;低富集玉米品种根的Pb含量高于高富集玉米品种,而茎、叶和籽粒的Pb含量低于高富集玉米品种;玉米植株对Pb的总吸收量为4.46~7.94 mg·株-1,低富集玉米品种植株的Pb总吸收量显著低于高富集玉米品种;(3)不同基因型玉米品种对Pb的富集系数和转运系数均小于1,表现为低富集玉米品种低于高富集玉米品种;(4)不同基因型玉米品种土壤p H值为6.60~6.82,且低富集玉米品种显著高于高富集玉米品种,土壤有效态Pb含量范围为969.86~1 116.15 mg·kg-1。     

玉竹对土壤Cd Pb的吸收和耐性研究

以盆栽玉竹为试验材料,分别用不同浓度的Cd、Pb进行处理,研究玉竹的生物量、重金属积累和部分生理指标的变化。结果表明,当土壤Cd浓度≤1mg.kg-1或Pb浓度≤1000mg.kg-1时对玉竹的生长有促进作用,超过这个浓度范围就表现为抑制作用。玉竹叶、茎、根对两种重金属的吸收都呈极显著正相关,且根的吸收能力大于茎和叶,玉竹对Pb有较强的抗性。Cd、Pb处理后,玉竹叶片SOD酶和POD酶活性的增加能在一定程度上减轻重金属胁迫引起的膜脂过氧化伤害,但长时间的Cd胁迫会对植株产生明显的抑制作用。Cd、Pb处理会使玉竹叶片脯氨酸含量在短时间内上升,但是高浓度的重金属处理和长时间的胁迫环境则会导致脯氨酸含量下降。MDA含量均随着Cd、Pb处理浓度的升高而增加,并且时间越长,增加越多。     

硒对烤烟生长、化学指标及矿质营养元素含量的影响

为探讨不同浓度的硒(Se)对植物生长、化学指标及矿质营养元素含量的影响,本研究以云烟87为试验材料,采用盆栽试验方法,研究了不同硒浓度对烤烟生长、化学指标及烤烟根、茎、叶中矿质元素N、P、K、Ca、Mg、Mn、Zn、Cu累积的影响。结果表明,土壤施硒(亚硒酸钠)4.4 mg·kg-1时,烟叶中烟碱、蛋白和还原糖等含量处于最适范围,根、茎、叶中矿质元素N、P、K、Ca、Mg、Mn、Zn、Cu的含量达到最大值。低硒处理(Se≤4.4 mg·kg-1)显著提高了烤烟各部位对矿质元素的吸收,尤其对N、K、Ca、Mg、Mn的影响最为显著,从而促进了烤烟的生长,烟叶化学成分更加协调;而高硒处理(Se≥11.1 mg·kg-1)则降低了烤烟各部位对矿质元素的吸收,尤其对N、P、K的影响最显著,从而抑制了烤烟的生长。土壤中不同硒浓度通过调控植物对矿质元素的吸收进而影响植物的生长和化学指标,该研究结果为指导富硒烟叶的生产提供了理论依据。     

间作对不同品种玉米和大叶井口边草吸收积累重金属的影响

采用土壤盆栽试验,研究砷（As）超积累植物大叶井口边草（PteriscreticaL.）与玉米品种云瑞6号（ZeamaysL.Yunrui6）、云瑞8号（ZeamaysL.Yunrui8）、云瑞88号（ZeamaysL.Yunrui88）间作对其吸收积累重金属的影响。结果表明,不同玉米品种对大叶井口边草的生物量都有一定的抑制作用,均不同程度地降低了其生物量。与玉米间作显著提高了大叶井口边草地上部和根部对As、Cd的吸收,同时显著降低了地上部对Pb的吸收,而地下部对Pb的吸收却有明显增加,尤其以云瑞8号的间作效应最显著。与单作相比,间作能显著提高玉米各器官重金属含量,只有云瑞88号的茎中As含量明显降低,由单作的310.89mg.kg-1降低至间作的145.86mg.kg-1。研究初步表明,大叶井口边草与云瑞8号间作可提高修复As、Cd、Pb污染土壤的效率。     

蚌埠市区土壤重金属积累特征及生态风险评价

为了解蚌埠市区土壤重金属污染状况,利用原子发射光谱法(ICP-AES)测定了其重金属含量,并依次采用了单因子污染指数法、内梅罗综合污染指数法和Hakanson潜在生态风险指数法对其污染程度和潜在风险性进行了评价。结果表明,蚌埠市区土壤中重金属Zn、Cu、Pb、Cd、Mn和Cr的平均含量依次为90.61 mg kg-1、24.69 mg kg-1、37.27 mg kg-1、0.37 mg kg-1、323.45mg kg-1、22.71 mg kg-1,在安徽省各城市中处于中等偏下水平。单因子污染指数法评价结果表明,Cd为重度污染;Zn、Pb、Cu为轻度污染;Mn和Cr为安全等级。综合污染指数法评价结果表明,工业区和交通区土壤重金属为重度污染,商业区、居民区和文教区为中度污染,公园绿地为轻微污染。潜在生态风险指数法评价结果表明,Cd元素为强生态风险程度;Pb、Cu、Zn、Cr和Mn均为轻微生态风险。工业区和交通区为中等生态风险;商业区、居民区、文教区和公园绿地为轻微生态风险。在去除Cd元素以后,各功能区均处于轻微生态风险水平。总的来说,蚌埠市区土壤除了存在Cd的强生态风险外,其它各重金属生态环境较好。     

硫、硅对水稻体内NPT含量及镉亚细胞分布的影响

在4 mg kg~(-1)的镉污染条件下,设置不同的外源硫和硅供应水平,对辽星1号和沈农315两个品种的水稻进行了土培实验,在分蘖期对辽星1号水稻进行了亚细胞分析,观察在不同条件下重金属镉的亚细胞分布;并在分蘖期测定植株茎叶部分的非蛋白巯基(NPT)含量,研究不同硫硅配比对水稻吸收分配重金属的机理。结果表明,沈农315号水稻叶当中的NPT含量高于辽星1号,外源硫可以提升两个品种水稻叶中的NPT含量,增强对重金属的耐性,同时增加镉在包括液泡在内的细胞可溶部分的分布;施硅可以强化细胞壁,随着施硅量的提升,根茎叶细胞壁中的镉分布均显著提升,并且根细胞壁中的提升幅度大于茎,说明施硅不仅可钝化土壤中的镉,并且在植物体内,加强根细胞壁对镉的固化是硅增强植物体重金属抗性的主要途径。     

新乡市大棚菜田土壤重金属积累特征及污染评价

采用微波消解-ICP-AES技术,测定不同种植年限大棚菜田土壤样品中As、Pb、Zn、Cd、Cr、Mn、Ni、Cu等重金属的含量,研究不同种植年限与大棚菜田土壤重金属累积的相关性以及大棚菜田土壤重金属累积特征,并利用地积累指数法进行污染评价。结果表明:大棚菜田土壤重金属Zn、Pb、Ni、Mn和Cu的含量与种植年限具有极显著相关性;大棚菜田土壤中重金属Cd和Cr的含量与种植年限不相关。重金属元素间相关性分析表明,Zn与Pb、Cd、Ni、Mn、Cr、Cu,Pb与Cd、Ni、Mn、Cr、Cu,Cd与Ni、Mn、Cr,Ni与Mn、Cr、Cu,Mn与Cr、Cu具有污染同源性,Cu与Cd、Cr不具有污染同源性。地积累指数法污染评价结果显示Cd的污染等级达到了6级,已构成了极严重污染;Zn和Cu的污染等级达到2级,已构成了中度污染;Pb、Mn的污染等级达到1级,已经构成了轻~中度污染;As、Ni、Cr均未构成污染。     

大冶矿区周边农田土壤和油菜重金属污染特征研究

以大冶典型铜矿区为中心,辐射周边农田,探索农田土壤重金属污染特征及重金属在油菜中的积累变化规律。结果表明,以湖北省土壤背景值进行评价,土壤受到重金属不同程度的污染,其中Cd严重超标,Cu次之;采用国家二级标准进行评价,Zn、Cr和Pb未对土壤造成污染。进行内梅罗综合污染指数法评价发现,以土壤背景值为评价标准,各采样点均达到重金属严重污染水平;以国家二级标准评价时,只有2号采样点土壤属于中度污染水平,其他样点土壤都受到了较为严重的重金属污染。矿区农田油菜各部位重金属含量变化幅度较大,包括Cu、Pb、Zn、Cd和Co在内的5种重金属含量分布规律都是茎叶〉籽粒≈根,Mn则是籽粒〉茎叶〉根。油菜地上部植株中Cu、Pb、Zn、Cd含量均超出食品卫生标准最高限值,且Cd、Pb超标倍数远大于Cu、Zn。富集系数变化规律为Mn〉Zn〉Cd〉Ni〉Cu〉Pb垌Co。     

土壤可见光-近红外反射光谱与重金属含量之间的相关性

发展基于反射光谱技术的快速、简便、低成本的土壤重金属信息提取方法是区域土壤重金属污染治理所需要的。选择江西贵溪铜冶炼厂污染区,分析了9种重金属元素(Cu、Pb、Zn、Cd、Co、Ni、Fe、Mn及Cr)与土壤可见光-近红外反射光谱之间的相关性及其相关的原因。研究表明,研究区土壤中存在Cu(含量介于66.71~387 mg kg-1之间)和Cd(含量介于0.36~6.019 mg kg-1之间)的强烈富集。土壤重金属含量与反射光谱之间存在显著相关,污染元素Cu的最高相关系数为-0.87,Pb、Zn、Co、Ni、Fe的最高相关系数达到高度相关(|r|>0.80),Cr、Cd、Mn的最高相关系数达到显著相关(|r|>0.70)。微分光谱适于获取土壤中的重金属元素信息,利用组合波段能显著提高相关性。Cu与反射光谱之间的相关性主要受有机质的影响;Pb、Zn、Co、Ni主要受黏土矿物和铁锰氧化物的影响;Cr与反射光谱之间的相关性同时受有机质和黏土矿物的影响。     

内蒙古草原白乃庙铜矿区土壤重金属污染特征研究

对位于内蒙古荒漠草原上的白乃庙铜矿采选矿区土壤和尾矿区周围土壤重金属污染状况进行了调查研究。结果表明,矿区土壤中Cu、Cr、Ni、Fe和Mn浓度均高于内蒙古土壤平均值。单因子指数法评价结果表明,五个调查区域土壤都受到了重金属Cu、Cr、Ni、Mn、Fe的污染,其中Cu为重污染,Cr、Ni、Mn、Fe为轻污染,Pb为安全级别,Zn和As只对某些区域有轻污染。综合污染指数法评价结果表明,五个调查区域的土壤重金属污染等级均属重污染,主要贡献元素是Cu,其次是Cr、Ni、Mn、Fe,这与尾矿砂中这些重金属的浓度是相对应的。由于周边地形复杂,多为低山丘陵,所以该地区主导风向对于尾矿库区不同方向土壤重金属污染水平的影响差异并不显著。     

Evaluation of Different Approaches for Respiratory Quotient Calculation and Effects of Nitrogen Sources on Respiratory Quotient Values of Hydrocarbon Bioremediation

Blechnum orientale L. is a traditional, medicinal fern found in China. To assess the characteristics of heavy metals and As accumulation, the fronds, roots, and the rooting soils of this fern were sampled from urban, suburban, and rural woodlands across Guangdong Province in southern China. The concentrations of As, Cd, Cr, Cu, Hg, Mn, Ni, Pb, and Zn in both the fern and its rooting soils were separately detected by ICP-MS. Contamination levels of woodland rooting soils were also assessed using both a single pollution index and the Nemerow pollution index. Both the metal concentrations and the pollution index showed that soils from urban, suburban, and even rural woodlands were adversely contaminated by As, Cd, Hg, and Pb. Based on transfer factor, B. orientale had good translocation of As, Hg, and Mn, but poor translocation of Cd, Cr, Ni, Cu, Ni, Pb, and Zn from the roots to the fronds. This result suggests that this fern could be an excluder to latter metals. Despite the significantly higher levels of metals in the roots as compared with the fronds, the low bioaccumulation factor suggests that this fern has a weak capacity for metal accumulation.

     

Gehalte von Baumwurzeln an chemischen Elementen einschließlich Schwermetallen aus Luftverunreinigungen

Concentrations of chemical elements in tree roots including heavy metals from air pollution Total concentrations of P, S, Na, K, Mg, Ca, Al, Cr, Mn, Fe, Co, Ni, Cu, Zn, Cd and Pb were measured in roots from beech, spruce, ash, maple and a forest herb (Mercurialis perennis). The root samples were taken from a site with an acid soil type (Saure Braunerde) and from a site with calcareous soil (Rendzina). All elements except Mn, Zn and Pb (on acid soils) and Ca (on calcareous soils) showed higher concentrations in finest roots (<1 mm diameter) compared to fine roots (1–2 mm). In the case of the toxic heavy metals, this is interpreted as a consequence of reduced root uptake due to physiological processes or to organic complexing, followed by an accumulation at the root surface. Compared with aboveground plant parts, roots show accumulation of Al, Pb, Cd and Zn, indicating reduced translocation from roots to shoots. Roots from acid soil show higher concentrations of P, Mn, and Pb than in calcareous soil. The concentrations of Al and heavy metals in the roots are considered to be a consequence of the contamination of the investigated forest sites by long-range transported air pollutants, i.e. acid precipitation and deposition of heavy metals.     

Contents and chemical forms of heavy metals in school and roadside topsoils and road-surface dust of Beijing

Purpose

The concentration of human activities in urban systems generally leads to urban environmental contamination. Beijing is one of ancient and biggest cities on the world. However, information is limited on Beijing’s soil contamination, especially for roadside and campus soils. Thus, the aims of this study were to investigate the contents and chemical forms of toxic heavy metals Cd, Cr, Cu, Ni, Pb, and Zn in the road-surface dust, roadside soils, and school campus soils of Beijing. In addition, enrichment and spatial variation of these toxic heavy metals in the soils and dust were assessed.

Materials and methods

Topsoil samples were collected from the schools and roadside adjacent to main ring roads, and dust samples were collected from the surface of the main ring roads of Beijing. These samples were analyzed for total contents and chemical forms of Cd, Cr, Cu, Ni, Pb, Sc, Zn, Al, and Fe. Enrichment factors (EFs, relative to the background content) were calculated to evaluate the effect of human activities on the toxic heavy metals in soils.

Results and discussion

Heavy metal contents in the road dust ranged from 0.16 to 0.80, 52.2 to 180.7, 18.4 to 182.8, 11.9 to 47.4, 23.0 to 268.3, and 85.7 to 980.9 mg kg^?1 for Cd, Cr, Cu, Ni, Pb, and Zn, respectively. In the roadside soil and school soil, Cd, Cr, Cu, Ni, Pb, and Zn contents ranged from 0.13 to 0.42, 46.1 to 82.4, 22.7 to 71.6, 20.7 to 29.2, 23.2 to 180.7, and 64.5 to 217.3 mg kg^?1, respectively. The average EF values of these metals were significantly higher in the dust than in the soils. In addition, the average EF values of Cd, Cu, Pb, and Zn in the soils near second ring road were significantly higher than those near third, fourth, and fifth ring roads. Anthropogenic Cd, Pb, and Zn were mainly bound to the carbonates and soil organic matter, while anthropogenic Cu was mainly bound to oxides. The mobility and bioavailability of these metals in the urban soils of Beijing generally decreased in the following order: Cd?>?Zn?>?Pb?>?Cu?>?Ni?>?Cr; while in the dust, they decreased in the following order: Zn, Cu, and Cd?>?Pb?>?Ni?>?Cr.

Conclusions

Both EF and chemical forms documented that Cr and Ni in the soils and dust mainly originated from native sources, while Cd, Cu, Pb, and Zn partially originated from anthropogenic sources. In overall, Beijing’s road dust was significantly contaminated by Cd and Cu and moderately contaminated by Cr, Pb, and Zn, while Beijing’s roadside soil and school soil were moderately contaminated by Cd and Pb. However, the maximal hazard quotients (HQs) for individual Cd, Cr, Cu, Ni, Pb, and Zn and comprehensive hazard index (HI) of these metals in the dust and soil were less than 1, indicating that the heavy metals in the dust and soil generally do not pose potential health effects to children, sensitive population.     

宝鸡长青镇铅锌冶炼厂周边土壤重金属污染研究

通过野外采样和实验室分析,在分析土壤基本理化性质的基础上,重点研究宝鸡长青镇铅锌冶炼厂周边土壤中重金属元素的含量和形态特征,并进行了污染评价。结果表明,宝鸡长青镇铅锌冶炼厂周边土壤中Cu、Pb、Zn、Mn、Co、Ni、Cr的平均含量分别为31.8、41.3、102.6、704.6、14.4、37.4、83.2mg·kg-1,均高于陕西省和全国土壤元素背景值,尤其是Cu、Pb和Zn。土壤中Cu、Zn、Ni和Cr主要以残余态的形式存在,Pb、Mn和Co主要以可还原态和残余态的形式存在,重金属的迁移顺序为Mn（63.91%）〉Pb（60.08%）〉Co（51.70%）〉N（i37.12%）〉Zn（32.09%）〉C（r30.58%）〉Cu（19.95%）,其中,Mn、Pb和Co有50%~65%可以发生迁移,易被生物体利用,危害较大。评价结果表明,宝鸡长青镇铅锌冶炼厂周边土壤主要受到了Pb的轻度污染。     

杭州市城市土壤重金属的潜在可淋洗性研究

研究了杭州市城市土壤 8个重金属元素 (Cd、Co、Cr、Cu、Ni、Pb、Zn、Mn)的含量、形态和潜在可淋洗性。结果表明 ,该城市土壤中Cd、Cr、Cu、Ni、Pb、Zn和Mn均有明显的积累 ,其中Cd、Co、Cr和Ni主要以稳定的残余态为主 ,而Cu、Pb、Zn和Mn则以可提取态为主 ,因此在强还原、强酸性或有利于有机质分解条件下Cu、Pb、Zn、Mn的释放潜力较高。用荷兰能源研究中心的淋洗方法 (pH4 0 )测试表明 ,该市城市土壤的重金属可淋洗性较低 ,在一般条件下该城市土壤重金属不会有较大的释放 ,这与该城市土壤中酸可提取态重金属比例较低并含有较高的有机质及粘粒含量有关     

共培养对土壤重金属污染植物修复的调控作用

A co-culture of two plant materials, Astragalus sinicus L., a leguminous plant with concomitant nodules, and Elsholtzia splendens Naki-a Cu accumulator, along with treatments of a chelating agent (EDTA), root excretions (citric acid), and a control with E. splendens only were used to compare the mobility of heavy metals in chelating agents with a co-culture and to determine the potential for co-culture phytoremediation in heavy metal contaminated soils. The root uptake for Cu, Zn, and Pb in all treatments was significantly greater (P < 0.05) than that of the control treatment. However with translocation in the shoots, only Cu, Zn, and Pb in plants grown with the EDTA treatment and Zn in plants co-cropped with the A. sinicus treatment increased significantly (P < 0.05). In addition, when a co-culture in soils with heavy and moderate contamination was compared, for roots in moderately contaminated soils only Zn concentration was significantly less (P < 0.05) than that of heavily contaminated soils, however, Cu, Zn, and Pb concentrations of shoots were all significantly lower (P < 0.05). Overall, this "co-culture engineering" could be as effective as or even more effective than chelating agents, thereby preventing plant metal toxicity and metal leaching in soils as was usually observed in chelate-enhanced phytoremediation.