镉在土壤-金丝垂柳系统中的迁移特征

以金丝垂柳为试验对象,采用盆栽试验方式,设置无植物和金丝垂柳两组试验,分别对两组试验的土壤做梯度浓度Cd处理:0(无镉处理)、2(低浓度处理)、20(中浓度处理)、80(高浓度处理) mg/kg 土壤干重,无植物组各处理分别定义为CK(无镉处理)、L(低浓度处理)、M(中浓度处理)、H(高浓度处理),金丝垂柳组各处理分别定义为CKP(无镉处理)、LP(低浓度处理)、MP(中浓度处理)、HP(高浓度处理)。通过对土壤中各形态Cd含量及金丝垂柳叶、韧皮部、木质部、根部的Cd含量测定,分析了金丝垂柳及不同浓度Cd处理对土壤中中性交换态、螯合态和残渣态Cd含量的影响,并评价了富集指数(BCF)、转移系数(TF)和生物有效性(BF),明确了Cd在土壤-金丝垂柳系统中的转移特征及金丝垂柳对土壤中Cd的清除效果。结果表明:(1)金丝垂柳对土壤中中性交换态、有效态Cd含量及总Cd量的降低具有极显著影响,HP组与无植物H组相比,中性交换态及有效态Cd含量分别降低了52.73%、25.34%,MP、HP组与对应的无植物处理组的总Cd量相比分别降低了11.33%、13.89%;(2)金丝垂柳各处理组的Cd积累量随Cd处理浓度的增加和处理时间的延长而增加,处理90 d后,HP处理中木质部和根部的Cd含量可达170.64 mg/kg、212.49 mg/kg;(3)各浓度Cd处理下,金丝垂柳各部位生物富集系数呈根>木质部>韧皮部、叶,且随着Cd处理浓度的增加而显著降低,随处理时间的延长而升高;与40 d相比,90 d时LP组叶的生物富集系数增加了6.90倍,增幅最大。(4)各部分转移系数均随处理时间的延长而降低,90 d时LP、MP的转移系数分别比40 d时的结果低47.94%、41.34%。(5)金丝垂柳LP、HP组土壤Cd的生物有效性显著低于相应的无植物处理L、H组,分别低70.73%、88.46%,MP组与M组无显著差异。研究结果表明,金丝垂柳能有效地吸收土壤中的有效态Cd,降低土壤中Cd的生物有效性及总Cd量,提高土壤的安全性,并能将吸收的Cd有效地转移至地上部分,尤其是木质部储存。随着植株不断生长,生物量的增加,金丝垂柳可有效地清除土壤中的Cd,适用于对Cd污染地区进行长期植物修复。     

N、P、K肥对香根草修复土壤镉、锌污染效率的影响

通过盆栽试验研究在30 mg/kg镉(Cd)污染土壤条件下N[CO(NH2)2:100、200、300 mg/kg土]、P(P2O5:50、100、200 mg/kg土)和K(KCl:100、200、300 mg/kg土)处理对香根草修复土壤Cd和锌(Zn)污染效率的影响。结果表明:3种N处理能促进香根草地上部生长,而且显著提高地上部特别是叶的Cd和Zn含量,导致其修复效率成倍显著增加;200 mg/kg K处理显著提高Zn修复效率,但300 mg/kg K和50、200 mg/kg P处理却显著降低Cd、Zn修复效率。因此,为改善香根草对较贫瘠土壤中Cd、Zn污染的修复效率,应对香根草适施N肥,并控制或者不施P、K肥为佳。     

Cd、低Pb/Cd下冬小麦幼苗根系分泌物酚酸、 糖类及与根际土壤微生物活性的关系

采用土壤盆栽试验法研究了Cd、低于国家“土壤环境质量标准”规定的Ⅱ类土壤环境基准值300 mg/kg干土时的Pb与Cd复合处理对冬小麦幼苗根系分泌物总酚酸和简单糖类及其与根际土壤微生物活性关系的影响特征.结果表明:1)冬小麦幼苗生长3周时,随Cd浓度的升高,根系简单糖类的分泌量表现为降低-增加-降低现象,而酚酸分泌量主要表现为显著(P＜0.05)增加;幼苗生长7周时,简单糖类分泌量极显著(P＜0.01)降低,酚酸分泌量表现为降低-增加-降低现象;幼苗生长12周时,简单糖类分泌量在Cd≤50.00 mg/kg干土时降低,Cd浓度为70.00 mg/kg干土时极显著(P＜0.01)增加,酚酸分泌量在Cd≤20.00mg/kg干土时降低,Cd＞20.00 mg/kg干土时增加.2)低于国家“土壤环境质量标准(GB15618-1995)”规定的Ⅱ类土壤环境基准值(300 mg/kg)时,Pb的存在会对Cd胁迫下冬小麦根系酚酸和简单糖类分泌特征有明显影响,主要表现为可使Cd处理下幼苗根系酚酸分泌量增加,而简单糖类分泌量降低.3)低Pb/Cd处理与Cd处理之间,冬小麦幼苗根系酚酸和简单糖类分泌量与细菌、真菌和放线菌数量、脲酶、转化酶和脱氢酶活性、有机质和全氮含量、微生物量碳等根际土壤微生物生化活性之间的相关性特点明显不同.     

水淹生境下秋华柳对镉污染土壤的修复能力

以耐水淹和耐重金属的秋华柳(Salix variegata)作为试验材料,从土壤角度出发,探究秋华柳在水淹条件下对镉污染土壤的修复能力。设置无植物和种植秋华柳两个处理组,分别对两组设置两个水分处理组:正常供水组(CK)及土壤水淹组(FL),4个镉浓度处理组:对照组(0 mg/kg)、低浓度(0.5 mg/kg)、中浓度(2 mg/kg)及高浓度(10 mg/kg)。分别于处理后的第30天和第60天对各处理组的土壤和水淹组水样进行取样。试验结果表明:(1)镉处理浓度越高,土壤中镉活性态浓度越高,生物毒性越强。(2)水淹显著降低土壤活性态Cd浓度(P0.05),增大土壤修复难度。(3)种植秋华柳对30d土壤Cd全量及各形态镉浓度均无显著影响(P0.05);对第60天正常供水和水淹组土壤中交换态、碳酸盐结合态的镉浓度以及60d水淹组土壤Cd全量均有显著影响(P0.05)。(4)秋华柳种植显著降低土壤Cd迁移系数,30d正常供水组、水淹组以及60d正常供水组和水淹组平均降幅分别为2.0%、4.12%、9.71%、9.32%。处理时间过短和试验用苗生物量小可能是秋华柳对土壤全量Cd影响不大的主要原因,但秋华柳均显著降低正常供水和水淹组土壤迁移系数且二组降幅差异不大。研究表明:水淹生境下,秋华柳对Cd污染的土壤仍有较好的修复能力。     

德国鸢尾对Cd胁迫的生理生态响应及积累特性

通过盆栽研究了Cd胁迫下德国鸢尾的生长状况、生态效应、生理特性及吸收和富集Cd的能力.结果表明:德国鸢尾对小于5 mg/kg的Cd有较强的耐性,适用于城区土壤修复;Cd浓度大于5 mg/kg时抑制德国鸢尾生长,降低了其生态效应.随着Cd浓度的增大,德国鸢尾根系活力、叶绿素含量和含水量逐渐降低,游离脯氨酸和可溶性糖含量先升高后降低,细胞膜透性逐渐升高.Cd在德国鸢尾体内分布为根系＞地上部分,随着Cd浓度的增大,德国鸢尾根系和地上部分Cd积累浓度逐渐升高、富集系数和转运系数逐渐降低;Cd浓度为20 mg/kg时德国鸢尾对Cd的积累量最大,为2.122 mg/plant.     

香根草对镉毒害的生理响应——采用傅里叶变换红外光谱法(FTIR)

为阐明香根草(Vetiveria zizanioides)对镉(Cd~(2+))胁迫的耐性机理及其对重金属Cd~(2+)的积累特征,通过水培试验,采用傅里叶变换红外光谱法(FTIR)研究在不同Cd~(2+)浓度处理时香根草根、茎、叶化学组分的变化,同时测定香根草叶Cd~(2+)的亚细胞分布和其重金属Cd~(2+)含量。结果表明,其根组织在2927 cm~(-1)处峰高先下降后上升,表明在低Cd~(2+)(Cd~(2+)3 mg/L)处理条件下香根草分泌的有机酸不断螯合Cd~(2+),造成羧酸O—H的减少,但随着Cd~(2+)含量的升高,其羧酸螯合力变弱,有机酸含量渐渐升高;茎组织在1631 cm~(-1)峰高处先上升后下降,表明在低Cd~(2+)(Cd~(2+)3 mg/L)处理条件下香根草产生氨基酸、多肽和蛋白质等物质,通过渗透调节来增强抗逆性,但随着Cd~(2+)含量的升高,蛋白质二级结构中肽键间氢键的结合力受影响较大。当Cd~(2+)处理浓度为7 mg/L时,香根草生长10 d后,地上部分及根组织富集Cd~(2+)量分别高达212.49 mg/kg和290.59 mg/kg。香根草地上部分的Cd~(2+)含量随Cd~(2+)处理浓度的增加而增加。香根草叶片富集的Cd~(2+)主要分布于细胞质中,其次为细胞壁,而在线粒体和叶绿体中含量最低。     

pH值和Fe、Cd处理对水稻根际及根表Fe、Cd吸附行为的影响

通过营养液-蛭石联合培养试验,设置系列pH值(4.5—7.5)和Fe、Cd处理,研究不同pH值及Fe、Cd浓度对水稻和蛭石表面Fe、Cd吸附的影响。结果表明,不同pH值处理下的根际氧化还原电位和酸度不同,0.9 mg/L Cd处理下的根际氧化势低于0.5 mg/L Cd,50 mg/L Fe处理下的根际酸度高于30 mg/L Fe处理。根表吸附Fe、Cd组分和数量都受根际Eh、pH值制约,根表Fe、Cd吸附量在处理pH值6.0时最低,并分别在处理pH值7.5和处理pH值4.5达到最高。但根系表面对Fe、Cd的吸附机制与蛭石表面不同,蛭石吸附Fe主要为晶态Fe,占到总沉积Fe的73%—87%;水稻根表沉积Fe以非晶态Fe为主,占总沉积Fe的91%—95%;与处理pH值和根际Eh间有显著的相关性(蛭石晶态Fe:ppH=0.011、pEh=0.042;水稻根表非晶态Fe:ppH=0.050、pEh=0.004)。蛭石表面交换态Fe及交换态Cd与处理pH值和Eh间存在显著的相关性(pH值:pFe<0.001、pCd=0.009;Eh:pFe=0.016、pCd=0.002),而根表交换态Fe及交换态Cd仅与处理pH值间有显著的相关性(pFe=0.007,pCd=0.048)。不同Fe、Cd浓度处理对根际Eh、pH值的升降和根表Fe、Cd吸附均有影响。与对照相比,增Cd处理可以降低根际Eh和升高pH值,减少溶液Cd浓度并增加根表Cd吸附量;增Fe处理则可以升高根际Eh和降低pH值,增加溶液Fe、Cd浓度并减少根表Fe、Cd吸附量。这是水稻应对Fe、Cd浓度胁迫的生理反应之一。     

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。     

秋华柳和枫杨幼苗对镉的积累和耐受性

以秋华柳和枫杨当年实生幼苗为研究对象,采用向土壤添加外源镉(CdCl₂ · 2.5H₂O)的形式设置了0(对照组)、10 、20 、50、100 mg/kg 5个处理,研究了镉胁迫下秋华柳和枫杨幼苗的生长、生物量变化和根茎叶镉含量,并评价了两树种的耐性指数(Ti)、转移系数(Tf)和生物富集系数(BCF)。结果表明:(1)在镉含量为10 mg/kg时,秋华柳和枫杨幼苗基于生长和生物量参数的耐性指数(Ti)分别为91.72和91.62,与对照组相比无显著变化,其余各组(20、50、100 mg/kg)则显著低于对照植株(P<0.05);(2) 土壤镉浓度小于20mg/kg时,秋华柳植株茎、叶镉积累量分别高达61.73 mg/kg、163.04 mg/kg,根镉积累量为91.05 mg/kg;枫杨植株茎、叶镉积累量最高分别为7.9 mg/kg、5.25 mg/kg,仅为秋华柳茎、叶的12.8%和3.2%,根镉积累量高达190.68 mg/kg;(3) 除对照外,秋华柳幼苗各部分镉含量为叶＞根＞茎,转移系数(Tf)介于0.789-1.513之间,枫杨幼苗各部分镉含量为根＞茎＞叶,转移系数(Tf)介于0.037-0.044之间,远远小于秋华柳Tf;(4)秋华柳和枫杨幼苗在土壤镉浓度为10 mg/kg时具有很高的生长适应性和耐性,秋华柳根吸收的镉向地上部分转移能力、地上部分积累镉的能力都远远大于枫杨,生物富集系数(BCF)进一步证实了这一特性。研究证明,秋华柳植株具有很高的镉耐性、镉转移能力及地上部分积累镉的能力,适合于镉污染严重区域的植物修复。     

鬼针草(Bidens pilosa L.)对镉污染农田的修复潜力

为探究富集植物鬼针草对镉(Cd)污染农田土壤的修复潜力,通过野外调查,原土盆栽试验和田间试验,测定鬼针草及其根系土壤Cd含量,计算鬼针草的富集系数和去除率。结果表明,野外调查中不同铅锌矿区生长的鬼针草叶片中Cd含量最大值为53.3 mg/kg。盆栽试验中,低浓度Cd土壤处理(T1),鬼针草地上部Cd的富集系数为4.70,转运系数1.59,大于1。高浓度Cd土壤处理(T2 13.4 mg/kg),其地上部Cd积累量达到43.1 mg/kg,其地上部Cd富集系数为3.51。鬼针草对Cd表现出稳定的积累特性。田间试验小区中,土壤Cd含量均值为2.66 mg/kg,鬼针草中地上部Cd含量均值为10.9 mg/kg,富集系数为4.16,使用鬼针草修复Cd污染土壤每公顷地种植一茬鬼针草的去除率为4.3%—6.2%。使用富集植物鬼针草修复农田Cd污染具有较好的工程应用前景。     

The Optimal Root Length for Vetiveria zizanioides When Transplanted to Cd Polluted Soil

In order to facilitate transportation and accelerate growth, roots of Vetiveria zizanioides must be pruned before transplanting. The present research is aimed to investigate the best root length for vetiver grown in cadmium (Cd) polluted soil. The results indicated that 6 cm root-length plant (RLP) was the best candidate in phytoremediation of Cd-contaminated soil for its stronger tolerance and better growth promoting activities.     

Evidence for separate translocation pathways in determining cadmium accumulation in grain and aerial plant parts in rice

Background  

Cadmium (Cd) translocation and accumulation in the grain and aerial plant parts of rice (Oryza sativa L.) is an important aspect of food safety and phytoextraction in areas with contaminated soil. Because control of Cd translocation and accumulation is likely to be determined by the plants genetics, the Cd contents of grain and the aerial parts of rice may be manipulated to improve food safety and for phytoextraction ability. This study studied Cd translocation and accumulation and their genetic control in aerial parts of rice to provide a starting point for improving food safety and phytoextraction in Cd-contaminated soils.     

Soil Nitrogen Fertilization Effects on Phytoextraction of Cadmium and Lead by Tobacco (Nicotiana tabacum L.)

A greenhouse experiment using 24 plastic pots filled with 6 kg of Pb- and Cd-contaminated soil was carried out. In all 24 pots, soils were heavy metal–contaminated with 10 mg Cd kg^?1 soil and 500 mg of Pb kg^?1 soil by using CdCl and PbNO₃. Two-month-old tobacco (Nicotiana tabacum L.) plants were used to extract these heavy metals. Results showed that tobacco is able to remove Cd and Pb from contaminated soils and concentrate them in its harvestable part, that is, it could be very useful in phytoextraction of these heavy metals. Increasing additions of ammonium nitrate to soil (50, 100, and 150 mg N kg^?1 soil) significantly (p ≤ .05) increased aboveground Cd and Pb accumulation during a 50-day experimental period, whereas increasing additions of urea to soil (50 and 100 mg N kg^?1 soil) did not show these effects at the same significance levels. Increasing additions of ammonium nitrate to soil shows as dry matter increases, both accumulated Cd and accumulated Pb also increase when tobacco plants are growing under Pb- and Cd-contaminated soil conditions. Higher Pb concentrations depress Cd/Pb ratios for concentrations and accumulations, suggesting that Pb negatively affects Cd concentration and/or accumulation.     

Evaluation of three herbaceous index plant species for bioavailability of soil cadmium, chromium, nickel and vanadium

Uncultivated plants growing on disturbed sites may be useful for assessing the bioavailability of some metals in soils, and thus the potential for metal mobilization up the terrestrial food chain, an important element in ecological risk assessment. A planted chicory cultivar (Cichorium intybus L. var. foliosum Hegi.) and the uncultivated plants horseweed (Canada fleabane) (Erigeron canadensis L.) and dogfennel (Eupatorium capillifolium (Lam.) Small) were evaluated for their ability to act as index plant species for soil Cd, Cr, Ni, and V at two field sites where these metals had been applied five yr previously to two highly weathered sandy Ultisols. Soil Cd was available to all analyzed plant tissues of all three plant species at both sites, particularly on the sandier Blanton soil. Chicory was an effective index plant for Cd on the finer textured Orangeburg soil but functioned as an indicator plant (toxicity symptoms were observed) on the sandier Blanton soil. Horseweed and dogfennel were effective index plants for Cd in both contaminated soils. Soil Cr, Ni, and V were less bioavailable than soil Cd and plant metal uptake was more sensitive to residual soil Cr, Ni, and V than was soil extraction with double acid. Horseweed and chicory may have potential as index plants for soil Cr. Chicory may have potential as a Ni index plant. Chicory and dogfennel may have potential as V index plants.     

Uptake and Bioaccumulation of Pentachlorophenol by Emergent Wetland Plant Phragmites australis (Common Reed) in Cadmium Co-contaminated Soil

Despite many studies on phytoremediation of soils contaminated with either heavy metals or organics, little information is available on the effectiveness of phytoremediation of co-occurring metal and organic pollutants especially by using wetland species. Phragmites australis is a common wetland plant and its potential for phytoremediation of cadmium pentachlorophenol (Cd-PCP) co-contaminated soil was investigated. A greenhouse study was executed to elucidate the effects of Cd (0, 10, and 20 mg kg^?1) without or with PCP (0, 50, and 250 mg kg^?1) on the growth of the wetland plant P. australis and its uptake, accumulation and removal of pollutant from soils. After 75 days, plant biomass was significantly influenced by interaction of Cd and PCP and the effect of Cd on plant growth being stronger than that of PCP. Coexistence of PCP at low level lessened Cd toxicity to plants, resulting in improved plant growth and increased Cd accumulation in plant tissues. The dissipation of PCP in soils was significantly influenced by interactions of Cd, PCP and plant presence or absence. As an evaluation of soil biological activities after remediation soil enzyme was measured.     

Assessing the potential for zinc and cadmium phytoremediation with the hyperaccumulator Thlaspi caerulescens

Thlaspi caerulescens is a Zn and Cd hyperaccumulator, and has been tested for its phytoremediation potential. In this paper we examine the relationships between the concentrations of Zn and Cd in soil and in T. caerulescens shoots, and calculate the rates of Zn and Cd extraction from soil. Using published data from field surveys, field and pot experiments, we show that the concentrations of Zn and Cd in the shoots correlate with the concentrations of Zn and Cd in soils in a log-linear fashion over three orders of magnitude. There is little systematic difference between different populations of T. caerulescens in the relationship between soil and plant Zn concentrations. In contrast, populations from southern France are far superior to those from other regions in Cd accumulation. Bioaccumulation factors (plant to soil concentration ratio) for Zn and Cd decrease log-linearly with soil metal concentration. Model calculations show that phytoremediation using T. caerulescens is feasible when soil is only moderately contaminated with Zn and Cd, and the phytoremediation potential is better for Cd than for Zn if the populations from southern France are used. Recent progress in the understanding of the mechanisms of Zn and Cd uptake by T. caerulescens is also reviewed.     

水淹生境下秋华柳对镉污染土壤研究修复能力

以耐水淹和耐重金属的秋华柳（Salix variegata）作为试验材料,从土壤角度出发,探究秋华柳在水淹条件下对镉污染土壤的修复能力。设置无植物和种植秋华柳两个处理组,分别对两组设置两个水分处理组：正常供水组（CK）及土壤水淹组（FL）,4个镉浓度处理组：对照组（0 mg/kg）、低浓度（0.5 mg/kg）、中浓度（2 mg/kg）及高浓度（10 mg/kg）。分别于处理后的第30天和第60天对各处理组的土壤和水淹组水样进行取样。试验结果表明：（1）镉处理浓度越高,土壤中镉活性态浓度越高,生物毒性越强。（2）水淹显著降低土壤活性态Cd浓度（P < 0.05）,增大土壤修复难度。（3）种植秋华柳对30d土壤Cd全量及各形态镉浓度均无显著影响（P > 0.05）;对第60天正常供水和水淹组土壤中交换态、碳酸盐结合态的镉浓度以及60d水淹组土壤Cd全量均有显著影响（P < 0.05）。（4）秋华柳种植显著降低土壤Cd迁移系数,30d正常供水组、水淹组以及60d正常供水组和水淹组平均降幅分别为2.0%、4.12%、9.71%、9.32%。处理时间过短和试验用苗生物量小可能是秋华柳对土壤全量Cd影响不大的主要原因,但秋华柳均显著降低正常供水和水淹组土壤迁移系数且二组降幅差异不大。研究表明：水淹生境下,秋华柳对Cd污染的土壤仍有较好的修复能力。     

贵州牛角塘铅锌矿区优势植物的重金属富集特征

为筛选适合贵州喀斯特地区重金属污染土壤修复治理以及矿区生态复垦的植物材料,该研究在贵州牛角塘铅锌矿区采集30种优势植物及其根系土壤,测定其地上部、地下部和根系土壤的Cd、Cu、Ni、Pb、Zn含量,计算植物对重金属的富集和转运系数,并通过聚类分析综合评估植物的应用潜力.结果表明:(1)千里光、鬼针草地上部Cd含量高达4...     

Native rhizobia from Zn mining soil promote the growth of Leucaena leucocephala on contaminated soil

Plants on contaminated mining soils often show a reduced growth due to nutrient depletion as well as trace elements (TEs) toxicity. Since those conditions threat plant's survival, plant growth-promoting rhizobacteria (PGPRs), such as rhizobia, might be of crucial importance for plant colonization on TE-contaminated soils. Native rhizobia from mining soils are promising candidates for bioaugmented phytoremediation of those soils as they are adapted to the specific conditions. In this work, rhizobia from Zn- and Cd-contaminated mining soils were in vitro screened for their PGP features [organic acids, indole-3-acetic acid (IAA), and siderophore (SID) production; 1-aminocyclopropane-1-carboxylate (ACC) deaminase activity; and Ca₃(PO₄)₂ solubilization] and Zn and Cd tolerance. In addition, some type and reference rhizobia strains were included in the study as well. The in vitro screening indicated that rhizobia and other native genera have great potential for phytoremediation purposes, by exerting, besides biological N₂ fixation, other plant growth-promoting traits. Leucaena leucocephala–Mesorhizobium sp. (UFLA 01-765) showed multielement tolerance and an efficient symbiosis on contaminated soil, decreasing the activities of antioxidative enzymes in shoots. This symbiosis is a promising combination for phytostabilization.     

水淹生境下秋华柳对Cd污染土壤微生物数量及酶活性的影响

三峡库区消落带面临水淹及Cd污染双重胁迫,为探究秋华柳(Salix variegata Franch.)在水淹条件下对Cd污染土壤的修复能力,以秋华柳扦插苗为试验材料,设置正常供水(CK)和水淹组(FL)两个水分处理方式,4个Cd浓度梯度:对照组(0mg/kg)、低浓度(0.5mg/kg)、中浓度(2mg/kg)及高浓度(10mg/kg),分别对处理60 d和120 d的土壤微生物数量及酶活性变化特征进行研究。试验结果表明:(1)Cd浓度处理均未显著影响土壤微生物数量(P0.05),水淹显著降低处理60 d土壤细菌数、真菌数及处理120 d的土壤放线菌数及真菌数(P0.05)。(2)种植秋华柳显著提高处理60 d土壤细菌数量(P0.05),对土壤放线菌、真菌数量也有一定提升。(3)Cd浓度处理显著影响处理60 d土壤磷酸酶活性及处理120 d脲酶活性(P0.05),水淹显著降低处理60 d土壤磷酸酶活性及处理120 d脲酶、蔗糖酶和磷酸酶活性(P0.05)。(4)正常供水及水淹条件下,种植秋华柳对土壤酶活均有一定改善作用。种植秋华柳显著提高了处理60 d土壤磷酸酶活性以及处理120 d脲酶和蔗糖酶活性(P0.05)。研究结果表明:水淹生境中,秋华柳对Cd污染土壤微生物数量及酶活性具有改善作用,在Cd污染土壤修复方面有一定应用前景。