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1.
蚯蚓在土壤重金属污染及其修复中的应用研究进展   总被引:10,自引:0,他引:10  
唐浩  朱江  黄沈发  邱江平 《土壤》2013,45(1):17-25
蚯蚓作为主要的大型土壤动物类群,对土壤环境改善起到了重要的作用,本文在系统分析、归纳总结国内外相关领域研究成果的基础上,综述了蚯蚓在土壤重金属污染及其修复中的应用研究进展,主要包括:蚯蚓作为土壤重金属污染的指示生物,蚯蚓对重金属的富集与释放,重金属对蚯蚓生理生态的影响研究,蚯蚓在土壤重金属污染修复中的作用机制,蚯蚓与植物、微生物的协同作用,以及蚯蚓粪作为重金属污染修复剂的潜力分析等.在此基础上,概括提出了蚯蚓在重金属污染土壤修复领域面临的主要问题.  相似文献   

2.
植物修复作为一种生态友好型原位绿色修复技术成为重金属污染土壤修复研究的热点。然而,目前最具有推广价值的超积累植物因生物量低、生长缓慢、对重金属的积累具有专一性等缺点,大大限制了植物修复技术在重金属污染尤其是复合重金属污染土壤治理方面的推广应用。利用生长速度快、生物量大的普通植物借助其它技术辅助的联合植物修复便成了有效可行的替代途径和研究焦点。近年来,金属螯合剂诱导的化学一植物联合修复技术备受关注。本文综述了螯合剂诱导植物修复技术的研究进展、修复机理和目前存在的问题,并对该项技术的未来研究方向给予了展望。  相似文献   

3.
重金属污染土壤的螯合剂诱导植物修复研究进展   总被引:4,自引:0,他引:4  
植物修复作为一种生态友好型原位绿色修复技术成为重金属污染土壤修复研究的热点。然而,目前最具有推广价值的超积累植物因生物量低、生长缓慢、对重金属的积累具有专一性等缺点,大大限制了植物修复技术在重金属污染尤其是复合重金属污染土壤治理方面的推广应用。利用生长速度快、生物量大的普通植物借助其它技术辅助的联合植物修复便成了有效可行的替代途径和研究焦点。近年来,金属螯合剂诱导的化学-植物联合修复技术备受关注。本文综述了螯合剂诱导植物修复技术的研究进展、修复机理和目前存在的问题,并对该项技术的未来研究方向给予了展望。  相似文献   

4.
蚯蚓对印度芥菜修复Zn、Pb污染土壤的影响   总被引:4,自引:0,他引:4  
以褐土为供试土壤,分别加入不同浓度梯度Zn2+(0,100,200,400 mg kg-1)或Pb2+(0,200,400,800 mg kg-1)模拟土壤污染,设置添加蚯蚓与不添加蚯蚓处理,通过盆栽实验,研究蚯蚓对印度芥菜生长量和重金属吸收量的影响,旨在探讨蚯蚓在植物-土壤系统中影响重金属迁移转化的作用机理,为蚯蚓在植物修复技术的实践与完善提供理论参考。结果表明:(1)在Zn、Pb污染土壤中,蚯蚓生长率分别降低3%~24%、6%~29%;(2)蚯蚓活动可以降低土壤的pH,显著增加土壤中Zn的有效态含量;(3)蚯蚓活动显著增加了印度芥菜地上部生物量(22.6%~88.6%鲜重,31.3%~122%干重)和印度芥菜地上部Zn的浓度及Zn和Pb的吸收量。印度芥菜地上部重金属浓度和吸收量与土壤中DTPA提取态含量呈极显著正相关(P <0.01),与土壤pH呈负相关。(4)蚯蚓对重金属的活化和对植物生长的促进是解决植物修复瓶颈问题的有效手段。  相似文献   

5.
农艺措施强化重金属污染土壤的植物修复   总被引:10,自引:0,他引:10  
作为植物修复强化技术,农艺措施可有效提高土壤重金属污染的修复效率。本文从土壤管理和植物管理两大方面综述了农艺措施强化重金属污染土壤植物修复的研究进展,重点讨论了施肥、蚯蚓强化以及植物栽培管理措施用于强化植物修复的基本原理与相关应用,并提出今后研究的方向。  相似文献   

6.
砷污染土壤的生物修复研究进展   总被引:8,自引:0,他引:8  
白建峰  林先贵  尹睿  张华勇 《土壤》2007,39(5):692-700
土壤As污染已是全球性问题,我国也不例外,对As污染土壤的生物修复已是研究热点,但相关机理仍不完全清楚.本文综述了国内外微生物、蚯蚓、植物在As污染土壤中吸收转化As及其解As毒机理,以及微生物-植物复合系统修复As污染土壤方面实验室内研究情况.目前广泛认为植物修复土壤重金属/非金属污染较有应用前景,可限于甚至是使用超富集植物单一作用下仍有较多缺陷,如通过微生物技术及蚯蚓调节根际微生态,以利于植物在污染土壤中存活或/和吸收更多的As,将极具应用前景.  相似文献   

7.
重金属污染土壤的植物提取修复强化途径主要有2种,一是提高植物生物量,二是提高植物体内重金属含量。从螯合剂的作用机理,常用螯合剂种类,不同种类螯合剂对土壤中目标重金属的活化效果,以及螯合剂诱导下植物对目标重金属的吸收和积累效应,螯合剂使用对生态环境造成的负面影响等方面综述了重金属污染土壤螯合诱导强化植物提取修复技术的研究进展,同时对植物修复后的评价以及螯合诱导植物修复技术今后的发展方向进行了探讨。  相似文献   

8.
土壤重金属污染、生态效应及植物修复技术   总被引:5,自引:0,他引:5  
探讨了土壤中重金属的来源、特点以及生态效应,综述了土壤重金属污染的植物修复技术,展望了重金属污染土壤的植物修复研究发展趋势。  相似文献   

9.
重金属污染土壤的植物强化修复研究进展   总被引:5,自引:2,他引:3  
《土壤通报》2017,(4):1008-1013
随着工农业生产的快速发展,土壤重金属污染日益严重,土壤重金属污染的高效快速修复技术备受关注。在各种土壤重金属污染修复技术中,植物修复技术因其清洁、简单、高效、低消耗等优点,得到人们的认可,具有良好的发展前景。论文综述了土壤重金属污染来源及现状,植物修复技术的基本原理及特点,植物强化修复技术的研究进展,分析了当前植物强化修复技术中存在的问题,并指明了植物强化修复技术的发展方向,以期为土壤重金属污染的快速、绿色修复提供理论依据。  相似文献   

10.
土壤重金属污染已成为亟待处理的环境问题,植物修复技术是一种绿色经济、有效缓解土壤重金属污染的修复方式,间作能够有效的修复土壤重金属污染,综述了间作系统中种间相互作用对植物吸收积累重金属的影响及其机理,并对今后的研究进行了展望。  相似文献   

11.
内生细菌强化重金属污染土壤植物修复研究进展   总被引:9,自引:0,他引:9  
马莹  骆永明  滕应  李秀华 《土壤学报》2013,50(1):195-202
近年来,植物修复因其独特的优势备受推崇,尤其是当前植物内生细菌的应用为植物修复重金属污染土壤提供了有效的新方案.在植物修复过程中,耐重金属的内生细菌利用与植物的共生互惠关系,通过自身的抗性系统缓解重金属的毒性,促进植物对其迁移,并通过溶磷、固氮等途径改善植物营养以及分泌植物激素、铁载体、特异性酶、抗生素等作用,促进植物在逆境条件下的生长和对重金属的富集.本文综述了近年来国内外关于重金属抗性植物内生细菌促进植物生长、增强植物对重金属的抗性以及影响重金属在植物体内吸收、转运和积累的作用机制,系统分析了内生细菌促进植物修复重金属污染土壤的机理,并进一步讨论了植物内生细菌在重金属污染土壤植物修复工程中的应用前景与研究方向.  相似文献   

12.
Advances in fungal-assisted phytoremediation of heavy metals: A review   总被引:1,自引:0,他引:1  
Trace metals such as manganese (Mn), copper (Cu), zinc (Zn), and iron (Fe) are essential for many biological processes in plant life cycles. However, in excess, they can be toxic and disrupt plant growth processes, which is economically undesirable for crop production. For this reason, processes such as homeostasis and transport control of these trace metals are of constant interest to scientists studying heavily contaminated habitats. Phytoremediation is a promising cleanup technology for soils polluted with heavy metals. However, this technique has some disadvantages, such as the slow growth rate of metal-accumulating plant species, low bioavailability of heavy metals, and long duration of remediation. Microbial-assisted phytoremediation is a promising strategy for hyperaccumulating, detoxifying, or remediating soil contaminants. Arbuscular mycorrhizal fungi (AMF) are found in association with almost all plants, contributing to their healthy performance and providing resistance against environmental stresses. They colonize plant roots and extend their hyphae to the rhizosphere region, assisting in mineral nutrient uptake and regulation of heavy metal acquisition. Endophytic fungi exist in every healthy plant tissue and provide enormous services to their host plants, including growth enhancement by nutrient acquisition, detoxification of heavy metals, secondary metabolite regulation, and enhancement of abiotic/biotic stress tolerance. The aim of the present work is to review the recent literature regarding the role of AMF and endophytic fungi in plant heavy metal tolerance in terms of its regulation in highly contaminated conditions.  相似文献   

13.
丛枝菌根真菌在植物修复砷污染土壤中的作用   总被引:2,自引:0,他引:2  
肖艳平  尹睿  沈生元  陈玉成  邢赜  陈雪民 《土壤》2010,42(2):171-177
丛枝菌根真菌能增强植物对矿质元素的吸收、提高植物的抗逆性、增强抗病性、改善植物根际微环境,减轻重金属对植物的毒害,影响植物对重金属的吸收和转运,在重金属污染土壤的植物修复中显示出极大的应用潜力。近年来,As污染已成为全球非常突出且急需解决的环境问题之一,对As污染土壤的生物修复也因而成为研究热点。本文主要从丛枝菌根真菌改变土壤pH和酶活性、增强植物对As的耐性和影响植物对As的吸收方面综述了丛枝菌根在As污染土壤修复中应用的研究进展,揭示出菌根应用在As污染土壤中的作用潜力和研究方向。  相似文献   

14.
Enhanced phytoextraction of heavy metals using chelating agents and agricultural crops is widely discussed as a remediation technique for agricultural soils contaminated with low mobile heavy metals. In this study, phytoextraction efficiency of Zea mays after single and split applications of EDTA was tested on the laboratory and the field scale. EDTA effectively increased the mobility of target heavy metals (Pb and Cd) in the soil solution. Split applications provided generally lower water-soluble levels of Pb and Cd both in the pot and the field experiment. Therefore, the risk of groundwater contamination may be reduced after split applications. Higher Pb and Cd mobilisation after single applications increased plant stress, phytotoxicity and reduced plant dry above-ground biomass production compared to corresponding split doses. Single doses enhanced plant uptake of Pb and Cd and the phytoremediation efficiency compared to corresponding split doses. Results of plant dry above-ground biomass and heavy metal uptake obtained from the pot experiment could be to some extent verified in the field experiment. Plant uptake of Pb and Cd was lower and biomass production dropped after EDTA additions in the field experiment. Remediation factors in the field experiment were in general significantly lower than in the pot experiment mainly due to the much higher mass of soil per plant under field conditions. This highlights the limitations when going from the lab to the field scale. The low phytoremediation efficiency in the field and the mobilisation of high amounts of Pb and Cd down the soil profile may make the use of EDTA and Z. mays not suitable for the remediation of severely heavy metal contaminated soils in a reasonable time frame and may result in substantial groundwater pollution under used crop management.  相似文献   

15.
Lead and zinc mine tailings from Guangdong, China were found to be toxic to two common species of the earthworm Pheretima, unless the spoil was diluted by at least 20% with an artificial uncontaminated soil. With different soil dilutions, there were significant differences in mortality, growth and Zn uptake between the two species. Zinc and arsenic were principally responsible for the toxicity of the tailings. LC50 values for Zn, Pb, Cu and As for Pheretima were similar to those reported in the literature for Eisenia fetida. Following inoculation with the earthworms, spoil pH, EC and available metals increased; available-Pb and -Zn concentrations increased by up to 48.2% and 24.8% respectively. The findings suggest that earthworms may play an important role in reclamation of mining spoils to achieve a healthy soil supporting sustainable vegetation. Potentially increased toxicity of metals to plants and animals, through increased bioavailability in the presence of earthworms, is discussed in the context of their role in modifying the efficiency of phytoremediation treatments.  相似文献   

16.
In this study we have investigated the toxicity of soils from thetwo abandoned pyrite mines Ertelien and Konnerud in the southernpart of Norway. Soil samples were collected close to the pitheadof the mines, and earthworms were exposed to different concentrations of the contaminated mine soil mixed with commercial plant soil for a period of 14 days. Life-cycle responses such as growth and survival, as well as the biomarkerresponse lysosomal fragility were measured. The body burdens ofthe four heavy metals Cu, Cd, Zn and Pb were detected in the worms, and the body concentration of the metals generally increased with increasing heavy metal concentration in the soil.The growth and mortality of the earthworms were not influenced when exposed to any of the mine soil concentrations used. The lysosomal fragility of the earthworm coelomocytes measured by the neutral red retention time (NRR-time) was found to be markedly reduced in all the exposed earthworms. This assay seemsto be a sensitive and dose dependent endpoint for the toxicity assessment of heavy metal mixtures in pyrite mine soils.  相似文献   

17.
Background: Stimulatory efficacy of spent mushroom compost (SMC) cannot be overemphasized. Aims: In this study, the effect of SMC on phytoremediation and plant's response to heavy metal polluted soil was investigated and suggested for the establishment of feasible soil remediation. Methods: Heavy metal polluted soil (80 kg) was sterilized at 121°C in soil sterilizer for 30 min and repeated four more times to remove microbial interference. Five kg of soil was packed into pots supplemented with SMC of Pleurotus ostreatus at different concentrations of 10, 20, 30, and 40%, and control (no SMC), and used to grow the test plant (Megathyrsus maximus commonly known as Guinea grass) for 90 d. Effect of SMC treatments on chemical characteristics of the soil was determined through soil analysis before and after the experiment. Plant response to SMC in polluted soils was studied by observing root proliferation, plant growth, and biomass. Results: The results suggest that SMC treatment modified soil chemical characteristics, the germination index (GI), plant growth, and phytoremediation potential. The soil's pH increased from 4.3 in control to 6.8 both in 40 and 30% SMC treatments; also the soil's nutrients, cation exchange capacity (CEC), and GI improved with incremental increase in SMC treatments, while the heavy metal removal was best observed at 40 and 30% treatments. In addition, the bio‐stimulatory effect of SMC was confirmed on guinea grass root proliferation, growth, phytomass and its phytoremediation potentials on heavy metals. Conclusions: The SMC is therefore suggested for soil stimulation to improve plant's growth and phytoremediation.  相似文献   

18.
Abstract

In order to quantify the uptake by lettuce plants (Lactuca sativa L.) of heavy metals contained in the phosphate fertilizers and to evaluate their residual bioavailability in the growth substrate a greenhouse experiment was carried out. The superphosphate added to the soil contained varying amounts of heavy metals, particularly Cd, Cr and Zn which accumulated in the soil and increased the amounts available for plant uptake. The accumulation of metals observed in the plant tissues did not have physiological effects on lettuce and did not affect negatively the growth of the plants. The heavy metal speciation in soil indicated that metals extractable by EDTA increased by increasing the phosphorus added. These amounts of metals, adsorbed or complexed in the soil after harvest, represent in protected environments a potentially bioavailable species for the following cultivations.  相似文献   

19.
Phytoremediation Technology: Hyper-accumulation Metals in Plants   总被引:2,自引:0,他引:2  
This paper reviews key aspects of phytoremediation technology and the biological mechanisms underlying phytoremediation. Current knowledge regarding the application of phytoremediation in alleviating heavy metal toxicity is summarized highlighting the relative merits of different options. The results reveal a cutting edge application of emerging strategies and technologies to problems of heavy metals in soil. Progress in phytoremediation is hindered by a lack of understanding of complex interactions in the rhizosphere and plant based interactions which allow metal translocation and accumulation in plants. The evolution of physiological and molecular mechanisms of phytoremediation, together with recently-developed biological and engineering strategies, has helped to improve the performance of both heavy metal phytoextraction and phytostabilization. The results reveal that phytoremediation includes a variety of remediation techniques which include many treatment strategies leading to contaminant degradation, removal (through accumulation or dissipation), or immobilization. For each of these processes, we review what is known for metal pollutants, gaps in knowledge, and the practical implications for phytoremediation strategies.  相似文献   

20.
Abstract

Phytoremediation is increasingly used to remediate metal contaminated soils. However, in order to provide technically efficient phytoremediation of contaminated sites the plant yield and metal uptake have to be enhanced dramatically. The aim of the study was to find appropriate combination of plant species and fertilizers capable of improving yields of the plants and stimulate a transfer of metals to more available to the plants forms. Wheat Triticum vulgare was used for the phytoremediation research. To increase yield of crops and enhance mobility of metals in the rhizosphere the soils were amended with three fertilizers (urea, horse manure, and “ispolin”). Short-term (36 d) vegetation test showed that concentrations of heavy metals in the plants grown in contaminated soil (from site 2) were significantly higher than those in the plants grown in clean soil (from site 1). Growth of wheat resulted in a decrease of Cd content in the soil. Amendment of the contaminated soil with urea enhanced the effect and the decrease of Cd concentration in the soil was more significant. The best effect was demonstrated after application of ispolin: concentrations of Cd, Cu, Pb, and Zn in the rhizosphere decreased 1.2–1.4 times as compared with those in the initial contaminated soil (the decrease was statistically significant).  相似文献   

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