盐胁迫对2种栎树苗期生长和根系生长发育的影响

以低浓度(50 mmol/L)和高浓度(150 mmol/L)NaCl处理弗吉尼亚栎(Quercus virginiana)和麻栎(Quercus acutissima)1年生幼苗,研究了2种栎树在盐胁迫下的生长、对盐分的敏感性和耐受性及其根系形态学参数变化以及根系对盐离子的吸收与积累。结果表明,高浓度盐胁迫明显抑制了2种栎树地上部生物量的积累(P0.05),而低浓度盐胁迫对弗吉尼亚栎地上部干重的影响不明显,但显著抑制了麻栎地上部干重(P0.05);2种栎树的根冠比在盐胁迫下呈增加趋势,特别是在高浓度盐胁迫下,2种栎树的根冠比明显增加(P0.05),盐胁迫下增加生物量在根部的分配是植物应对盐胁迫的方式之一。2种栎树根部生物量积累在盐胁迫下变化不明显,但2种栎树根系形态学参数在盐胁迫下的响应不同,弗吉尼亚栎根系总长度、总表面积和总体积在盐胁迫下均有不同程度增加,特别是在低浓度盐胁迫下,根系形态学参数明显增加(P0.05),但麻栎根系形态学参数有下降趋势,但与对照相比变化不明显;通过对不同径级根系总长的分析发现,弗吉尼亚栎根系总长度的增加主要是由于直径小于2 mm的细根总长的增加,细根长度的增加对于植物吸收水分和营养物质具有重要意义;通过对Na+和Cl-在根系的含量分析表明,盐胁迫下2种栎树根系盐离子的积累均有明显增加,但弗吉尼亚栎根系盐离子的含量在低浓度和高浓度盐胁迫下的差异不明显,而麻栎在高浓度盐胁迫下根系盐离子的含量明显高于弗吉尼亚栎。综合2种栎树盐胁迫下的生物量分配策略和根系形态学响应以及盐离子的积累规律,证明2种栎树尽管在生物量分配策略方面具有相同的特点,但根系的响应策略截然不同,弗吉尼亚栎在盐胁迫下能够扩大根系吸收范围,维持较高的K+/Na+比值,而麻栎在盐胁迫下根系由于吸收过多的盐离子,导致根系的生长发育受到抑制,影响了根系在逆境中的分布范围,从而在一定程度上避免了进一步的盐害。     

曼陀罗和苍耳对污染土壤中镉的吸收与富集

目的:研究曼陀罗和苍耳对重金属镉的吸收与富集特征.方法:室外盆栽试验和室内原子吸收测定曼陀罗和苍耳体内的镉含量.结果:土壤中的镉刺激了植物的生长,曼陀罗和苍耳的生物量都比对照有所增加;曼陀罗和苍耳体内的镉含量随土壤中镉浓度的增加而增加;当土壤中镉浓度为100mg·kg-1时,曼陀罗地上部分富集系数为1.15,大于1,而在其它测试浓度下均小于1;苍耳地上部分的富集系数在所有测试浓度下都小于1.结论:曼陀罗和苍耳都不属于镉的超富集植物.     

Cd胁迫下苎麻的生长响应与富集、转运特征研究

通过盆栽试验,分析了苎麻湘苎三号在Cd胁迫下生长响应及其富集、耐性和迁移特征.结果表明,低浓度Cd处理(≤100mgmg·kg^-1)能促进苎麻生长发育,株高、茎粗、有效分蘖数和生物量都有所增加,以50mg·kg^-1胁迫处理最佳;此后则随处理浓度增加抑制效应越明显,到500mg·kg^-1时,各营养生长指标较对照显著减少,但仍生长较好,表明苎麻对重金属Cd胁迫具有很强的耐性.地下部与地上部Cd含量随处理浓度提高而增加,至500 mg.k g-1浓度时达最高值,分别为221.95mg.kg-1和390.61mg·kg^-1.苎麻Cd富集系数和转运系数分别为0.47～1.10和0.57～0.94.因此,苎麻不属于Cd超富集植物,而只是Cd富集植物,鉴于其具有根系发达、保水固土能力强和地上部生物量大等特点,苎麻是目前重金属Cd污染修复较理想的植物.     

上海地区绿化树种重金属污染防护特性的研究

通过测定土壤样品的重金属含量,调查了上海七宝镇污染水系两侧与上海宝钢集团厂区的重金属污染状况。结果表明,在污染水系两侧重金属含量较对照稍高,而上海宝钢厂区各样点土壤重金属含量明显高于对照,存在较严重的污染．同时在这两处重金属污染地带观察记录了绿化树种的生长状况,采集植物样品以ICP仪进行树木样品的重金属含量分析,综合两方面数据对近20种常见绿化树种的重金属污染的防护特性进行了比较研究．结果表明,法国冬青、紫薇、木芙蓉、女贞和龙柏等植物种类富集重金属能力较强,且生长状况较为良好,最适于作为重金属污染厂区的生态防护绿化的主要树种;而蚊母、夹竹桃和石楠等植物种类虽然富集重金属能力较低,但有较强的耐性,能良好生长。也适于作为污染区绿化美化树种。     

菰和菖蒲对重金属的胁迫反应及其富集能力

通过盆栽实验研究了Cu—Zn—Ph-Cd复合污染条件下,菰和菖蒲的生长状况、生理特性及吸收和富集重金属的能力。结果表明,高浓度污染下菰和菖蒲不能存活;低、中浓度中菖蒲的生长受到抑制,菰各生长指标与对照相比差异不显著,表明菰对低、中浓度重金属的耐性强于菖蒲。随着污染浓度的增加,菰和菖蒲叶片叶绿索含量显著降低;菰叶绿素a／b值略有降低,菖蒲叶绿素a／b值显著降低;菰和菖蒲叶片脯氨酸含量、相对电导率显著升高,超氧化物歧化酶（SOD）、过氧化物酶（POD）活性在低浓度时升高,中浓度时降低。菰体内重金属含量为Zn〉Cu〉Pb〉Cd,菖蒲体内的含量为Cu〉Zn〉Pb〉Cd,且二者体内的重金属含量都随着污染浓度的增加而升高。菰和菖蒲对Cd的富集系数较大,地上部分（茎与叶）和地下部分（根与根状茎）均大于1;对Pb的富集系数较小,地上部分和地下部分均小于1。菰和菖蒲地下部分重金属含量均高于地上部分含量,二者根系对4种重金属都有较强的滞留效应,平均滞留率均大于50％。各处理中菰对重金属的吸收量均高于菖蒲。综合分析菰和菖蒲的生长、生理及富集重金属的能力,菰比菖蒲更适用于低、中浓度重金属污染水体的生态修复。     

5种湿地植物对土壤重金属的富集转运特征

选择芦苇、水葱、千屈菜、扁秆藨草、长苞香蒲5种湿地植物进行盆栽实验,比较它们对土壤中的5种重金属镉、铬、汞、铅、锌的富集特性,分析重金属在各植物体和土壤中的动态分布,以评价所测植物对土壤中重金属的综合富集能力,为利用植物修复金属污染土壤提供理论依据和技术支持。结果表明:(1)种植湿地植物对土壤重金属的富集效果显著高于无植物对照,且随着处理时间的延长,土壤中重金属镉、铬、汞、铅、锌的含量均呈下降趋势。(2)湿地植物对重金属镉、铬、汞、铅、锌的富集效果差异显著,其中水葱根部对重金属镉的富集系数最大,芦苇根部对重金属铬、汞、铅、锌的富集系数均最大,千屈菜、扁秆藨草和长苞香蒲根部对5种重金属的富集系数均较小;芦苇地上部分对金属镉的富集系数最大,千屈菜地上部分对金属铬、汞、铅的富集系数均最大,水葱地上部分对金属锌的富集系数最大。(3)5种湿地植物对重金属镉、铬、汞、铅、锌的转移系数差异显著,其中扁秆藨草对土壤中镉、铬、铅、锌的转移系数均为最大,对铬和锌的转移系数均大于1,长苞香蒲对铬的转移系数大于1,仅次于扁秆藨草。其他3种植物对5种重金属的转移系数均小于1。研究表明,5种湿地植物对重金属Cd、Cr、Hg、Pb、Zn都有富集和转移的能力,但不同植物对不同重金属的富集效果不同。     

黄土丘陵区主要林分生物量及营养元素生物循环特征

以黄土丘陵区子午岭为研究区域 ,用标准木法和收获法对暖温带森林优势群落辽东栎林、油松林及刺槐人工林的生物量、营养元素生物循环量及循环特征进行了研究。结果表明 :黄土丘陵区子午岭油松林、辽东栎林和刺槐人工林 3林分总生物量为 :86 .2 4 7、12 9.0 0 5 t/ hm2和 14 4 .795 t/ hm2 ,乔木层生物量分别为 :85 .2 2 3、12 6 .989t/ hm2和 14 2 .4 88t/ hm2 ,随群落针阔树种转化替代 ,群落总生物量呈现明显的增加趋势。年均生长量为 3.2 75～ 5 .6 99t/ hm2。生物量和年生长量排序为刺槐人工林 >辽东栎林 >油松林。 3林分林下植被层生物量、凋落物贮量表现为刺槐林 >辽东栎林 >油松林 ,林下植被层生物量的差异主要是由林分郁闭度和林下凋落物的不同引起的 ;刺槐林和辽东栎林林下植被层发达的根系和较高的凋落物量有利于提高土壤肥力、保持水土。同化器官的各种元素含量高于其它器官 ,茎中营养元素的含量最低。乔木层营养元素积累量分别为 :0 .74 5、1.378t/ hm2和 1.80 5 t/ hm2 。不同林分不同营养元素的积累量差别较大。因采伐而引起的 3林分林地养分流失量分别达 6 5 .4 5 %、5 3.76 %和 2 5 .1%。 3林分林下植被层和凋落物层的营养元素积累量排序为 :刺槐林 >辽东栎林 >油松林。凋落物营养元素贮     

AMF和植物富集土壤中铅和镉的效应

为了筛选更适合修复土壤重金属污染的丛枝菌根真菌(Arbuscular mycorrhizal fungi,AMF)和寄主植物组合,对二月兰(Orychophragum violaeeus)、龙葵(Solanum nigrum)和麦冬(Ophiopogon japonicus)接种AM真菌摩西管柄囊霉(Funneliformis mosseae)和根内球囊霉(Glomus intraradices),通过测定Pb(1 000 mg/kg)和Cd(1.5 mg/kg)污染土壤中上述3种植物生长状况及其对Pb和Cd吸收与富集能力的影响,旨在获得富集重金属能力较强的AM真菌+植物组合。结果表明,施加Cd土壤中二月兰和麦冬的生物量高于对照,施加Pb或Cd处理显著降低龙葵的生长。龙葵对Pb和Cd富集能力最强,麦冬最弱;二月兰对Pb和Cd的转移能力最强。供试植物对Cd的富集能力和转移能力均大于对Pb的富集能力和转移能力。在Pb和Cd的胁迫下,摩西管柄囊霉和根内球囊霉均能促进供试植物的生长发育,并增加植株对Pb和Cd的富集系数,其中,摩西管柄囊霉对龙葵生物量、Pb和Cd富集系数的效应最大。综合考虑植物本身的生物量、对Pb和Cd的耐受力和富集能力,结论认为摩西管柄囊霉+龙葵组合是修复Pb或Cd污染土壤的高效AM真菌+植物组合之一,相关机制有待进一步研究。     

香根草和百喜草对铅锌尾矿重金属的抗性与吸收差异研究

铅锌尾矿是一类重金属含量极高,对植物生长产生毒害的生境.盆栽实验的结果显示,香根草和百喜草在纯尾矿或由尾矿和垃圾组成的混合基质上都能生长,但植物的长势随基质中重金属含量的增加而减弱,其中香根草的生物量所受的影响比百喜草的更大,即百喜草有比香根草更强的重金属抗性.2种植物体内的重金属含量高低均为Zn＞Pb＞Cu,但二者对它们的富集能力大小分别是,香根草为Zn＞Cu＞Pb,百喜草则为Cu＞Zn＞Pb.香根草和百喜草的根系对3种重金属都有较强的滞留效应,滞留率均在50%以上;其中香根草对重金属的滞留率又明显高于百喜草;而且,同一植物对不同的重金属的滞留率也明显不同,香根草对Pb的滞留率最高,而百喜草对Cu的滞留率显著高过对Zn和Pb.由于香根草的生物量明显大于百喜草,结果香根草对Pb、Zn的吸收量比百喜草高.当用25%的垃圾改良金属尾矿时,百喜草对重金属的吸收量即达最大;而香根草则在尾矿和垃圾各占50%的基质中吸收最多的重金属;因此,添加一定量的垃圾(25%～50%左右)用于尾矿改良时,不仅能使尾矿得到更快的植被恢复与更高的植物修复效果,而且能使垃圾资源得到充分合理的利用.总之,当开展对金属尾矿的植被恢复时,可选择种植抗性强、覆盖快的百喜草,但如果要对尾矿中的重金属进行生物净化,则应选择种植生物量大的香根草,种植香根草还可较好地防止重金属的二次污染或生物富集.     

重金属镉在番茄及其害虫西花蓟马中的积累与传递

重金属镉（Cd）是农田土壤中的重要污染源,可在植物和植食性昆虫中积累与传递。本文采用水培法,研究了不同浓度的Cd在番茄Solanum lycopersicum不同组织和在其重要害虫西花蓟马Frankliniella occidentalis体内的积累量。结果表明,随着水培营养液中Cd浓度的增加,番茄植株的根、茎和叶中Cd含量呈增长趋势。根中Cd的积累量远高于茎和叶,当水培溶液中Cd含量为20 mg/L时,根、茎和叶中的积累量分别达19 333.67±233.38、122.67±6.84和147.33±2.96 mg/Kg（干重）。随着Cd浓度的增加,番茄根、茎和叶的鲜重和干重均显著下降。西花蓟马取食Cd处理的番茄叶片后,体内Cd显著积累,最高达1.95±0.36 mg/Kg。同时,Cd积累量的提高进一步影响了以番茄叶片为食的西花蓟马的适合度,降低了其存活率。除对照外,番茄茎-叶的转移系数和叶片对Cd的富集系数均大于1,叶片表现出较强的富集能力。而在所有的试验浓度处理中,西花蓟马对Cd的富集系数和转移系数均小于1,表明Cd未在其体内产生生物放大作用。研究结果明确了Cd在番茄各组织及其害虫中的积累和传递水平,为揭示重金属在农业生态系统食物链中的富集效应提供了基础数据。     

Wild Flora of Mine Tailings: Perspectives for Use in Phytoremediation of Potentially Toxic Elements in a Semi-Arid Region in Mexico

The aim of this research was to identify wild plant species applicable for remediation of mine tailings in arid soils. Plants growing on two mine tailings were identified and evaluated for their potential use in phytoremediation based on the concentration of potentially toxic elements (PTEs) in roots and shoots, bioconcentration (BCF) and translocation factors (TF). Total, water-soluble and DTPA-extractable concentrations of Pb, Cd, Zn, Cu, Co and Ni in rhizospheric and bulk soil were determined. Twelve species can grow on mine tailings, accumulate PTEs concentrations above the commonly accepted phytotoxicity levels, and are suitable for establishing a vegetation cover on barren mine tailings in the Zimapan region. Pteridium sp. is suitable for Zn and Cd phytostabilization. Aster gymnocephalus is a potential phytoextractor for Zn, Cd, Pb and Cu; Gnaphalium sp. for Cu and Crotalaria pumila for Zn. The species play different roles according to the specific conditions where they are growing at one site behaving as a PTEs accumulator and at another as a stabilizer. For this reason and due to the lack of a unified approach for calculation and interpretation of bioaccumulation factors, only considering BCF and TF may be not practical in all cases.     

多花黑麦草在酸化铅锌尾矿上的定植和生长

铅锌矿尾矿上设置长喙田菁压青和不压青处理,在此基础上研究多花黑麦草的萌发、生长和重金属积累情况.结果表明,种植长喙田菁改善了尾矿理化性状,尤其是提高了有机质、全N、有效态磷和K的含量.尾矿的强酸性环境(pH<3)是影响黑麦草在其上定植的主要因素.施用石灰可暂时改善尾矿酸度,但实验结束时尾矿酸度几乎完全恢复原状.因此,施用石灰可能只对种子发芽产生作用.大多数情况下多花黑麦草能在尾矿上萌发、生长和定植,并产生较大的生物量(DM1.4～3.2t·km^-2),表现出对酸性尾矿环境的一定的适应性.与未栽培长喙田菁的对照相比,栽培长喙田菁处理以及栽培长喙田菁并压青处理分别使多花黑麦草的生物量提高了4.8%～39.5%和7.7%～139.5%,其中压青处理又比不压青处理提高了2.7%～75.8%.“长喙田菁多花黑麦草”植被系列是一个成功的铅锌矿尾矿废弃地复垦的先锋阶段.     

基于几何形态分析的栎属白栎组叶片形态特征

以壳斗科栎属白栎组的5个种作为研究对象进行叶片几何形态学分析(GMMs)。选取了20个天然种群,共采集182个个体,887张叶片,对每张叶片采用几何形态学的标点法,数字化叶形态特征,使5个种的叶形态差异可视化。结果表明: 广义普氏分析可以有效地排除叶片位置和大小对叶片形状的影响。基于个体水平的主成分分析表明,槲树分别与槲栎和枹栎2个种的叶片形态差异明显,基于个体水平的典型变量分析表明,叶片的对称组分可以将槲栎与其他4个种准确区分。叶片非对称组分的多变量分析表明,5个种彼此间区别不明显。基于叶片水平的分析表明: 区分度较高的两组是槲栎vs.槲树(99.5% vs. 100%)和槲树vs.枹栎(99.0% vs. 100%),可以通过叶形准确区分;区分度略低的两组是白栎vs.枹栎(90.5% vs. 86.8%)和槲树vs.蒙古栎(85.1% vs. 82.9%)。本研究为存在频繁杂交渐渗的物种间叶型鉴定提供了新思路。     

Effects of earthworm (Pheretima sp.) on three sequential ryegrass harvests for remediating lead/zinc mine tailings

Farm soil and artificial soil were mixed separately with Pb/Zn mine tailings and placed in the ratios (w/w) of 0, 12.5, 25, and 50% in pots, together with 0.33 g KH2PO4 and 0.35 g urea/pot. Each pot contained 15 ryegrass seedlings (Lolium multiflorum) and 7 earthworms (Pheretima sp.). At the end of the experiment (after the third harvests of ryegrass), the earthworms were all found to be alive and burrowed completely at the bottom of the pots in all treatments. Earthworm activity increased plant biomass significantly in artificial soil/tailings mixtures in the second and third harvests as compared with the control (without addition of earthworms), but not in the farm soil/tailings mixture. The biomass of ryegrass in both soil/tailings mixtures decreased with increase of tailings, especially those containing 50% tailings. In general, the plant biomass obtained from farm soil/tailings mixtures was lower than that from artificial soil/tailings mixtures. Earthworm activity did not significantly increase DTPA-extracted Zn or Pb, in both soil/tailings mixtures. However, the concentrations in farm soil/tailings mixtures were lower in the second and third harvests, compared with the first harvest. The Zn and Pb uptake by ryegrass shoots in the two soils/tailings mixtures did not increase significantly (compared with the control) in the first and second harvests. However, in the third harvest, Zn and Pb uptake increased significantly in farm soil/tailings mixtures, but decreased significantly in artificial soil/tailings mixtures (compared with the control). The results indicated that the presence of earthworms and sequential plant harvesting could be a viable strategy for the remediation of Pb/Zn tailings.     

六种植物对Pb的吸收与耐性研究

 为了选择和筛选重金属Pb的耐性与富集植物,在温室砂培盆栽条件下对铅锌尾矿区附近生长的6种植物(山野豌豆（Vicia amoena Fisch）、草木樨(Melilotus suavena Ledeb)、披碱草(Elymus dahuricus Turca)、酸模（Rumex acetosa）、紫苜蓿(Medicago sativa)和羽叶鬼针草(Bidens maximowicziana Oett))体内Pb的含量与分布、重金属Pb的迁移总量、根系的耐性指数做了研究;拟定了６种植物对Pb的耐性临     

六种植物对Pb的吸收与耐性研究

为了选择和筛选重金属Pb的耐性与富集植物,在温室砂培盆栽条件下对铅锌尾矿区附近生长的6种植物(山野豌豆（Vicia amoena Fisch）、草木樨(Melilotus suavena Ledeb)、披碱草(Elymus dahuricus Turca)、酸模（Rumex acetosa）、紫苜蓿(Medicago sativa)和羽叶鬼针草(Bidens maximowicziana Oett))体内Pb的含量与分布、重金属Pb的迁移总量、根系的耐性指数做了研究;拟定了６种植物对Pb的耐性临     

Mobility and Translocation of Heavy Metals from Mine Tailings in Three Plant Species after Amendment with Compost and Biosurfactant

An experiment was performed to determine the effects of mine tailings alone mixed with compost or with compost plus crude biosurfactant on the accumulation of heavy metals (Pb, Zn, Cu, Cr, Cd, and Ni) in Acacia retinodes, Nicotiana glauca, and Echinochloa polystachya. The plants were grown in soil, mine tailings, and mine tailings containing compost over a period of seven and five months for shrubs or grass, respectively. The plants Acacia retinodes and Nicotiana glauca grown in mine tailings containing compost showed increases in dry biomass (from 62 to 79%) compared with plants in only tailings. Heavy metals accumulated in the roots and leaves showed high translocation rates of Cr in N. glauca, Cd in A. retinodes, and Ni in E. polystachya. Concentrations of heavy metals in the three plants irrigated with crude biosurfactant were not significantly different from those irrigated with water. Zn and Cd fractions within mine tailings containing compost were bound to carbonate, Pb was bound to residues, and Cu was bound to Fe-oxides. Cd had the highest mobility factor followed in order by Zn, Pb, and Cu. The elevated concentrations of Pb in roots and the low translocation rate for N. glauca and A. retinodes indicate that they are suitable for phytostabilizing Pb and Zn.     

Natural Colonization of Plants on Five Lead/Zinc Mine Tailings in Southern China

Mine tailings can have a specific assemblage of plant species due to their unique physicochemical properties, and this process can be important in developing ecological theory and restoration practice. Physicochemical properties and natural colonization of plants on five lead/zinc (Pb/Zn) mine tailings in southern China were investigated. The tailings studied included Fankou and Lechang in Guangdong Province, and Huangshaping, Shuikoushan, and Taolin in Hunan Province. Physicochemical properties of the tailings varied greatly both among and within tailings ponds, but in general, all contained high concentrations of heavy metals (Pb, Zn, Cu, and Cd) and low concentrations of N, P, and organic matter. Toxic levels of heavy metals and deficiency of major nutrients appeared to be the major constraints for colonization of plants on these Pb/Zn tailings and were reflected in the metal concentration of the plant tissues. The natural colonization of plants on these tailings was limited, with only some small patches distributed mainly on the edge of tailing ponds and even fewer patches on the center of the ponds. In total 54 plant species belonging to 51 genera and 24 families were recorded on the five tailings ponds, of which the 13 species belonging to Gramineae were major components of the tailings’ flora. Species establishing on the tailings at the initial colonization phase greatly depended on their seed‐dispersal capacity. Further establishment and growth were then dependent on at least one of the three ecological strategies: (1) microsite (avoidance) strategy: plant establishment on tailings depended on dispersing onto microsites of relatively favorable edaphic conditions; (2) tolerance strategy: plant establishment was a result of evolving metal‐tolerant ecotypes or constitutional metal tolerance; and (3) rhizome strategy: plant establishment on tailings depended on clonal growth by rhizomatous extension.     

Mycorrhizo-remediation of lead/zinc mine tailings using vetiver: a field study

A field study of Pb/Zn mine tailings was conducted to assess the influence of AM fungi and refuse compost on phytoremediation using vetiver grass slips. Our investigation revealed that vetiver could thrive on Pb/Zn mine tailings. The addition of refuse compost resulted in biomass that was more than 3-times higher when compared with the control, and were mainly attributed to an improvement of soil properties, as well as better nutrient supply than untreated control. AMF inoculation also significantly increased the dry matter of vetiver by a rate of 8.1-13.8%. It was observed that concentrations of N and P in the shoots were significantly higher in mycorrhizal treatments than those without AMF inoculation. However, AMF inoculation significantly decreased the metal concentrations in root, but not in shoot. Based on the results, it seems clear that AMF can play an essential role in the phytostabilization of metal contaminated soils.