镉污染农田土壤修复技术及安全利用方法研究进展

作物镉(Cd)超量累积是人体中镉的主要来源。研究镉污染农田土壤修复技术及安全利用方法对保护生态环境及保障食品安全具有重大意义。镉对植物的毒性效应与其生物有效性密切相关,且土壤镉的生物有效性决定其植物根系吸收量,因而基于土壤镉生物有效性调控原理的修复技术是农业环境领域近年来的研究热点。此外,植物镉含量也与植物自身特性密切有关,故筛选不同镉累积特性的植物可为镉污染土壤修复和安全利用提供重要生物质资源。文章综合评述了镉生物有效性的物理和化学调控方法,并分别就超累积植物和低累积作物介绍镉污染农田土壤的植物修复技术和安全利用方法。物理方法如水分管理主要通过改变土壤环境的Eh等理化性质从而影响土壤镉的形态转化过程,进而影响植物镉的吸收量;化学方法如施用钝化剂主要通过改变土壤的pH及土壤镉吸附特性,从而改变土壤镉的生物有效性。低镉累积作物通过减少根系镉吸收或降低地上部镉转运的方式减少可食部镉累积量;镉超累积植物的修复效率主要取决于其镉富集系数的高低及生物量的大小。化学和生物联合调控方法主要通过降低土壤镉含量或阻止镉进入作物可食部,实现"边生产边修复"。农田土壤镉污染修复技术及安全利用方法存在效率低、体系不稳定等问题,探究土壤镉生物有效性关键调控因子及其作用机制、充分挖掘特殊镉累积特性的植物资源并探寻改造植物镉耐性的方法以提高镉污染农田土壤修复效率将是今后该领域的研究热点。     

北京四环公路两侧植物铅、镉污染现状调查

植物叶片可富集多种污染元素,其含量与植物所处的环境有密切的关系,因此,植物叶片含污量可以指示环境污染情况,利用植物叶片的这种指示作用可以评价环境质量.铅、镉是严重污染人类环境、损害人体健康的微量元素,对人体毒性很大.大气中的铅、镉主要来源于冶炼、采矿和汽车尾气,而城市以及公路两侧地区铅、镉污染则主要源于汽车尾气.近年来,有研究成果表明利用植物叶片铅、镉含量可以指示大气铅污染状况,而且进一步的研究证明大气污染地区植物叶片的铅、镉主要是吸收或者吸附了大气中的铅和镉.     

土壤—植物系统中的镉研究进展

镉是土壤-植物系统中毒性最强的重金属之一，由镉产生的环境污染问题也日趋严重。近20年来，世界各国对镉在土壤-植物系统中的形态、转化、分布和毒害机理等都进行了广泛深入的研究本文对这些研究取得的成果和存在的分歧进行了综合评述，并提出对镉污染土壤进行综合治理的措施．     

镉胁迫下蓖麻对镉及矿质元素的富集特征

目前中国农田遭受镉污染的情况日益严重。蓖麻(Ricinus communis L.)是一种能源作物,同时对镉有较高的耐性和富集能力,因此利用蓖麻资源为合理利用镉污染农田提供了一种可行的途径。在温室条件下(5~32℃)采用盆栽试验,设定2个镉质量分数梯度(2.396和5.396 mg·kg-1),研究镉胁迫下30种蓖麻品种茎、叶和果实对镉和矿质元素(铝、钼、铜、钙、锌、硫、磷、镁、锰和铁)吸收和富集特征,以及矿质营养元素与镉富集的相关性。结果表明:镉在不同组织的分布情况为茎叶果实,铝、钼、硫、锰和铁在不同组织的分布为叶果实茎,钙和镁在不同组织的分布为叶茎果实,铜、锌和磷在不同组织的分布为果实叶茎。在低镉质量分数(2.396 mg·kg-1)处理条件下,茎、叶和果实中镉质量分数变化范围分别为0.600~1.670、0.310~1.970和0.130~0.909 mg·kg-1,平均值分别为1.030、0.831和0.362 mg·kg-1。在高镉质量分数(5.396mg·kg-1)处理条件下,茎、叶和果实中镉质量分数变化范围分别为1.012~4.032、0.698~3.514和0.227~1.525 mg·kg-1,平均值分别为1.964、1.583和0.694 mg·kg-1。蓖麻茎、叶和果实对镉和矿质元素(铝、钼、铜、钙、锌、硫、磷、镁、锰和铁)的富集受蓖麻品种和土壤中镉含量的显著影响。钙、硫、镁、铁的积累与镉的吸收呈显著正相关关系;锌、锰、铜、磷的积累与镉的吸收呈显著负相关关系,而铝、钼的积累与镉的吸收无显著相关关系。因此,合理调控污染土壤中矿质元素的含量可以提高蓖麻对镉污染土壤的修复效率。     

镉污染土壤对潜在能源植物生长的影响

利用重金属污染土壤种植能源植物是一种同时解决环境问题和能源问题的新理念,但目前相关研究成果并不多。通过盆栽试验研究人工镉污染土壤中象草Pennisetumpurpureum和亚香茅Cymbopogonnardus两种植物植株的生长状况和两种植物对土壤镉的吸收和富集能力。结果表明,当外源可溶性镉加入到土壤后,其主要是以生物有效性较高的状态存在。土壤镉对象草和亚香茅生长的影响作用有很大的不同,亚香茅比象草具有更强的镉耐受力,其生物量受镉污染影响小。两种植物植株镉含量均随土壤镉添加量的增加而增加。除高镉处理象草外,植物地下部分含镉量比地上部分高很多。高镉处理象草地下部分含镉量比地上部分低的现象可能反映出根系已积累了太多的镉,因而加速了向地上部的转移,从而加剧了植物中毒的程度。赤泥添加剂具有降低土壤酸度,减少植物对镉的吸收和增加象草和亚香茅生物量的作用。     

茴香对镉胁迫下钼硼锌协同处理的响应及精油组分的影响

采用营养液培养方式,以茴香(Foeniculum vulgare Mill.)为试验材料,研究了2 mg·L-1镉质量浓度下,钼硼锌协同处理对茴香植株生长、生理指标、地上部和根系镉含量及精油组分的影响。结果表明:镉胁迫下,与对照相比,钼硼锌协同处理均未显著促进茴香植株株高生长;T5处理有利于茴香植株生物量累积和叶绿素a、叶绿素b、叶绿素a+b、类胡萝卜素的合成,T1处理的可溶性糖含量最高,可溶性蛋白质含量最低,脯氨酸含量较低,丙二醛(MDA)含量最高,且叶绿素a、叶绿素b、叶绿素a+b、类胡萝卜素的合成显著受到抑制。镉胁迫下,钼硼锌协同处理后,茴香植株地上部和根系镉含量均高于对照。茴香精油中反式-茴香脑含量以T6处理最高。总之,镉胁迫下,钼硼锌协同处理并不能缓解镉对茴香植株的毒害作用;在轻微镉污染的土壤上种植茴香以食用地上部为目的,则不宜进行钼硼锌配施,否则会增加食入镉的危险性;利用茴香进行镉污染土壤修复为目的,则建议进行钼硼锌配施,可增加茴香植株对镉的吸收累积,提高修复效率。从提高修复效率和茴香精油质量方面综合考虑,T6处理效果最好。研究结果可为镉污染农田土壤上植物种植过程中钼硼锌的合理配施提供理论参考。     

海洋镉生物地球化学循环研究进展

镉是一种重要的有毒重金属元素,对生态系统和人体健康造成严重威胁.目前已有学者对土壤、大气、植物等介质中镉的环境行为进行了综述,而对海洋镉循环的系统梳理较少.本文综述了海洋中镉的来源、浓度分布与影响因素、镉生物地球化学循环过程及镉同位素在海洋中的示踪应用,并对海洋镉循环未来研究方向进行了展望.在现有研究的基础上,未来应在镉全球海洋大尺度循环、迁移转化及微观动力学机制方面开展更深入研究.海洋镉及其同位素生物地球化学循环的研究可为深入理解镉的环境行为与风险和发展有效的镉污染风险防控技术提供科学依据和数据支撑.     

不同比例钾锌共存对土壤镉有效性的影响

单一施用钾或锌肥会改变污染土壤中镉的有效性,但钾与锌共存对镉在土壤-植物系统中迁移和转化影响效果尚待明确.采用盆栽试验,研究了赤红壤上2种镉污染水平下,施用不同比例钾、锌对小油菜(Brassica campetris Lvar.Conmuni)生物量、镉吸收量及土壤溶液中镉质量浓度的影响.结果表明,钾、锌以不同比例与镉共存时并不会对赤红壤上小油菜的生长产生明显影响;增加共存体系中锌的用量,土壤溶液中镉的质量浓度明显升高,而小油菜植株镉含量明显降低.低、高镉污染赤红壤上,钾、锌共存摩尔比例为4:1时,土壤溶液中镉的质量浓度较对照分别增加189%和159%(两季平均值);小油菜体内镉含量较对照平均分别降低26.0%和34.9%.在低镉污染赤红壤上,钾、锌施用量与小油菜体内镉含量呈显著负相关;高镉污染赤红壤上,锌施用量与土壤溶液中镉的质量浓度呈显著正相关.中轻度镉污染土壤上,小油菜钾、锌肥最佳施用比例为4:1.钾、锌以不同比例施入土壤时,锌施用量多少是控制土壤镉有效性高低的主要因素.     

棉秆炭对镉污染土壤的修复效果

采用盆栽方法,研究了棉秆炭对镉污染土壤的修复效果及对镉污染土壤上小白菜(Brassica chinensis)镉吸收的影响.结果表明:以微孔为主的棉秆炭能够通过吸附或共沉淀作用降低土壤中镉的生物有效性.在轻度镉污染时,棉秆炭处理土壤对镉的吸附速率较快,随着镉污染程度的增加.吸附速率逐渐减慢,吸附量逐渐增加.棉秆炭能够明显降低镉污染土壤上小白菜可食部和根部的镉积累量,可食部镉质量分数降低49.43%～68.29%,根部降低64.14%～77.66%,说明棉秆炭具有修复土壤镉污染,降低蔬菜镉含量的作用,可提高蔬菜品质.     

洞庭湖区东亚金发藓(Pogonatum inflexum)对土壤镉污染反应特征初探

如何利用较为科学、合理的技术方法,对土壤中的镉污染及其修复效果进行监测与评价,是植物修复土壤镉污染实际操作中存在的重要问题。该研究基于东亚金发藓(Pogonatum inflexum)对镉的敏感性反应特征,初步探索一种适用于土壤镉污染的生物监测方法。以含镉背景值相对较低的土壤作为栽培基质,采用梯度质量分数镉胁迫的方式进行研究,结果表明,(1)当土壤中的镉质量分数大于2~3 mg·kg-1时,东亚金发藓植株孢子体和配子体的外观形态在短时间内呈现出显著变化特征;随镉质量分数的增加和时间的延长,小叶受害程度加深,出现黄化或褐变现象,测定期内5 mg·kg-1的镉处理最终可使植株枯亡。(2)叶绿素含量受镉胁迫影响显著,且对镉胁迫时间反应较为迅速:2 mg·kg-1以内的镉处理下,叶绿素含量在7d中的变化均不大;镉质量分数大于3 mg·kg-1时,对叶绿素含量影响显著,且随时间延长叶绿素下降程度更加明显;4 mg·kg-1的镉处理可使叶绿素含量下降3/4以上。(3)镉胁迫导致植物体内可溶性蛋白含量显著降低,处理初期可溶性蛋白含量变化不大,后期则变化明显,可导致蛋白含量减少40%~50%;同时细胞膜脂过氧化作用显著增强(表现为MDA浓度上升),MDA含量增加了1.8倍以上。(4)东亚金发藓叶绿素含量、可溶性蛋白含量及MDA含量等生理参数的变化,可有效指示土壤中镉的生物有效性,并能反映土壤镉安全浓度标准。(5)东亚金发藓的假根对土壤中的镉具有较强的感应能力,植株易受到镉离子毒害并快速、直观地表现出一系列症状,因此可作为有效监测土壤镉污染的理想植物材料。     

Project Tocoen. the fate of selected pollutants in the environment. Part XIX. the phytotoxicity of organic and inorganic pollutants‐cadmium. The effect of cadmium on the growth of germinating maize plants

The effect of increasing cadmium concentration (10, 100 and 1000 μmol dm^‐3) on the growth, leaf area, content of assimilation pigments, cadmium content and the regulatory ability of the tissue of maize plants was investigated.

The results obtained document, already after 6 days, a significant decrease of dry weight, reduction of leaf area, chlorophyll a and b as well as carotenoids in plants grown in the nutrient solution containing 1000 μmol dm ^‐3 of cadmium. A highly significant inhibition of growth, leaf area and assimilation pigments in plants growing in the nutrient solutions with 100 and 10 μmol dm^‐3 of cadmium was registered after 17 days of cultivation. In plants growing in the nutrient solution containing 100 μmol dm^‐3 of cadmium a demonstrable reduction of the content of assimilation pigments was registered after 11 days of culture.

With increasing cadmium concentration in the nutrient solution as well as in the plant tissue after 6 and 17 days of culture both the range of the regulatory zone and the extent of optimum pH increased into the acid region. The pH values of the isoelectric point decreased with increasing cadmium content in the solution.     

镉对籽粒苋耐性生理及营养元素吸收积累的影响

初步阐明了镉对籽粒苋耐性生理及营养元素吸收积累的影响,为进一步揭示籽粒苋的镉耐性与镉富集机理奠定了基础。通过对生物量的监测,对叶绿素、蛋白质、游离氨基酸、大量元素及微量元素等的含量的测定,阐明镉胁迫对籽粒苋生长生理、抗胁迫耐性、营养元素吸收分配的影响。研究结果显示,镉胁迫对籽粒苋的生长抑制作用不明显,植株生物量随着镉浓度的提高而轻微降低。随着镉处理浓度的提高,叶绿素含量下降幅度显著;蛋白质和游离氨基酸含量变化幅度不明显;钾含量无大幅变化;镉、磷、钙、镁、锌、铁、锰、铜含量变化幅度较显著。镉、钾、磷、锰的迁移系数随着镉处理浓度的提高无显著变化;钙的迁移系数呈上升趋势;镁、锌、铁、铜的迁移系数均呈下降趋势。这些结果表明：镉胁迫降低籽粒苋叶绿素含量,抑制植株光合作用,继而抑制了植株的生长,但其程度不明显;镉胁迫条件启动活性氧防御机制;引起植株体内部分养分代谢紊乱。结论：低浓度镉处理条件下,籽粒苋受镉离子影响,抗氧化能力下降。在高浓度镉处理条件下,籽粒苋调节了营养元素的吸收和分配,启动了一系列活性氧防御机制,提高了抗胁迫能力。     

Heavy metals,occurrence and toxicity for plants: a review

Metal contamination issues are becoming increasingly common in India and elsewhere, with many documented cases of metal toxicity in mining industries, foundries, smelters, coal-burning power plants and agriculture. Heavy metals, such as cadmium, copper, lead, chromium and mercury are major environmental pollutants, particularly in areas with high anthropogenic pressure. Heavy metal accumulation in soils is of concern in agricultural production due to the adverse effects on food safety and marketability, crop growth due to phytotoxicity, and environmental health of soil organisms. The influence of plants and their metabolic activities affects the geological and biological redistribution of heavy metals through pollution of the air, water and soil. This article details the range of heavy metals, their occurrence and toxicity for plants. Metal toxicity has high impact and relevance to plants and consequently it affects the ecosystem, where the plants form an integral component. Plants growing in metal-polluted sites exhibit altered metabolism, growth reduction, lower biomass production and metal accumulation. Various physiological and biochemical processes in plants are affected by metals. The contemporary investigations into toxicity and tolerance in metal-stressed plants are prompted by the growing metal pollution in the environment. A few metals, including copper, manganese, cobalt, zinc and chromium are, however, essential to plant metabolism in trace amounts. It is only when metals are present in bioavailable forms and at excessive levels, they have the potential to become toxic to plants. This review focuses mainly on zinc, cadmium, copper, mercury, chromium, lead, arsenic, cobalt, nickel, manganese and iron.     

镉胁迫对银条内镉残留及其品质的影响

为探索重金属Cd对银条（Stachys floridana Schuttl.ex Benth.）地下茎品质的影响及其Cd残留情况,将银条地下茎在经消毒的沙子中发芽生长,并浇灌改良Hoagland营养液,待银条长到第一朵花的花蕾出现时,对生长状况良好的银条按一定周期浇灌不同质量浓度的Cd^2＋（CdCl2分析纯）,以不施镉为对照,两个月成熟后采其地下茎进行品质测定,并利用电感耦合等离子体发射光谱仪测定经消解的样品中Cd的含量。实验结果表明,随着Cd胁迫质量浓度的增加,可溶性糖、可滴定酸、可溶性蛋白含量逐渐降低,呈负相关关系,相关系数分别为-0.984 9^＊＊、-0.991 2^＊＊和-0.893 3^＊＊,其含量分别为对照的58.40%、57.56%和75.68%;可溶性固形物、维生素C含量呈先稍微上升然后再下降的趋势,而粗纤维的含量则逐渐升高,但数值变化不是很明显;Cd在地下茎中的残留随着Cd胁迫质量浓度的增加而升高,且各处理与对照呈极显著差异,并与国家蔬菜卫生标准相比,Cd含量严重超标,在250 mg·L^-1的Cd质量浓度下其残留是国家标准的16.46倍。     

The effects of feeding by the black bean aphidAphis fabae Scop. (Homoptera: Aphididae) on copper and cadmium accumulation in broad bean (Vicia faba L.)

Broad beans (Vicia faba L.), cultured hydroponically were supplied with 100 g mL^–1 copper or 50 g mL^–1 cadmium in nutrient solution. Samples of plant material from both nutrient regimes were analysed before and after infestation by the black bean aphid (Aphis fabae Scop.). Heavy aphid infestation resulted in a significant reduction in copper content of shoots in comparison with uninfested plants. A similar, but less well- defined, situation occurred in the case of cadmium.Further investigations examined the effects of different levels of aphid infestation on the above phenomena. In all cases the presence of feeding aphids reduced elemental accumulation in plant shoots. Long term infestation with population densities as low as three adult aphids showed a reduction in shoot copper and cadmium content.     

模拟降水对碱性盐化土壤中镉的淋滤及形态变化的影响

采用人工模拟方式,试验研究了不同pH值的降水对碱性盐化土壤中镉的连续淋滤效果,分析了淋洗后土壤中镉的形态变化特征。结果表明,在不同pH值降水对土壤中镉的淋滤过程中,12h内基本上达到高峰,12h后镉的淋滤量较低,随着时间的延续镉的淋洗量基本保持不变;降水有利于土壤中的镉释放,且pH值越低,镉的释放量越高。土壤盐化对降水淋洗镉的效果有一定影响,氯化物的存在,有利于镉的淋滤,淋滤量增加值在18%～94%之间,随着淋洗液pH值的增加,镉的淋滤量增加幅度减少;与对照组土壤样品相比,淋洗液pH降低利于增大硫酸盐型盐化土壤中镉的淋滤量,当pH值为中性时,镉的淋滤量减少;苏打型盐化土壤镉的淋洗效果与硫酸盐型土壤相似。模拟降水淋洗后,土壤中镉的形态发生明显变化,与淋洗前相比,土壤中镉的可交换态、碳酸盐结合态、有机结合态的质量分数降低,随着淋洗液酸性的增加,降低幅度增大;镉的铁锰氧化态相对质量分数在淋洗后有所增加。     

Influence of Dissolved Organic Matter On the Bio-Availability and Toxicity of Metals in Soils and Aquatic Systems

Cations in soil are essential for the growth of plants and micro-organisms. Their availability is dependent on soil organic matter. Soil organic matter (SOM) is heterogeneous comprising amino, aliphatic and phenolic acids, but particularly humic substances. All these substances can complex cations selectively. Mechanisms of complexation with dissolved organic matter are discussed. Such complexation can lead to the apparently contradictory observations that dissolved organic matter (DOM) can either increase the concentration of some less soluble nutrients, making them more available for plant uptake, or make them less available and hence less toxic. the importance of DOM is discussed in relation to soil solution, particularly the rhizosphere, and also in relation to aquatic systems. the latter systems contain mainly dissolved humic substances whereas in the soil, non-humic substances assume a greater importance.

SOM in the rhizosphere is derived from plant, microbial and animal remains but much, especially the water-soluble compounds, are acquired through root exudation. Exudation has important consequences for enhanced nutrient availability as a result of the production of non-humic substances such as amino, aliphatic and phenolic acids. in future, the role of root exudation in relation to DOM and nutrient availability should be investigated more fully, particularly as predicted elevated CO₂ levels are likely to have a major impact on root exudation, nutrient availability, and possibly ecosystem community structure and functioning. It is likely that more information will become available on aquatic systems as more highly sensitive techniques and equipment capable of dealing with low concentrations of DOM in these systems become available.     

Influence of Dissolved Organic Matter On the Bio-Availability and Toxicity of Metals in Soils and Aquatic Systems

Cations in soil are essential for the growth of plants and micro-organisms. Their availability is dependent on soil organic matter. Soil organic matter (SOM) is heterogeneous comprising amino, aliphatic and phenolic acids, but particularly humic substances. All these substances can complex cations selectively. Mechanisms of complexation with dissolved organic matter are discussed. Such complexation can lead to the apparently contradictory observations that dissolved organic matter (DOM) can either increase the concentration of some less soluble nutrients, making them more available for plant uptake, or make them less available and hence less toxic. the importance of DOM is discussed in relation to soil solution, particularly the rhizosphere, and also in relation to aquatic systems. the latter systems contain mainly dissolved humic substances whereas in the soil, non-humic substances assume a greater importance.

SOM in the rhizosphere is derived from plant, microbial and animal remains but much, especially the water-soluble compounds, are acquired through root exudation. Exudation has important consequences for enhanced nutrient availability as a result of the production of non-humic substances such as amino, aliphatic and phenolic acids. in future, the role of root exudation in relation to DOM and nutrient availability should be investigated more fully, particularly as predicted elevated CO₂ levels are likely to have a major impact on root exudation, nutrient availability, and possibly ecosystem community structure and functioning. It is likely that more information will become available on aquatic systems as more highly sensitive techniques and equipment capable of dealing with low concentrations of DOM in these systems become available.     

基因工程改良植物对重金属污染土壤的修复

利用基因工程改良植物，调整植物吸收、运输和富集重金属的能力以及它们对重金属的耐受性，开拓了植物修复的新领域。到目前为止，已有成功改变这些特性的少数例子。例如，汞离子还原酶可以改善植物抵抗力和提取能力，金属巯基蛋白可增强植物对镉的耐受力，铁还原酶和铁蛋白可增加植物对铁的吸收量。文章综述和讨论了这方面的研究进展及方向。     

Biochemical responses and accumulation of cadmium in Spirodela polyrhiza

The present study focused on biochemical responses of Spirodela polyrhiza to cadmium stresses and its accumulation. The laboratory experiments were conducted for the assessment of biochemical responses and accumulation of cadmium in plants at its various concentrations (0.1, 0.5, 1.5 and 2.0 ppm) at the regular interval for twelve days exposure. Spirodela showed visible symptoms like withering of roots and chlorosis at higher concentration (2.0 ppm), however the plant showed normal growth at lower concentration (0.1 ppm). The estimation of biochemical parameters (total chlorophyll, protein and carbohydrate) of test plants showed a significant increase at lower concentration (0.1 ppm) of cadmium. The biochemical changes decrease with increase in exposure concentration and duration. The toxic effect of cadmium is directly proportional to its concentration and duration. The accumulation of cadmium by Spirodela polyrhiza was maximum at four days exposure duration and gradually decreases.