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。     

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。     

Na2CO3胁迫下甜菜幼苗根际土壤环境因子的变化及其相关性

以两个甜菜品种‘KWS0143’(耐盐碱性强)和‘Beta464’(耐盐碱性较弱)为对象,设置4个Na₂CO₃浓度处理[占土壤质量的0%(CK)、0.4%、0.8%和1.2%],采用盆栽方法研究甜菜幼苗时期植株干质量、根际土壤酶活性和微生物数量的变化.结果表明: 与对照相比,0.4%处理的植株干质量明显增加,而0.8%和1.2%处理显著受到抑制,且处理间差异显著. 不同处理下甜菜幼苗根际土壤脲酶、过氧化氢酶和碱性磷酸酶活性表现出相似的变化规律,0.4%处理酶活性较对照有所增加但不显著;0.8%和1.2%处理则显著降低了酶活性,同时‘KWS0143’的土壤酶活性均高于‘Beta464’.与对照相比,0.4%处理土壤微生物群落没有显著变化;0.8%和1.2%处理的根际土壤细菌、真菌和放线菌数量显著减少,且‘KWS0143’的根际微生物数量高于‘Beta464’.两品种植株干质量、土壤酶和土壤微生物之间呈显著正相关;通径分析表明,‘KWS0143’植株干质量决定系数表现为:放线菌>细菌>过氧化氢酶>脲酶>真菌>碱性磷酸酶,‘Beta464’表现为:放线菌>过氧化氢酶>脲酶>真菌>碱性磷酸酶>细菌.     

乌兰布和沙漠东北部沙区人工林土壤微生物及酶活性研究

以荒漠为对照,对乌兰布和沙漠东北部沙区9种人工林0～20 cm和20～40 cm土层的3大类微生物(细菌、放线菌和真菌)及4种酶活性(蔗糖酶、脲酶、过氧化氢和碱性磷酸酶)的生态分布特征进行了研究.结果表明:(1)各林地三大菌数量级均表现为细菌(106)＞放线菌(105)＞真菌(103);在0～40 cm垂直剖面内,细菌数在柠条、沙枣和沙棘林地中较多,两白杨林地中放线菌数量最多,真菌数在花棒和柠条林地中较多,微生物总数整体表现为灌木林地多于乔木林地;随土层加深各林地土壤微生物总数量均呈明显减少趋势.(2)在0～40 cm土层中,两白杨林地蔗糖酶活性最高,小美旱林地脲酶活性和过氧化氢酶活性均较高,沙棘和沙枣林地碱性磷酸酶活性较高;土壤酶活性具有明显垂直分异特征,除过氧化氢酶外其余几种酶活性均随土层深度增加而递减,其中脲酶活性降幅最大.(3)4种土壤酶活性间整体正相关性较好,土壤放线菌数量与其蔗糖酶、脲酶和过氧化氢酶活性呈显著正相关.可见,人工乔、灌林地的土壤微生物数量比荒漠地增加,酶活性增强,土壤生物学性质得到改善;不同林地土壤微生物组成、数量、分布和土壤酶活性存在差异.     

秸秆和生草覆盖对桃园土壤养分含量、微生物数量及土壤酶活性的影响

以秸秆(覆盖重量分别为小麦(Triticum aestivum)秸3.25 kg·m^-2、玉米(Zea mays)秸1.97 kg·m^-2、禾本科杂草3.67 kg·m^-2)和生草(白三叶草(Trifolium repens)、高羊茅(Festuca arundincea)和紫花苜蓿(Medicago sativa), 播种量均为50 kg·hm^-2)为覆盖材料, 以不覆盖为对照, 研究了不同覆盖材料对桃园土壤微生物数量和酶活性的影响, 及其与土壤养分的关系。结果表明, 与对照相比, 除覆盖生草根际和非根际土壤全磷和速效磷含量差异均不显著外, 其他处理根际和非根际土壤碱解氮、速效钾、全氮、全钾和有机质含量差异均达到显著水平; 所有处理根际和非根际土壤氨化细菌、真菌和放线菌数量、土壤含水率和pH值、土壤脲酶和磷酸酶活性差异均达到显著水平。白三叶草处理的根际和非根际土壤碱解氮、速效钾、全氮、全钾、有机质含量, 土壤氨化细菌和真菌数量, 土壤脲酶和磷酸酶活性的平均升幅均最高, 分别为99%、270%、267%、117%、272%、158%、141%、156%和64%。氨化细菌、真菌、放线菌、脲酶和磷酸酶分别与土壤碱解氮、速效钾(放线菌和磷酸酶除外)、全氮、全钾和有机质呈显著或极显著的正相关。通径分析表明, 在3种土壤微生物和2种酶对养分含量的影响中, 脲酶是影响土壤碱解氮、速效钾、全氮、全钾和有机质的主要因子。     

Na2CO3胁迫下甜菜幼苗根际土壤环境因子的变化及其相关性

以两个甜菜品种‘KWS0143’(耐盐碱性强)和‘Beta464’(耐盐碱性较弱)为对象,设置4个Na₂CO₃浓度处理[占土壤质量的0%(CK)、0.4%、0.8%和1.2%],采用盆栽方法研究甜菜幼苗时期植株干质量、根际土壤酶活性和微生物数量的变化.结果表明: 与对照相比,0.4%处理的植株干质量明显增加,而0.8%和1.2%处理显著受到抑制,且处理间差异显著. 不同处理下甜菜幼苗根际土壤脲酶、过氧化氢酶和碱性磷酸酶活性表现出相似的变化规律,0.4%处理酶活性较对照有所增加但不显著;0.8%和1.2%处理则显著降低了酶活性,同时‘KWS0143’的土壤酶活性均高于‘Beta464’.与对照相比,0.4%处理土壤微生物群落没有显著变化;0.8%和1.2%处理的根际土壤细菌、真菌和放线菌数量显著减少,且‘KWS0143’的根际微生物数量高于‘Beta464’.两品种植株干质量、土壤酶和土壤微生物之间呈显著正相关;通径分析表明,‘KWS0143’植株干质量决定系数表现为:放线菌>细菌>过氧化氢酶>脲酶>真菌>碱性磷酸酶,‘Beta464’表现为:放线菌>过氧化氢酶>脲酶>真菌>碱性磷酸酶>细菌.     

短期施肥对羊草草甸割草场土壤微生物的影响

以呼伦贝尔羊草草甸天然割草场为研究对象,从土壤微生物数量、微生物生物量和酶活性等指标,探讨土壤微生物对短期施肥的响应及指标间的关系。结果表明,施肥显著地增加了土壤真菌数量,随着施肥水平增加,真菌和放线菌数量均有增大的趋势,而细菌数量逐渐减小。施肥显著增加了土壤微生物生物量碳和微生物熵,而对微生物生物量氮、土壤蔗糖酶、脲酶和过氧化氢酶无显著性影响。施肥后土壤真菌数量与微生物生物量碳呈极显著正相关,细菌与放线菌呈显著正相关。低水平处理(N 3.5 g·m~(-2)+P 1.7 g·m~(-2))比较适合土壤微生物的繁殖。施肥后草地土壤微生物之间关系密切。微生物数量对短期施肥的响应最为敏感,其次为酶活性和微生物生物量;其中,真菌的响应程度最高。     

外来入侵植物意大利苍耳对土壤微生物群落、土壤酶活性和土壤养分的影响

研究了不同浓度的意大利苍耳水提液(0.025, 0.1 g·mL–1)对入侵地土壤微生物群落结构、土壤酶活性和土壤养分的影响。结果表明, 意大利苍耳水提液处理使土壤中细菌数量显著增加, 真菌数量总体上呈增加趋势, 而放线菌的数量则一直低于对照(蒸馏水处理)。Biolog 分析结果显示, 不同处理下土壤的平均颜色变化率(AWCD)均显著低于对照; 对单一碳源的研究发现, 各处理下土壤微生物的主要碳源为聚合物和酚酸。水提液处理显著增加了土壤速效氮和速效钾的含量, 并且增加了土壤脲酶和蔗糖酶的活性。相关性分析表明, 土壤脲酶活性与土壤蔗糖酶活性及细菌数量三者之间呈正相关, 而土壤脲酶活性与放线菌数量呈负相关; 土壤有机质与土壤脲酶、土壤蔗糖酶和细菌数量呈正相关, 速效氮、速效钾与土壤脲酶、土壤蔗糖酶和真菌数量呈正相关。以上研究结果表明, 意大利苍耳水提液可以改变土壤微生物群落结构、土壤酶活性和土壤养分, 从而使其更加有利于自身的生长和扩张。     

洞庭湖退田还湖区不同土地利用方式下土壤微生物数量与酶活性特征

以钱粮湖垸为例,研究了洞庭湖退田还湖区林地(Ⅰ)、园地(Ⅱ)、旱地(Ⅲ)、水田(Ⅳ)和荒地(Ⅴ)等不同土地利用方式下的土壤微生物数量、酶活性及其典范相关关系。结果表明:5种土地利用方式下不同土层细菌、放线菌数量均以旱地最高,真菌数量以荒地最高;细菌是土壤微生物的主要类群,占全部微生物的比例为44.42%～92.93%,其次为真菌数量,所占比例为4.89%～42.76%,放线菌数量最少,所占比例为1.71%～24.52%;不同土地利用方式下0～50cm土层磷酸酶、脲酶、蛋白酶和脱氢酶活性变化范围为0.01～0.07mg.g-1.d-1、0.01～0.05mg.g-1.d-1、0.92～7.11mg.kg-1.d-1和0.01～0.38μl.g-1.d-1;土壤磷酸酶、脲酶、脱氢酶活性分别以园地、荒地、水田最低,而旱地土壤蛋白酶活性总体最低;土壤微生物典范变量(U)中,放线菌数量与之呈正相关,回归系数最大(0.174),其次为细菌数量(0.003),而真菌数量则出现负相关(-0.215);土壤酶活性典范变量(V)中,脲酶活性与之呈正相关,回归系数最大(10.557),其次为脱氢酶活性(1.616),而磷酸酶活性(-17.275)与蛋白酶(-0.041)则出现负相关。不同层次土壤微生物数量及酶活性在典范变量上的聚集趋势可为该区域土壤健康诊断与立地类型划分提供依据。     

长期重金属胁迫对农田土壤微生物生物量、活性和种群的影响

调查了沈阳张士灌区长期污水灌溉造成的原位农田土壤重金属污染状况,从土壤微生物生物量、微生物活性和微生物种群数量的角度评价了长期重金属污染对农田土壤生态系统的影响.结果表明,张士灌区土壤存在严重的Cd污染,土壤Cd含量达1.75～3.89 mg·kg ^-1,部分区域还伴有Cu、Zn复合污染.在目前污染程度下,土壤微生物生物量碳(C_mic)、微生物商(qM)、土壤脱氢酶活性以及自生固氮菌数量随土壤重金属含量增加呈下降趋势,代谢商(qCO₂)随土壤重金属含量增加显著升高,而底物诱导呼吸强度(SIR)、纤维素酶活性以及细菌、放线菌和真菌数量无明显变化.相关性分析表明,土壤Cd含量变化是影响微生物参数变化的主要因素,在微生物参数中微生物商和代谢商对重金属污染最敏感.     

水淹条件下秋华柳亚细胞中镉的分配特征

选取秋华柳(Salix variegata)扦插苗为研究对象,通过设置0、0.5、2、10 mg/kg 4个镉胁迫浓度,研究了水淹条件下秋华柳根、枝、叶亚细胞中镉的分配特征。结果表明:(1)试验各处理组秋华柳存活率均为100%,表现出良好的镉和水淹耐受能力。(2)与对照相比,在水淹条件下,各处理组秋华柳根、枝和叶的细胞壁仍是镉最主要的富集部位。各处理组植株细胞壁中的镉含量显著高于其他组分,质体中镉含量次之,细胞核和线粒体组分中的镉含量始终处于较低水平。(3)水淹显著提高了秋华柳根细胞壁中的镉含量,显著降低了高浓度镉处理(10 mg/kg)下萌枝细胞壁中的镉含量,但对叶细胞壁中的镉含量没有显著影响。(4)水淹显著提高了秋华柳根细胞中质体中的镉含量,对萌枝、叶细胞质体中的镉含量没有显著影响。研究证明,水淹条件下,秋华柳根枝叶细胞壁仍然是镉积累富集的最主要部位,从而减少了重金属对植物细胞的伤害。秋华柳适用于三峡消落带镉污染区域的植物修复。     

The beneficial role of potassium in Cd-induced stress alleviation and growth improvement in Gladiolus grandiflora L.

Heavy metal contaminated agricultural soils are one of the most important constraints for successful cultivation of crops. The current research was conducted to evaluate the role of potassium (K) on plant growth and amelioration of cadmium (Cd) stress in Gladiolus grandiflora under greenhouse conditions. G. grandiflora corms were sown in media contaminated with 0 (C), 50 (Cd50) and 100 (Cd100) mg Cd kg^?1 soil. The plants growing in Cd-contaminated media exhibited reduced gas exchange attributes, chlorophyll (Chl) contents, vegetative and reproductive growth as compared to control. The plants raised in Cd contaminated media showed reduced nutrition yet higher Cd contents. However, supplementation of 60 mg Kg^?1 K in treated plants (C+K, Cd50+K and Cd100+K) improved quantity of total soluble protein and proline (Pro) along with activity of antioxidant enzymes including superoxide dismutase (SOD), catalase (CAT), peroxidase (POD) and ascorbate peroxidase (APX) under Cd stress. Similarly, K supplementation reduced the level of malondialdehyde (MDA) and hydrogen peroxide (H₂O₂) in treated plants. Potassium supplemented plants exhibited better vegetative and reproductive growth. The improved stress tolerance in K supplemented plants was attributed to the reduced quantity of MDA and H₂O₂, enhanced synthesis of protein, proline, phenols, flavonides and improved activity of antioxidant enzymes. The present research supports the application of K for alleviation of Cd stress in G. grandiflora.     

Foliar Spraying and Seed Soaking of Zinc Fertilizers Decreased Cadmium Accumulation in Cucumbers Grown in Cd-Contaminated Soils

It is important to use proper agronomic management to reduce cadmium (Cd) accumulation in plants, ensuring food safety. To find the most effective agronomic approach, the effect of foliar spraying and seed soaking of zinc (Zn) fertilizers on Cd accumulation in cucumbers (Cucumis sativus L.) grown in two soil Cd levels (2 and 5 mg kg^?1 Cd) with and without an immobilizing amendment (red mud, RM) was investigated in the present study. The results showed that the treatment of foliar Zn or seed Zn significantly decreased the Cd concentration in cucumber shoots by about 12–36% in Cd-contaminated soils without amendment. Combined with RM treatment, the foliar Zn treatment further decreased the Cd concentration in cucumber shoots by up to 48–66% in Cd-contaminated soils. There were significant negative correlations between Cd and Zn concentrations in shoots of cucumbers grown in soils treated with RM and foliar Zn. The results revealed that the cucumber seedlings treated with RM and foliar Zn had a higher capacity for limiting the transfer of Cd to aboveground tissues. The results also suggested that increasing seed Zn concentrations sufficiently might act as an efficient, economic, and practical method for decreasing Cd uptake in crops grown in mildly Cd-contaminated and Zn-deficient soils.     

微生物在镉污染土壤修复中的应用及其作用机理

土壤中镉（Cd）含量的超标导致了土壤生态系统的恶性发展,微生物作为土壤中的常见组分之一在缓解土壤镉污染中展现出巨大潜力。本文总结了微生物、微生物-植物和微生物-生物炭在镉污染土壤修复中的应用并阐述了相关的作用机理。芽孢杆菌（Bacillus）、不动杆菌（Acinetobacter）、荧光假单胞菌（Pseudomonas fluorescence）、丛枝菌根真菌（arbuscular mycorrhizal fungi,AMF）等微生物可以通过吸附、矿化、沉淀、溶解等方式改变镉的生物有效性,从而达到缓解镉污染的目的。pH值、温度、微生物生物量、镉初始浓度以及时间等对微生物降低镉的生物有效性方面有着显著的影响。假单胞菌、伯克霍尔德菌（Burkholderia）、黄杆菌（flavobacterium）等微生物可以通过促生、活化等作用促进超富集植物对Cd²⁺的吸收。生物炭作为一种土壤改良剂,其独有的理化性质可以作为微生物的庇护所。微生物-生物炭联合使用与单用生物炭相比可以进一步促进镉的残渣态的增加,降低土壤中有效态的比例。     

Some observations of two kinds of lemuridae (Varecia variegata variegata andLemur fulvus albifrons) in the reserve of Nosy Mangabe

A total of nine groups of ruffed lemurs (Varecia variegata variegata), as well as one solitary individual, were observed on Nosy Mangabe, an island located off the eastern coast of Madagascar, for a total 536 min between November 30 and December 8, 1983. The average group size was 2.8 animals (N=5), and the population density was 175 animals/km², as estimated from direct observation and location of vocalization. During the same period, nine groups of brown lemurs (Lemur fulvus albifrons) and one solitary individual were observed for a total 320 min. One group of brown lemurs was composed of eight animals (two adult males and females, one male juvenile, two infants, and one individual of undetermined age and sex). Feeding competition occurred between the two species, with whichVarecia variegata variegata dominating.     

Adsorption,Bioavailability, and Toxicity of Cadmium to Soil Microorganisms

The influence of adsorption on cadmium toxicity to soil microorganisms in soils was quantified as a function of solution and sorbent characteristics. The influence of adsorption on cadmium toxicity to soil microorganisms was assessed indirectly through the relative change in microbial hydrolysis of fluorescein diacetate (FDA) as a function of total Cd concentration and sorbent characteristics. The sequence of relative percentage of FDA hydrolysis was reference smectite (RS) > untreated Vertisol (UV) > dithionate-citrate-bicarbonate (DCB)-treated Vertisol (DV) > H₂O₂-treated Vertisol (HV) in suspensions containing the same total Cd concentrations. The correlation between the percentage of FDA hydrolysis and activity of Cd²⁺ _(aq) illustrates that RS has a higher capacity of Cd adsorption. The microbial activity of RS was higher and the toxicity was lower than that of other soil samples. The HV had lower capacity of Cd adsorption so that its FDA hydrolysis was low and the Cd toxicity was high.     

Phytostabilization potential of ornamental plants grown in soil contaminated with cadmium

In a greenhouse experiment, five ornamental plants, Osmanthus fragrans (OF), Ligustrum vicaryi L. (LV), Cinnamomum camphora (CC), Loropetalum chinense var. rubrum (LC), and Euonymus japonicas cv. Aureo-mar (EJ), were studied for the ability to phytostabilization for Cd-contaminated soil. The results showed that these five ornamental plants can grow normally when the soil Cd content is less than 24.6 mg·kg^?1. Cd was mainly deposited in the roots of OF, LV, LC and EJ which have grown in Cd-contaminated soils, and the maximum Cd contents reached 15.76, 19.09, 20.59 and 32.91 mg·kg^?1, respectively. For CC, Cd was mainly distributed in the shoots and the maximum Cd content in stems and leaves were 12.5 and 10.71 mg·kg^?1, however, the total amount of Cd in stems and leaves was similar with the other ornamental plants. The enzymatic activities in Cd-contaminated soil were benefited from the five tested ornamental plants remediation. Soil urease and sucrase activities were improved, while dehydrogenase activity was depressed. Meanwhile, the soil microbial community was slightly influenced when soil Cd content is less than 24.6 mg·kg^?1 under five ornamental plants remediation. The results further suggested that ornamental plants could be promising candidates for phytostabilization of Cd-contaminated soil.     

镉在土壤-香根草系统中的迁移及转化特征

以无植物组处理为对照,采用盆栽试验方式探讨不同Cd浓度胁迫条件下香根草根际土壤中重金属Cd的积累、迁移及转化特征。土壤Cd处理设4个浓度梯度,分别为0、2、20、80 mg/kg土壤干重。结果表明:(1)香根草可以显著降低土壤中生物有效态Cd和总Cd含量。(2)香根草各部分Cd积累量随处理浓度的增加和处理时间的延长而增加,90 d时80 mg/kg处理组地上部分和根的Cd积累量分别高达180.42 mg/kg和241.54 mg/kg。(3)各浓度Cd处理下,富集系数随着Cd处理浓度的增加而显著降低,随处理时间的延长而升高。(4)香根草地上部分Cd含量小于根部,各处理转移系数均小于1。随着处理时间的延长,中低浓度处理组的转移系数稍有降低,高浓度处理组的转移系数则显著上升。(5)种植香根草使其根际土中残渣态的Cd转化为生物有效态Cd,提高Cd清除效率。研究结果表明,香根草能够有效地吸收土壤中的Cd,降低土壤中总Cd含量,提高土壤安全性,可作为Cd污染地区植物修复的备选物种。     

Melatonin affects the growth and cadmium accumulation of Malachium aquaticum and Galinsoga parviflora

Phytoremediation technology has become one of the main techniques for remediating soils polluted by heavy metals because it does not damage the environment, but heavy metal-tolerant plants have the disadvantages of low biomass and slow growth. A pot experiment was conducted to study the effects of melatonin (Mel) on growth and cadmium (Cd) accumulation in the Cd accumulator Malachium aquaticum and hyperaccumulator Galinsoga parviflora by spraying different concentrations of Mel on them. The results showed that shoot biomass, photosynthetic pigment content and antioxidant enzyme activity were increased in both species after Mel was sprayed on their leaves. Mel reduced the Cd content in shoots of M. aquaticum and increased it in those of G. parviflora. In general, Cd accumulation was greatest in M. aquaticum when Mel was 200 μmol L^?1 (120.71 μg plant^?1, increased by 15.97% than control) and in G. parviflora when Mel was 100 μmol L^?1 (132.40 μg plant^?1, increased by 68.30% than control). Our results suggest it is feasible to improve the remediation efficiency of lightly Cd-contaminated soil by spraying G. parviflora with100 μmol L^?1 Mel.