云南会泽废弃铅锌矿区和非矿区中华山蓼根际真菌镉耐性研究

采用常规、含Cd2＋和含Pb2＋的马丁氏培养基,对云南省会泽县废弃铅锌矿区和非矿区中华山蓼（Oxyria sinensis Hemsle）根际真菌进行分离,将分离的菌株接种到含不同浓度（0、0.05、0.5和5mmol·L-1）Cd2＋的马铃薯葡萄糖培养液中,研究和比较了废弃铅锌矿区和非矿区中华山蓼根际真菌的镉耐性。结果表明,Cd2＋显著抑制铅锌矿区和非矿区中华山蓼根际真菌的生长;Cd2＋对常规、含Cd2＋和含Pb2＋的马丁氏培养基分离的铅锌矿区中华山蓼根际真菌的EC50平均值和最大值均明显大于非矿区,表明铅锌矿区中华山蓼根际真菌对Cd2＋的耐性强于非矿区,采用含Cd2＋培养基,从铅锌矿区中华山蓼根际分离出的真菌Cd2＋耐性最强。     

先锋植物对铅锌尾矿库重金属污染的修复作用

通过野外调查发现湖南湘西花坦铅锌尾矿库定居成功五节芒、辣蓼和截叶铁扫帚3种先锋植物.研究先锋植物对其根际土壤理化性质的改良,先锋植物对重金属Pb、Zn、Cd的吸收积累及其生长对根际土壤重金属化学形态的影响.结果表明,先锋植物的定居提高了其根际土壤有机质、全氮含量和土壤含水率,而pH值均有所降低;3种先锋植物均表现为对Zn具有较强的富集能力,而对Pb、Cd的富集能力很差;先锋植物的生长通过促进残留态Pb、Zn、Cd向弱结合态转化,改变了Pb、Zn、Cd的形态分布,影响土壤中Pb、Zn、Cd的生物有效性.先锋植物五节芒、辣蓼和截叶铁扫帚的自然定居,有利于铅锌尾矿库重金属污染的修复.     

铜对伴矿景天生长及锌镉吸收性的影响

利用植物生长室水培试验和温室土培盆栽试验相结合,研究了Cu对Zn、Cd超积累植物伴矿景天生长及Zn、Cd吸收性的影响。水培试验结果显示,0.31～50μmol/L Cu处理14天对伴矿景天生长及对Zn、Cd吸收性没有显著影响;但100μmol/L Cu处理显著抑制植物生长,降低地上部Zn、Cd及根中Cd浓度,对根中Zn浓度变化没有显著影响。盆栽试验结果发现,在土壤Cu仅为3.61 mg/kg时伴矿景天生长不良,外加Cu显著促进其生长并随Cu浓度升高效应增加;但施用3 mmol/kgEDDS和再次外加250 mg/kg Cu处理使伴矿景天因体内Cu积累量过高而导致明显毒害,地上部Cu最高达1 068 mg/kg。可见低量Cu处理可促进伴矿景天生长,利于植物对土壤Zn、Cd的吸取修复,但土壤中Cu浓度过高将抑制Zn、Cd超积累植物的生长,降低其Zn、Cd吸收能力,在利用该Zn、Cd超积累植物修复高Cu的Zn和Cd污染土壤时应采取适当措施降低Cu毒害效应。     

镉污染土壤的植物修复及其EDTA调控研究I. 镉对富集植物印度芥菜的毒性

本文通过温室盆栽试验研究了在10~190 mg/kg共10个浓度梯度的Cd处理下,印度芥菜生长对Cd的响应、Cd在根与地上部的积累以及在Cd胁迫和毒害条件下对Ca和Zn吸收的影响。结果表明,Cd对印度芥菜生长的毒害浓度在各个生育期各有不同:幼苗期与营养生长前期在70~110 mg/kg左右;营养生长后期在110 mg/kg以上;成熟期在150 mg/kg左右。植物吸收的镉随土壤镉处理浓度的增加而增加,本试验中印度芥菜根和叶积累镉最高浓度分别为300 和160 mg/kg。在Cd胁迫下,印度芥菜吸收的Ca和Zn增加;在Cd毒害条件下,印度芥菜吸收的Ca和Zn下降。认为高浓度的Cd对印度芥菜生长有抑制,但印度芥菜对镉也表现出很强的耐性,这种耐性可能与植物体内Cd和Ca、Zn之间的平衡有关。     

微生物对土壤Cd Pb和Zn生物有效性的影响研究

采用土壤盆栽模拟试验方法,研究了接种不同微生物对重金属富集植物——印度芥菜修复土壤中Cd、Pb、Zn的作用效果。结果表明,接入菌株JA27、JC55、JC40不仅显著促进植物的生长,提高印度芥菜的生物量,降低了土壤pH,并且对土壤Cd、Pb、Zn产生活化作用,使土壤Cd、Pb、Zn有效态含量显著增加,增强印度芥菜对土壤Cd、Pb、Zn吸收量,显著提高了富集植物的修复效果。以上3个处理使印度芥菜地上部Cd、Pb、Zn吸收量分别提高了117%～137%、37%～62%、9%～15.1%。接种JB37对土壤Cd、Pb、Zn产生钝化作用,并且抑制印度芥菜对土壤Cd、Pb、Zn的吸收。JB37处理印度芥菜地上部Pb、Zn吸收量分别降低了72.5%、27%,对Cd吸收量无显著影响。     

朝天委陵菜的重金属耐性与吸收性研究

利用植物生长室水培试验和温室土培盆栽试验的方法,研究了朝天委陵菜在不同浓度Pb水培条件下和Cu、Zn、Pb、Cd复合污染土壤条件下的重金属耐性和吸收性,结果表明,水培条件下随着处理浓度的增加,朝天委陵菜均生长良好,虽高浓度Pb处理下出现植株矮小、叶渐黄、根系变黑等毒害症状,但植株并未死亡,表明在水培条件下朝天委陵菜对Pb具有极强的耐性;在最高浓度3 600μmol/L Pb处理下地上部和根中Pb浓度达到最大值,分别为947 mg/kg和71 053 mg/kg。在温室土培盆栽条件下,朝天委陵菜在外加Cu、Zn、Pb和Cd分别为200、1 000、1 000和5 mg/kg的土壤上较对照生长受到抑制,地上部Cu、Zn、Pb和Cd浓度分别达到741±164、18 248±2 222、1 543±483和29.4±5.2 mg/kg;外加重金属更高时则导致植株死亡。朝天委陵菜对Pb胁迫和Cu、Zn、Pb、Cd复合污染土壤具有较强的耐受性,可作为重金属尤其是Pb污染土壤的修复植物。     

重金属和pH值对类芦种子萌发的影响

类芦(Neyraudia reynaudiana)是一种具有极强耐干旱、贫瘠、高温等逆境的多年生禾草植物,是南方水蚀荒漠化地区、采矿采石厂及各类边坡植被自然恢复中的先锋植物。为探索在各类矿区及受重金属污染的地区采用类芦进行生态修复的可行性,通过室内发芽试验,对类芦种子在Hg2+,Cr6+,Cd2+,Pb2+,Zn2+,Cu2+等6种重金属离子胁迫及不同pH值条件下的萌发能力进行了研究。结果表明,类芦种子在pH值为5.0~9.0的范围内具有良好的萌发能力;6种重金属离子随着处理浓度的升高,对类芦种子的抑制作用逐渐加强,且出现显著抑制作用的最低浓度顺序为:Cd2+Cu2+Hg2+,Zn2+,Cr6+Pb2+;6种重金属对类芦种子活力指数出现显著影响的浓度均较显著影响发芽率、发芽势和发芽指数3个指标的浓度低,说明类芦幼苗生长比种子萌发对6种重金属更加敏感。     

广东大宝山矿区植物对重金属的富集特征

对大宝山矿区自然定居和人工种植的13种优势植物根际土壤污染状况及其对重金属的富集特征进行研究.结果表明,大宝山矿区土壤受重金属Cd、Pb、Zn、Cu污染,其中以Cd、Cu的污染最为严重.在调查的13种优势植物中,铺地黍地上部分的Pb含量达到1 214.00 mg/kg,泡桐叶中Cu含量达到1 024.80mg/kg,超过了Pb和Cu超富集植物含量的临界值(1 000 mg/kg);其运转系数分别为1.77.13.74,都大于1.0,符合超富集植物的标准,表明铺地黍可能是Pb的超富集植物,泡桐可能是Cu的超富集植物.除铺地綦、泡桐外,其他11种优势植物的重金属吸收能力没有达到超富集植物的标准,但它们能在此区域定居,表现出对重金属有较强的耐性,其中象草、纤毛鸭嘴草、芒萁、五节芒、马尾松对重金属复合污染胁迫的耐性较强,可作为大宝山矿植被重建的先锋物种.     

镉污染土壤的植物修复及其EDTA调控研究：Ⅰ、镉对富集植物印度芥菜的毒性

本通过温控盆栽试验研究在10－190mg/kg共10个浓度梯度的Cd处理下，印度芥菜生长对Cd的响应，Cd在根与地上部的积累以及在Cd胁迫和毒害条件下对Ca和Zn吸收的影响，结果表明，Cd对印度芥菜生长的毒害浓度在各个生育期各有不同：幼功期与营养生长前期在70－110mg/kg左右；营养生长后期在110mg/kg以上；成熟期在150mg/kg左右。植物吸收的镉随土壤镉处理浓度的增加而增加，本试验中印度茶菜根和叶积累镉最高浓度分别为300和160mg/kg，在Cd胁迫下，印度芥菜吸收的Ca和Zn增加，在Cd毒害条件下，印度芥菜吸收的Ca和Zn下降。认为高浓度的Cd对印度芥菜生产有抑制，但印度芥菜对镉也表现出很强的耐性，这种耐性可与植物体内Cd和Ca，Zn之间的平衡有关。     

超积累植物东南景天根际土壤酶活性研究

通过野外调查和盆栽试验研究了超积累植物东南景天根际土壤酶活性变化及其与重金属有效态的关系。研究结果表明,在矿山土壤、重度污染土壤和轻度污染土壤上,种植超积累生态型东南景天后,根际土壤有效态Zn分别比非根际减少了14.3%,7.9%和47.4%,有效态Cd分别比非根际减少25.1%,21.9%和20%。在铅锌矿区,东南景天生长地段土壤蔗糖酶、酸性磷酸酶、脱氢酶活性高于其它植物生长地段。在矿山土壤和重度污染土壤中,超积累生态型东南景天根际土壤酶活性明显高于非根际土壤,同时也高于非超积累生态型根际土壤。Pb、Zn、Cd、Cu4种重金属对东南景天根际土壤脲酶、蔗糖酶、脱氢酶活性均有抑制作用,而Pb对磷酸酶有一定的刺激作用。东南景天根际土壤脱氢酶、酸性磷酸酶活性与重金属有效态含量呈极显著相关。     

黑麦草生长及根系形态对土壤Cd，Pb与石油污染的响应

[目的] 研究不同污染条件下黑麦草生理指标的动态变化,为植物修复污染土壤提供初步理论基础。[方法] 通过室内试验模拟不同类型的土壤污染。设置4个处理,未污染土壤+黑麦草（SH）、重金属污染土壤（500 mg/kg Pb²⁺和50 mg/kg Cd²⁺）+黑麦草（SGH）、石油污染土壤（1 000 mg/kg石油）+黑麦草（SPH）、石油和重金属复合污染土壤（500 mg/kg Pb²⁺,50 mg/kg Cd²⁺和1 000 mg/kg石油）+黑麦草（SPGH）,采用WINRHIZO根系分析系统测量根系形态指标,用分光光度计测量叶片色素指标,研究不同类型土壤污染对黑麦草生长的影响。[结果] 3种不同类型的污染土壤均不同程度地刺激了黑麦草根系的生长。与未污染处理相比,在20 d时,石油重金属复合处理下的黑麦草根系的根长、根表面积、根体积、根直径分别增加了88.10%,148.60%,221.90%,32.20%。与未污染相比,随着培养时间的增加各污染处理的地下生物量呈现出先增加后减少的趋势,地上生物量均低于未污染处理,且在第10,40,80 d时,复合污染处理的地上生物量最小,较未污染处理分别降低了34.68%,45.42%,58.05%。80 d时,重金属污染处理、石油污染处理和石油重金属复合污染处理的黑麦草叶绿素含量显著低于未污染处理,分别降低了26.84%,44.82%和47.02%。[结论] 不同污染物都可以促进黑麦草根系形态发育,降低黑麦草的生物量及色素含量;石油重金属复合处理对黑麦草的生长影响最大,石油污染处理次之。基于不同污染物对黑麦草根系形态及生长影响的差异,在今后植物修复土壤污染过程中,可添加一些生长调节物质来缓解污染对植物的毒害作用,提高植物生物量及增强相关生理功能,提升污染土壤修复效果。     

养殖废水灌溉下施用生物质炭和果胶对土壤养分和重金属迁移的影响

【目的】 养殖废水中含有丰富的养分,但也含有一定的重金属。本文研究了生物质炭和果胶对养殖废水灌溉下的土壤–植物系统养分和重金属迁移规律的影响,以利用养殖废水中的养分,并对其重金属进行调控。 【方法】 选取新乡市郊区农田土壤为供试土壤,采用根箱试验方法种植玉米。设置根箱土壤中添加1%的生物质炭和果胶,分别灌溉蒸馏水和养殖废水发酵产生的沼液。测定了土壤中养分和重金属的含量,探讨了其在土壤–植物系统的迁移规律。 【结果】 沼液灌溉的植株地上部生长与蒸馏水灌溉无显著差异。果胶相比于生物质炭可以促进植株生长。沼液灌溉时,果胶处理的根系和地上部生物量分别比对照增加了25.38%和31.21%。沼液灌溉普遍降低了根际和非根际土壤的pH,生物质炭处理和果胶处理与对照根际和非根际土壤的pH均无显著差异。沼液灌溉增加了非根际土壤的电导,生物质炭相比于果胶增加了土壤的电导。沼液灌溉增加了土壤全氮、有效磷、速效钾和有机质含量。果胶根际土壤的全磷、碱解氮、有效磷、有效Fe、有效Mn均高于生物质炭处理,生物质炭处理根际和非根际土壤的全钾和速效钾含量均高于果胶处理。沼液灌溉相比于蒸馏水灌溉,增加了植株根、茎中N含量和Ca含量。生物质炭处理植株根茎叶N含量、根茎P含量、茎K含量、根茎叶Ca含量、根茎Mg含量高于果胶处理,但果胶处理养分的转运系数较高。养殖废水灌溉增加了根际和非根际土壤中有效Cu和Zn尤其是Zn的含量。与对照相比,生物质炭降低了根际土壤Cu、Pb、Ni的含量,而果胶增加了它们的含量。沼液灌溉增加了植株根茎叶中Cu、Zn、Pb含量,果胶处理植株根系Cu、Zn、Pb、Cd、Ni含量最高,但向地上部转运较少。 【结论】 在北方碱性土壤灌溉养殖废水发酵产生的沼液时,施用生物质炭和果胶可以提高土壤肥力和植株养分含量,生物质炭通过减少土壤中有效态重金属含量以减少重金属在植物体内累积,果胶虽然增加土壤有效态重金属含量,但可以降低其向地上部的转运,避免了重金属在植物体内的累积。      

Use of Spinach, Radish, and Perennial Ryegrass to Assess the Availability of Metals in Waste Foundry Sands

Opencast coalmine effluent contains higher concentrations of Cd, Cr, Co, Ni and Pb. Biofiltration of these metals has been demonstrated successfully with the help of aquatic macrophytes i.e., E. crassipes, L. minor and A. pinnata. Experiments revealed E. crassipes reduced highest concentration of heavy metals followed by L. minor and A. pinnata on 20th days retention period. Plant tissue analysis revealed higher accumulation of metals in roots than leaves. Highly significant correlations have been noted between removal of heavy metals in effluent and their accumulation in roots and leaves of the experimental sets. Translocation factor also revealed lower transportation of metals from root to leaves. Reduction in chlorophyll and protein content was noted with the accumulation of heavy metals. N, P and K analysis in plant tissues indicated continuous decrease in their concentration with increasing metal concentration. Negative and significant correlations between metal accumulation and N, P and K concentrations in plant tissues showed adverse effects of heavy metals. Analysis of variance (Dunnett t-test) showed significant results (p?<?0.001) for all the metals in different durations.     

Tolerance to cadmium of vesicular arbuscular mycorrhizae spores isolated from a cadmium-polluted and unpolluted soil

We carried out a trial to investigate if vesicular arbuscular (VA) mycorrhizae from a Cd-polluted soil can increase both their Cd tolerance and their influence on the host plant, compared with the same strain from unpolluted soil. Inocula (S0, S1 and S2, respectively), were prepared from soil containing 0, 10, 100 mg/kg Cd (T0, T1 and T2, respectively). Each inoculum was added to each soil giving nine treatments. The percentage infection of barley roots and the spore numbers decreased proportionally with increasing Cd concentration in soil. However, the S2 inoculum showed the highest capacity to colonise the barley roots. This inoculum also created the best biotic barrier against the movement of Cd from the roots to the shoot in the T2 soil. In the T1 soil, the S1 and S2 inocula were less efficient than the S0 inoculum, probably because the level of soil pollution was not sufficiently high for any difference to be seen. We concluded that VA mycorrhizae can adapt to heavy metals and that their performance can influence metal translocation in the plant, providing a biological barrier. This is very important for the use of VA mycorrhizae in the reclamation of polluted soils.     

Accumulation and output of heavy metals by the invasive plant Spartina alterniflora in a coastal salt marsh

Spartina alterniflora is a foreign introduced species and has far-reaching effects on salt marsh ecosystems, particularly on the biogeochemical cycle of heavy metals. To ascertain whether the invasive plant Spartina alterniflora Loisel is a source of metals in the environment, we determined the bimonthly concentrations of heavy metals, chromium(Cr), lead(Pb), copper(Cu), zinc(Zn),and manganese(Mn), in the roots, stems, and leaves of S. alterniflora from a typical semidiurnal tidal zone in the coastal area of northern Jiangsu Province, China. Based on the measurements, we calculated annual metal primary accumulation and output. To calculate the annual output of heavy metals from S. alterniflora, a new method that calculates the annual rate of biomass loss and decomposition was developed. The annual primary accumulation of Cr, Pb, Cu, Zn, and Mn was 19.08, 84.19, 63.74, 442.58, and774.66 mg m~(-2), respectively, and the annual output from S. alterniflora to the surrounding environment was 4.01, 18.09, 14.00, 97.11,and 164.28 mg m~(-2), respectively. Spartina alterniflora only provides temporary storage, and its absorption of heavy metals could be used to remediate contaminated soil and for phytomining. The heavy metals released by S. alterniflora to the environment cannot be ignored; thus, S. alterniflora should be considered a source of metal contamination. Therefore, when we evaluate the remarkable ability of certain plant species to concentrate metals in their tissues, the balance between heavy metal accumulation and output should be considered.     

工业和农业污染稻田土壤重金属的赋存形态及水稻吸收运移比较

[目的]稻田土壤重金属污染是当前农产品安全生产关注的重要问题.本文比较分析工业和农业污染源稻田土壤重金属的赋存形态及水稻吸收运移,以期为稻田土壤重金属污染控制提供参考.[方法]在长江中下游地区调查选取工业源和农业源重金属污染稻田各27块,在水稻成熟期使用抖根法采集根际土壤及水稻根系和籽粒样品,采用Tessier七步提取...     

脱硫石膏改良重度苏打盐化土的环境效应

为了解连续施用脱硫石膏改良苏打盐化土的持续效应及环境效应,以经过3a大田连续施用不同量脱硫石膏(0,15,22.5,30t/hm~2)改良的重度苏打盐化土为供试土壤,采用盆栽试验方法,研究2a盆栽试验后,脱硫石膏的持续效应对饲草玉米生长、土壤环境以及农作物中重金属累积的影响。结果表明:15t/hm~2用量的脱硫石膏可以显著提高饲草玉米的出苗率、株高、茎粗和生物量,较对照分别提高20.6%,16.8%,8.1%和10.1%,试验范围内改良效果最佳。脱硫石膏使土壤的pH、EC降低,Na~+减少,Ca~(2+)和SO_4~(2-)增加,且脱硫石膏用量越大,影响越大。土壤和饲草玉米地下部中的As、Hg、Ni含量随脱硫石膏用量的增加而增加,试验范围内土壤重金属含量均符合二级国家土壤环境安全标准(GB 15618—1995)。饲草玉米地上部重金属含量与脱硫石膏添加量无显著相关关系,根据饲料卫生标准(GB 13078—2001),各处理玉米中重金属含量均未超标。饲草玉米对重金属的富集作用地下部大于地上部,且对不同重金属富集能力CdHgAsNi。利用适量的脱硫石膏量改良苏打盐化土的持续效应良好,且对环境未造成不良影响。     

伊乐藻对CuCd污染底泥修复的应用研究

在自然条件下,采用人工模拟水缸培养方法,研究了湖泊底泥不同Cu、Cd处理对沉水植物伊乐藻生长、叶绿素含量以及Cu、Cd吸收和积累的影响。结果表明,较低浓度Cu刺激伊乐藻的生长（生物量、叶绿素）,高浓度抑制伊乐藻的生长;随着Cd处理浓度的增加,伊乐藻的生物量、叶绿素含量均一直降低,在底泥Cd含量为168．69mg·kg^-1 DW（含背景值）时,植株出现死亡。随着Cu处理浓度的增加,伊乐藻体内的Cu含量一直增加,在底泥cu含量为414mg·kg^-1DW（含背景值）时,根部、叶部的富集系数均达到最大（0．21和0．17）;伊乐藻体内的Cd含量随Cd处理浓度的增加先增后减,底泥Cd含量为88．69mg·kg^-1 DW时,根部、叶部的富集系数均达到最大（0．07和0．09）。以上结果说明,伊乐藻对Cu、Cd具有很强的耐受性,可以作为原位修复Cu和Cd污染底泥的植物种类应用。     

Phytoremediation Potential of Vetiver Grass (<Emphasis Type="Italic">Vetiveria zizanioides</Emphasis>) for Treatment of Metal-Contaminated Water

Phytoremediation using vetiver grass (Vetiveria zizanioides) has been regarded as an effective technique for removing contaminants in polluted water. This study was conducted to assess the removal efficiency of heavy metals (Cu, Fe, Mn, Pb, Zn) using vetiver grass (VG) at different root lengths and densities and to determine metals uptake rate by plant parts (root and shoot) between treatments (low and high concentration). Removal efficiency for heavy metals in water by VG is ranked in the order of Fe>Pb>Cu>Mn>Zn. Results showed that VG was effective in removing all the heavy metals, but removals greatly depend on root length, plant density and metal concentration. Longer root length and higher density showed greater removals of heavy metals due to increased surface area for metal absorption by plant roots. Results also demonstrated significant difference of heavy metals uptake in plant parts at different concentrations indicating that root has high tolerance towards elevated concentration of heavy metals. However, the effects were less significant in plant shoot suggesting that metals uptake were generally higher in root than in shoot. The findings have shown potential of VG in phytoremediation for heavy metals removal in water thus providing significant implication for treatment of metal-contaminated water.     

Potential of Aquatic Macrophytes as Bioindicators of Heavy Metal Pollution in Urban Stormwater Runoff

The concentrations of heavy metals in water, sediments, soil, roots, and shoots of five aquatic macrophytes species (Oenanthe sp., Juncus sp., Typha sp., Callitriche sp.1, and Callitriche sp.2) collected from a detention pond receiving stormwater runoff coming from a highway were measured to ascertain whether plants organs are characterized by differential accumulations and to evaluate the potential of the plant species as bioindicators of heavy metal pollution in urban stormwater runoff. Heavy metals considered for water and sediment analysis were Cd, Cr, Cu, Ni, Pb, Zn, and As. Heavy metals considered for plant and soil analysis were Cd, Ni, and Zn. The metal concentrations in water, sediments, plants, and corresponding soil showed that the studied site is contaminated by heavy metals, probably due to the road traffic. Results also showed that plant roots had higher metal content than aboveground tissues. The floating plants displayed higher metal accumulation than the three other rooted plants. Heavy metal concentrations measured in the organs of the rooted plants increased when metal concentrations measured in the soil increased. The highest metal bioconcentration factors (BCF) were obtained for cadmium and nickel accumulation by Typha sp. (BCF = 1.3 and 0.8, respectively) and zinc accumulation by Juncus sp. (BCF = 4.8). Our results underline the potential use of such plant species for heavy metal biomonitoring in water, sediments, and soil.