在蚯蚓影响下土壤Pb、Cd有效态的变化及小白菜对Pb、Cd的富集转移作用

研究了在蚯蚓影响下Pb、Cd添加量不同(Pb:500～1 700 μg·g-1;Cd:1～30 μg·g-1)的土壤中Pb和Cd有效态及其含量的变化以及小白菜(Brassica chinensis L. )对土壤中Pb和Cd的富集和转移作用.结果显示,在蚯蚓的影响下,Pb添加量为500～1 400 μg·g-1的土壤中酸提取态和可还原态Pb含量显著提高,有效态Pb总含量也随土壤中Pb添加量的提高逐渐增加;Cd添加量为5～20 μg·g-1的土壤中酸提取态Cd含量显著提高,有效态Cd总含量也随土壤中Cd添加量的提高而逐渐增加;当土壤中Pb和Cd添加量分别达到1 700和30 μg·g-1时,蚯蚓对Pb和Cd基本无活化作用.在蚯蚓的影响下,小白菜地上部分Pb含量显著提高,对Pb的转移系数也均高于各自的对照,地上部分和地下部分对Pb的富集系数分别为0.037～0.061和0.401～0.628.在蚯蚓影响下,在Cd添加量较低(1～5 μg·g-1)的土壤中小白菜地上部分和地下部分的Cd含量以及对Cd的富集系数均高于各自的对照;而在Cd添加量较高(10～30 μg·g-1)的土壤中小白菜地上部分和地下部分的Cd含量以及对Cd的富集系数均低于各自的对照,并随土壤中Cd添加量的提高逐渐降低;小白菜地上部分和地下部分对Cd的富集系数分别为1.196～11.516和1.744～20.425;各处理组小白菜对Cd的转移系数与各自的对照差异不显著.研究结果显示,蚯蚓主要对土壤中酸提取态和可还原态Pb以及酸提取态Cd有活化作用,并且可促进Pb由小白菜地下部分向地上部分的转移,但对Cd的转移无明显促进作用;此外,小白菜对Pb的富集作用不明显,但对Cd有一定的富集能力,这种能力的大小与土壤Cd含量有关.     

pH对不同富集能力植物根际土壤溶液中镉形态的影响

为了解不同p H对土壤溶液中Cd形态分布的影响,采用Visual MINTEQ 3.0模型和阳极溶出伏安法(ASV)研究土壤p H分别为4.0、5.5、7.0和8.5时镉超富集植物东南景天和非富集植物垂盆草根际土壤溶液中Cd的形态分布。模型计算结果表明:随着p H的升高,2种植物土壤溶液中Cd2+的比例均逐渐减小,其中东南景天根际土壤溶液中Cd2+占总溶解性Cd的比例为46.1%~3.2%,垂盆草为60.9%~9.9%;当土壤p H≥5.5时,土壤溶液中Cd形态主要以有机络合态(Cd-DOM)为主;2种植物相比,4个p H水平下垂盆草土壤溶液中Cd2+比例均高于东南景天,但东南景天中有机络合态Cd所占比例较大。基于ASV法的测定结果表明:东南景天土壤溶液中电活性Cd占总溶解性Cd的比例从最小(p H 8.5时)的5.5%到最大(p H 4.0时)的79.6%,而垂盆草的变化范围为11.8%~86.7%;电活性Cd的测定结果与Visual MINTEQ 3.0模型计算结果显著相关(R2=0.80),从而互相验证了实验测量和模拟计算的可靠性。     

菖蒲幼苗对Cd胁迫的响应及其Cd富集能力分析

研究了菖蒲（Acorus calamus L．）幼苗对不同浓度Cd胁迫的响应及其Cd富集能力。结果表明，随Cd浓度的提高（0～25mg·L^-1），菖蒲幼苗的株高、根长、干质量、叶绿素含量和对Cd的耐性指数均逐渐下降，脯氨酸含量逐渐升高；各处理组的SOD和POD活性均高于对照，且以15mg·L^-1Cd处理组最高。随胁迫时间延长（1—10d），叶绿素含量持续下降，而SOD和POD活性及脯氨酸含量则先升高后下降。菖蒲幼苗体内Cd含量随Cd浓度的提高而增加，根系对Cd的富集能力高于地上部分。在Cd胁迫条件下，菖蒲幼苗对Cd的转移系数小于1，根系对Cd的滞留率为89．5％-93．9％，表明菖蒲幼苗根系对Cd有较强的滞留作用和富集能力。     

Cd、Pb投加浓度对其在黑土中化学形态分布及油菜生长和吸收Cd、Pb的影响

采用室内模拟实验和连续形态分级方法研究了Cd、Pb投加浓度对其在黑土中化学形态分布及油菜生长和吸收Cd、Pb量的影响.结果表明:随Cd、Pb投加量的增加,土壤中Cd交换态含量增幅较大,Pb碳酸盐结合态、Fe-Mn氧化物结合态含量增幅较大;外源Cd在土壤中的存在形态以交换态和残留态为主,Pb的交换态比例相对较低,其存在形态主要为残留态;土壤Cd、Pb投加浓度较低时,促进了油菜的生长,投加浓度较高时,对油菜生长的抑制作用较为明显;地下部分Cd、Pb含量远高于地上部分,与Cd相比,Pb向地上部的迁移率相对较小;土壤中Cd、Pb各形态含量与油菜地下、地上部分吸收的Cd、Pb量均呈显著正相关,与干质量呈负相关;交换态Cd、Pb对油菜干质量影响最大,碳酸盐结合态对油菜吸收Cd、Pb的贡献最大.     

水相Cd2+在南美白对虾体内的富集及氧化应激特征

为阐明水相环境中重金属镉元素(Cadmium, Cd)在甲壳类海产品中的富集与代谢过程、亚细胞微区分布特征和生物体氧化应激效应, 文章以南美白对虾(Litopenaeus vannamei)为研究对象, 应用双箱动力学模型设置了水环境下不同Cd暴露水平的富集吸收与清水净化释放试验, 实时监测南美白对虾内脏团和肌肉组织的Cd含量及谷胱甘肽巯基转移酶(Glutathione S-transferase, GST)、谷胱甘肽过氧化物酶(Glutathione peroxidase, GPx)和过氧化氢酶(Catalase, CAT)酶活力随时间变化情况, 同时结合差速离心技术分析了Cd富集后在机体内脏组织团中的亚细胞微区分布特征。实验得出南美白对虾对水环境中Cd的富集能力与水体暴露浓度呈明显的正相关关系, 内脏团组织是南美白对虾最主要的Cd元素吸收与代谢组织, 其对Cd的吸收速率、净化速率、生物富集因子及平衡状态时Cd含量均显著高于肌肉组织, 在相同暴露剂量下前者的生物富集因子平均为后者的75.5倍, 肌肉组织的Cd生物学半衰期明显长于内脏组织; Cd主要储存于类金属硫蛋白(Metallothionein-like protein, MTLP)和细胞碎片(Cell debris, CD)组分中, 少部分存在于细胞器(Organelle, ORG)、富含金属颗粒(Metal-rich granules, MRG)和热敏感蛋白(Heat sensitive protein, HSP), 且随着富集过程的持续, Cd的亚细胞微区分布发生动态变化, MTLP、ORG和HSP中Cd含量百分比逐渐升高, CD和MRG中的Cd含量百分比呈逐渐下降; 在肝脏和肌肉组织中GST、GPx和CAT酶活力在Cd富集阶段均持续显著升高, 在净化释放阶段处于下降趋势, 同一试验组下肝脏组织中抗氧化酶酶活力明显高于对应的肌肉组织。研究旨在阐述甲壳类海洋生物对环境中Cd元素的富集与分布特征, 了解Cd富集可能性机理, 为海洋甲壳类Cd污染风险评价与环境控制提供科学依据。     

镉胁迫下春小麦中镉的分布、富集及转移规律

采用盆栽试验,研究了镉胁迫下重金属镉(Cd)在春小麦中的分布、富集及转移规律。结果表明:Cd胁迫下,小麦根、茎、叶和籽粒中Cd积累量随外源Cd的增加而增加,小麦不同部位Cd积累量为根叶茎籽粒;籽粒中Cd含量与土壤中Cd显著相关;小麦不同部位对Cd的富集能力差异显著,且随外源Cd处理浓度的增加,各部位富集系数逐渐降低,低Cd浓度时各部位更易富集Cd;小麦植株地上部的转移系数亦呈递减趋势为茎、叶籽粒;在春小麦全生育期,土壤中Cd含量无明显变化,根对外源Cd的富集吸收于生育期70d左右达峰值,小麦植株中的Cd也在80d左右达到峰值后逐步减少,表明植株中的Cd,随籽粒的成熟逐步转移至籽粒。     

EGTA和酒石酸对蓖麻Cd胁迫与积累的调控作用

通过盆栽试验研究了解毒剂酒石酸与螯合剂EGTA的单施与配施对强化蓖麻修复Cd污染土壤的作用,探讨重金属污染土壤植物修复中螯合剂与解毒剂配合使用的可行性。结果显示:(1)除酒石酸单施处理外,其余处理均可显著提高土壤中醋酸提取态Cd含量,增强土壤Cd的活性,并以酒石酸与EGTA配施的效果更显好,其土壤醋酸提取态Cd含量为对照的1.41~2.49倍。(2)EGTA能有效促进Cd从蓖麻根部向地上部的转移,但高剂量EGTA处理对蓖麻根系有明显的毒害作用;EGTA与酒石酸配合施能缓解Cd对植株的毒害作用,增大蓖麻生物量和Cd积累量,其地上部Cd积累量比对照增加4.56~8.32倍。(3)蓖麻叶片Cd含量、地上部积累总量以及土壤净化率随土壤醋酸提取态Cd含量的升高而增大,并且呈良好的线性递增关系。研究表明,酒石酸与EGTA配施可通过调控土壤Cd的植物可利用性和降低Cd的生理毒性来提高蓖麻对Cd的富集能力和对Cd污染土壤的修复效果。     

高粱属植物对土壤镉吸收及亚细胞的分配

通过盆栽模拟试验研究了3种高粱属植物(甜高粱、高丹草和苏丹草)对土壤cd的富集效应及其亚细胞的分配.结果表明:cd在3种高粱属植物不同部位的富集量随着cd处理浓度的增加而增加,生育期内3种高粱属植物根系中Cd的富集量大于茎鞘和叶片中的富集量;高丹草对Cd的富集量高,甜高梁次之,苏丹草最低;Cd在高粱属植物叶片、茎鞘和根系中各亚细胞组分中的分布相似表现为细胞壁>可溶性部分>细胞核、叶绿体组分>线粒体.     

中华绒螯蟹对Pb和Cd的富集与释放特性

应用生物富集双箱动力学模型模拟了中华绒螯蟹(Eriocheir sinensis)分别在Pb浓度为0.25、0.50、0.75mg/L,Cd浓度为0.025、0.050、0.075 mg/L,的单一水环境中暴露时,蟹鳃、肝胰腺、肌肉和血淋巴对Pb和Cd的生物富集与释放实验,并通过非线性拟合得到中华绒螯蟹对Pb和Cd的富集速率常数k1、排出速率常数k2、生物富集系数BCF、生物半衰期B1/2、富集平衡时生物体内Pb和Cd含量CAmax等动力学参数.结果表明:(1)中华绒螯蟹对Pb和Cd具有明显的富集,蟹鳃、肝胰腺和肌肉中Pb和Cd的含量与富集时间和水环境中Pb和Cd暴露浓度表现出了很好的正相关,血淋巴在富集阶段没有明显的规律.理论平衡状态下鳃、肝胰腺和肌肉中Pb和Cd含量CAmax随着暴露浓度的增大而增大,且成正相关.(2)Pb和Cd在中华绒螯蟹组织器官中的富集具有选择性,开始实验前,Pb在中华绒螯蟹体内的的分布规律为:肝胰腺>鳃>肌肉>血淋巴;Cd的分布规律为:鳃>肝胰腺>血淋巴>肌肉.在实验浓度的Pb和Cd水环境中暴露16d后,Pb的分布规律为:鳃>肝胰腺>肌肉>血淋巴;Cd的分布规律为:肝胰腺>鳃>肌肉>血淋巴.(3)中华绒螯蟹对Pb和Cd的生物富集和释放都较缓慢.经过16d的生物富集,各组织器官中Pb和Cd的含量均未达到稳态平衡.Pb和Cd在组织器官中的生物富集系数(BCF)范围分别为5-51和6-3148,中华绒螯蟹对Cd的富集能力明显高于Pb(*P<0.05);Pb和Cd在中华绒赘蟹各组织器官的生物学半衰期(B1/2)范围分别为4-9d和8-57d,中华绒螯蟹对Cd的排出能力明显低于Pb.     

乐安河—鄱阳湖湿地植物群落特征及其优势植物对重金属Cu、Pb、Cd的富集

选择乐安河—鄱阳湖湿地典型植物群落,采用重要值方法评价各样点植物群落特征并筛选出典型优势植物,通过室内理化测试分析不同生境中优势植物植株及其根区土壤中重金属Cu、Pb、Cd的含量;采用生物富集系数(BCF)方法评价不同优势植物对重金属Cu、Pb、Cd的富集特性。结果表明:研究区湿地植物以草本为主,在各样点共发现124种物种,包括蕨类植物2科2属2种,种子植物40科97属122种,并从中筛选出羊蹄、红蓼、鼠曲草、紫云英、苎麻等5种富集能力较强的优势植物;植物根区土壤中的Cu、Cd含量均超过土壤环境质量三级标准,而且Cu、Cd的最高含量分别为824.03、5.03 mg·kg-1;不同优势植物对Cu、Pb、Cd等3种重金属元素中的1种或2种表现出较强的富集能力,其中优势物种红蓼对Cu具有较强的富集能力,含Cu量最高为148.80 mg·kg-1,另一种优势物种鼠曲草对三种元素的生物富集系数均较高,且对Cd的最高富集含量为15.17 mg·kg-1,对Cd的生物富集系数最高值为19.14,高于其他植物10倍以上,鼠曲草对重金属Cd具有富集植物的基本特征,且对Cu和Cd具有共富集特征并具有较高的耐性,紫云英、羊蹄等对Cd的富集能力也较强。上述5种优势植物种群对鄱阳湖湿地Cu、Pb、Cd等重金属污染物的生态修复具有一定参考价值,可作为鄱阳湖湿地重金属污染修复植物的选择对象。     

Distribution of cadmium in leaves of Thlaspi caerulescens

Knowledge of the intracellular distribution of Cd in leaves is necessary in order to understand the mechanisms of hyperaccumulation in Thlaspi caerulescens. Ganges and Prayon, two ecotypes accumulating Cd to different levels, were grown in nutrient medium containing varying concentrations (0, 5, 10, 50, and 100 microM) of Cd. Several different approaches were combined in this study to (i) validate the results obtained by a specific method and (ii) establish the link between observations and measurements performed at different scales. In both ecotypes, Cd, localized by autoradiography, was found mainly at the edges of the leaves, but also in points of higher concentration spread over the whole limb surface. This localization was clearly correlated with the necrotic spots observed on Prayon leaves. Scanning electron microscopy coupled with energy dispersive X-ray microanalysis (cryo-SEM-EDXMA) and tissue fractionation (apoplasm, cell walls, mesophyll protoplasts, and lower epidermis) showed that Cd had similar patterns of distribution in leaf cells of both ecotypes. Cadmium was found both inside the cells and in the cell walls, mainly in the large epidermal cells but also in small epidermal cells. All the methods used agreed well and the results indicated that metal storage in the plants studied involves more than one compartment and that Cd is stored principally in the less metabolically active parts of leaf cells.     

Effect of endophytic fungi on cadmium tolerance and bioaccumulation by Festuca arundinacea and Festuca pratensis

Endophytic fungi are a group of fungi that live asymptomatically inside plant tissue. These fungi may increase host plant tolerance to biotic and abiotic stresses. The effect of Neotyphodium endophytes in two grass species (Festuca arundinacea and Festuca pratensis) on cadmium (Cd) tolerance, accumulation and translocation has been our main objective. The plants were grown in a hydroponic system under different Cd concentrations (0, 5, 10, and 20 mg L(-1)) for 6 weeks. They were also grown in soil spiked with different concentrations of Cd (0, 10, 20, and 40 mg kg(-1)) for 2 months. The results from all Cd treatments showed higher biomass production (12-24%) and higher potential to accumulate Cd in roots (6-16%) and shoots (6-20%) of endophyte-infected plants than endophyte-free plants. Cadmium accumulation by plants indicated that the grasses were capable of Cd hyperaccumulation, a property that was augmented after endophyte infection. Maximum photochemical efficiency of photosystem II (Fv/Fm) revealed that Cd stress was significantly reduced in endophyte-infected plants compared to non-infected ones.     

Distribution and phytotoxicity of cadmium in tomato seedlings

Thirty-day-old seedlings of tomato (Lycopersicon esculentum cv. Kwangsoo) were treated with various cadmium (Cd) concentrations (0, 10, 50, 100, and 500 μM) for up to 20 days, and the detailed distribution of absorbed Cd and its phytotoxicity in different plant parts (root, stem, and leaves) were investigated. The accumulation of Cd in plants increased with external Cd concentrations and Cd was strongly retained by roots, with less than 30% of the absorbed Cd being transported to shoots. Among the leaves, the lower positioned older leaves accumulated more Cd than the younger leaves. Furthermore, Cd-exposure not only reduced the dry weight and length of both shoot and root, chlorophyll levels in leaves, and levels of photosynthesis, but also enhanced the concentration of malondialdehyde (a lipid peroxidation product) in all plant parts. Our results indicate that the physiological impairment of tomato seedlings exposed to toxic levels of Cd may be related to the internal distribution of absorbed Cd, prolonged exposure, and oxidative stress in different plant parts.     

水稻镉安全材料的镉吸收动力学特征

采用水培试验,以前期筛选出的水稻Cd安全材料D62B为试验材料,普通材料泸恢17为对照材料,在不同Cd浓度和时间处理下,研究水稻Cd安全材料的Cd吸收动力学特性.结果表明: 在不同Cd处理时间下,D62B根系对Cd的吸收总量均低于泸恢17,且随吸收时间的延长,差异逐渐增大.当吸收时间达到72 h,泸恢17体内积累的Cd总量为D62B的1.3倍.两种水稻材料Cd吸收动力学符合米氏方程,米氏方程常数(K_m)值差异不大,但泸恢17的最大吸收速率(V_max)是D62B的2倍.当Cd处理时间大于48 h,D62B根系对Cd的转移系数低于泸恢17,且其根部Cd分配比例明显大于泸恢17,即D62B根系对Cd的固持能力大于泸恢17.D62B的Cd吸收能力较弱,且其向地上部转移Cd的能力显著低于泸恢17.     

Accumulation and speciation of Cd in Avicennia marina tissues

Avicennia marina is a high-Cd-tolerant species in the mangrove wetlands. A hydroponic experiment was carried out to research the accumulation and chemical form distribution of Cd in the tissues of A. marina under different concentrations and durations of Cd stress. It was found that the concentrations of Cd in plant tissues followed the order of root > stem > leaf. The data suggested that root activity decreased, Cd accumulation ability weakened in roots, and the translocation factor increased in stems and leaves with the increase of stress duration. With a proactive defense mechanism, most Cd was bound to pectates, organic acids, and protein, especially in roots and stems with the most proportion of 88.51 and 78.91%, respectively, having lower biological activities. The Cd bounded to water-soluble organic acid and free inorganic aminophenol–Cd showed the lowest concentration. The pectates, organic acids, and protein-integrated Cd seem the most important in affecting Cd detoxification for A. marina; this mechanism of change in Cd biological activities decreases the toxicity of this aggressive pollutant and presents new knowledge about the tolerance of mangrove plants.     

Cadmium accumulation in relation to organic acids in leaves of Solanum nigrum L. as a newly found cadmium hyperaccumulator

The influence of various cadmium concentrations on organic acid levels in leaves of the Cd hyperaccumulator, Solanum nigrum L. and a closely related species, Solanum melongena L., were investigated. In particular, the relationship of organic acids with Cd accumulation in the two plants was investigated. The results showed that Cd accumulation in the shoots of S. nigrum was significantly higher than that of S. melongena. The accumulation of Cd in the leaves of S. nigrum ranged from 2.0 to 167.8 μg g⁻¹ dry weight (DW), but only from 1.2 to 64.0 μg g⁻¹ DW in S. melongena. Solanum melongena was considerably less tolerant to Cd than S. nigrum. Approximately 20% of the total Cd in S. nigrum leaves was water-soluble, suggesting that some accumulated Cd was associated with water-soluble compounds such as organic acids. Malic acid in the leaves of S. nigrum was the most abundant organic acid [up to 115.6–145.7 μmol g⁻¹ fresh weight (FW)], but this acid was not significantly affected by the Cd concentration in soil. However, the level of malic acid in S. melongena plants was much lower, only 16.3–75.4 μmol g⁻¹ FW. The significant positive correlations between total Cd and water-soluble Cd concentrations and both acetic and citric acid concentrations in the leaves of S. nigrum were observed. In contrast, there was no correlation between concentrations of the two acids and Cd concentrations in the leaves of S. melongena. These results indicated that acetic and citric acids in the leaves of S. nigrum might be related to its Cd hyperaccumulation.     

Organic matter influences phytotoxicity of cadmium to soybeans

Summary Soybeans (Glycine max L. var. Williams) were grown for six weeks in a greenhouse in quartz sand containing 0, 0.5, 1, 2, 4 or 8% (w/w) sterilized peat moss. The cation exchange capacities of the organic matter-sand (OM-S) mixtures ranged from 0.01 to 8.88 meq/100 g dry weight. Imposed on each OM-S mixture was a treatment of 0, 1.25, 2.5, 5.0, 10.0 or 20.0 ppm Cd applied as CdCl₂·21/2H₂O. Height growth was measured weekly and at harvest plants were separated into leaves, stems and roots for dry weight and tissue Cd determinations. For plants grown in sand alone, height growth and dry matter accumulation in all tissues were reduced and Cd content was increased. These effects were correlated with increasing Cd concentration in the rooting medium. Inhibitions in growth by Cd were reduced by addition of organic matter; the amount of alleviation was dependent on both the level of organic matter and the cadmium treatment. In the 0, 0.5 and 1% OM-S mixtures, Cd content in the various tissues was correlated with metal treatment. Tissue levels were markedly reduced for Cd treatments in the 2, 4 and 8% OM-S mixtures, although there was a positive correlation between tissue Cd and the 1.25 and 2.5 Cd treatments. The order of Cd accumulation in the tissues was roots stems>leaves.     

Cellular sequestration of cadmium in the hyperaccumulator plant species Sedum alfredii

Spatial imaging of cadmium (Cd) in the hyperaccumulator Sedum alfredii was investigated in vivo by laser ablation inductively coupled plasma mass spectrometry and x-ray microfluorescence imaging. Preferential Cd accumulation in the pith and cortex was observed in stems of the Cd hyperaccumulating ecotype (HE), whereas Cd was restricted to the vascular bundles in its contrasting nonhyperaccumulating ecotype. Cd concentrations of up to 15,000 μg g(-1) were measured in the pith cells, which was many fold higher than the concentrations in the stem epidermis and vascular bundles in the HE plants. In the leaves of the HE, Cd was mainly localized to the mesophyll and vascular cells rather than the epidermis. The distribution pattern of Cd in both stems and leaves of the HE was very similar to calcium but not zinc, irrespective of Cd exposure levels. Extended x-ray absorption fine structure spectroscopy analysis showed that Cd in the stems and leaves of the HE was mainly associated with oxygen ligands, and a larger proportion (about 70% in leaves and 47% in stems) of Cd was bound with malic acid, which was the major organic acid in the shoots of the plants. These results indicate that a majority of Cd in HE accumulates in the parenchyma cells, especially in stems, and is likely associated with calcium pathways and bound with organic acid (malate), which is indicative of a critical role of vacuolar sequestration of Cd in the HE S. alfredii.     

A comparison of dressed crab and a cadmium salt (CdCl2) as cadmium sources in rat diets

1. A long term low level exposure experiment was conducted on rats in order to determine the metabolic patterns of realistic environmental dietary levels of cadmium from different sources. 2. Male and female rats were fed a diet for 6 months with a high crab content containing 4 mg Cd/kg as organic bound cadmium from dressed crab, a diet with low crab content containing 0.2 mg Cd/kg as organic bound cadmium, a casein based diet containing 4 mg Cd/kg as cadmium chloride and a low cadmium level control diet. 3. Analysis of the cadmium levels in the kidney, liver and spleen showed that uptake from the dressed crab was only half of that from the diet fortified with cadmium chloride.     

镉在互花米草中积累、转运及亚细胞的分布

研究了在不同Cd浓度(0、5、100、200μg·g-1)处理下,互花米草花序、叶、茎、根茎、须根中Cd含量、积累量、转运特征,及Cd在互花米草体内的亚细胞分布。结果表明,Cd在互花米草不同器官中的积累能力存在较大差异。茎、根茎、须根中Cd含量及积累量随处理浓度的增加而升高,其中须根中Cd含量及积累量均高于其他器官。Cd处理浓度为100gμ·g-1时,花序和叶中Cd含量达到最大值,分别为8.65和7.82μg·g-1。在Cd处理浓度为200μg·g-1时,须根中Cd含量可高达390.00μg·g-1,积累量达3200μg·株-1。Cd在互花米草体内转运能力极低,绝大部分Cd积累在地下部位。Cd在互花米草亚细胞中的分布规律为细胞壁>胞液>细胞器。随着Cd处理浓度的增加,Cd在细胞壁中的分配比例增大,胞液中Cd分布比例则相应减小,细胞壁和胞液相互协调,增强互花米草对重金属Cd的耐性。