根际促生菌防控土传病害的机理与应用进展

根际促生菌作为一类活跃于植物根际的有益微生物,对抑制土传病害的发生,改善和维护土壤生态质量具有重要作用以及广阔的发展前景。本文综述了根际促生菌直接或间接的土传病害防控机理,包括产抗生素、产水解酶、释放挥发性气体、诱导抗性、分泌铁载体、分泌激素和固氮解磷等;亦从信号识别与迁移、定殖规律以及定殖的微生物群落影响等方面对根际促生菌的定殖防病机理予以了总结;此外,笔者还就根际促生菌的应用现状进行了概述。     

植物根际促生菌辅助红麻修复铅污染土壤

通过盆栽实验研究土壤Pb浓度对经济作物红麻（Hibiscuscannabinus）生长、富集及转运Pb的影响,并将具有较强Pb抗性的植物根际促生菌（PGPR）DBM1（Arthrobactersp．）接种至红麻根际,考察Pb胁迫下PGPR对红麻的促生作用,以探索利用PGPR辅助重金属耐性植物红麻对Pb污染土壤进行植物稳定修复的可行性。结果表明,土壤Pb浓度和接菌处理均显著影响红麻的生长。红麻对Pb具有较高耐性,可通过将Ph富集在根部,并抑制其向地上部转移,从而在中低Pb（Pb400和Pb800处理）污染土壤中良好定植和生长。土壤Pb浓度达到1600mg·kg^-1时,红麻生长开始受到Ph胁迫的抑制,红麻通过自身胁迫抵抗机制缓解Pb毒性。接种DBM1可有效促进红麻的生长,提高红麻叶绿素含量。DBM1对红麻的促生作用是由胁迫诱导的特性,在高Pb胁迫下促生效果更显著。因此,可利用植物根际促生茵DBM1辅助红麻对高Pb污染土壤进行植物稳定修复,在促进红麻生长的同时,有效抑制Pb向红麻地上部的转移。     

棉花根际促生细菌的研究进展

综述了根际促生细菌(PGPR)的概念、研究手段、基因标记技术和荧光原位杂交技术在研究棉花根际促生细菌中的应用.植物根系可以分泌各种对微生物有益的物质,吸引微生物在根际的聚集.棉花凝集素对根际促生细菌菌株的胞外多糖具有凝集作用,在棉花根际促生细菌与棉花根部相互识别过程中具有重要作用,可以利用棉花凝集素作为筛选工具筛选对棉花具有促生作用的根际促生细菌菌株.基因标记技术证明棉花根际促生细菌能高密度地定殖在棉花根部,对棉花的生长起促进作用,并能抑制某些植物病原菌及根际有害微生物.分子生物学技术在微生物生态学领域的应用促进了棉花根际促生细菌的研究和应用,可以利用棉花根际促生细菌研发微生物肥料.     

植物根际沉积与土壤微生物关系研究进展

【目的】活跃的根际微生物被喻为植物的第二套基因组,在植物的生长发育过程中发挥着关键作用。植物通过根际碳沉积影响根际土壤微生物群落的结构和功能;作为根际微生态系统中的物质流、能量流和信息流,根际碳沉积是连接大气、植物和土壤系统物质循环的重要纽带;因此,理解根际碳沉积在根际微生态中的作用对于提高植物抗逆性,增加作物产量,调控根际养分循环等方面具有重大的理论意义。【主要进展】本文就近年来关于根际微生物领域的研究成果,重点综述了根际微生物多样性和组学研究;根际碳沉积的组成和产生机理;根际微生物群落结构的形成机制;根际微生物在促进作物养分吸收、提高作物抗逆性等方面的生态功能;以及气候变化和长期施肥对植物-微生物互作关系的影响。在此基础上我们提出了未来可能的研究重点和发展方向:1)植物根际沉积物原位收集方法和检测技术的改进和发展;2)稳定同位素探针与分子生态学技术的结合,将植物、土壤和微生物三者有机地联系起来,综合分析根际界面中微生物的活性与功能;3)高通量测序、组学技术和生物信息学等新技术的引入势必使根际微生物学研究发生革命性的变化;4)随着全球气候变化和土壤肥力改变,例如全球变暖、CO2浓度升高和长期施用化肥,根际沉积物在植物-土壤-微生物中的分配与调节机制,以及这种环境选择压力下植物如何诱导根际促生菌发挥更大作用。希望通过平衡作物与微生物之间的相互关系来实现作物的高产高效,促进农田的可持续利用。     

多氯联苯污染土壤植物修复的机理、遗传缺陷及转基因技术

综述了多氯联苯污染土壤植物修复研究的主要进展,包括植物提取、植物转化和根际效应等方面的修复机理,自然植物及其根际微生物在多氯联苯污染修复功能方面存在的遗传缺陷,采用转基因技术对植物和根际微生物的修复功能进行遗传改造。同时对相关研究进行了评述,探讨了今后的发展趋势和重要研究方向。     

污染土壤植物修复技术研究进展

综述了国内外污染土壤植物修复技术研究进展 ,植物修复是利用某些植物对土壤重金属的超量吸收挥发以及对土壤中有机污染物降解等特殊功能 ,并与根际微生物协同作用 ,原位修复污染土壤的方法 ,费用低 ,效果显著 ,环境友好 ,是极具发展潜力的“绿色产业”。     

植物对污染土壤修复作用的研究进展

利用植物修复污染土壤是一种被人们认为安全可靠的方法.植物修复技术不仅能修复被石油污染的土壤,而且对更多品种污染的土壤修复有效,植物降解高分子有毒化合物的基础是根际环境及根际微生物,与无植物土壤不同.对根际区微生物降解和转化有机化合物的研究,更多的集中于植物对杀虫剂和除草剂的降解.事实证明,生物修复污染土壤是一项实用性和有效性很强的技术.     

砷污染土壤的生物修复研究进展

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.     

重金属污染土壤间作修复的研究进展

种植单一的超富集植物修复重金属污染土壤,不但中断农业生产导致经济收益降低,而且因生物量较低、修复周期长等诸多弊端导致修复效果不甚理想。间作作为一种传统的农艺管理方式,利用生态位和生物多样性原理等能提高农作物对资源的有效利用,对共植的农作物种类增量提质。在中、轻度污染土壤修复中利用间作体系,通过调控超富集植物与农作物的生长发育,促进超富集植物根系低分子量有机酸(LMWOAs)的分泌,降低其根际土壤p H,增加重金属活性,从而增加超富集植物对重金属的吸收,同时抑制农作物根系LMWOAs的分泌,以减少农作物对重金属的吸收,提高其产量和品质,实现"边生产边修复",提高土地利用率,并增加经济效益。本文根据近几年来国内外相关文献,综述了间作条件下超富集植物和农作物生物量、生理生化响应、重金属吸收、转运、富集等方面的变化,以及间作对土壤环境质量的影响,并对间作修复重金属污染土壤领域的发展趋势,如超富集植物和农作物间作的信号转导和分子生物学机制、间作体系下两类植物根际微生物类群的差异及其功能机制,以及构建高效间作体系提高重金属污染土壤的修复效率等方面进行了展望。     

抗镉并且产吲哚乙酸的细菌的筛选鉴定及其植物促生作用

植物促生长细菌（plant growth-promoting bacteria,PGPB）在植物修复重金属污染土壤的过程中能够有助于植物生长,从而提高植物的重金属污染土壤的修复能力。作为在重金属污染环境中应用的PGPB首先必须具有重金属抗性。镉是一种毒性很高的重金属,也是常见的环境污染因子之一。在植物中,镉抑制根和茎的生长,影响营养吸收和内环境稳定。现已知的PGPB的作用机制之一是产生植物生长激素如吲哚乙酸（indole acetic acid,IAA）和铁载体（siderophore）。本研究从土壤中筛选获得5株具有镉抗性（〉1.55 mmol/L）且产IAA和铁载体的细菌,这5株菌被编号为DJY、TK-2、TK-6、WM-1、PZ-23。在含镉培养基上,所有5种菌对芥菜根均有不同程度的促生长作用,其中TK-2对芥菜幼苗根萌发和下胚轴延伸的促进效果最为显著;促生效应并不由单一因素决定的,而是多种促生因素的统一协调作用的结果。     

内生细菌强化重金属污染土壤植物修复研究进展

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.     

印度芥菜(Brassica juncea L.)重金属耐性机理研究进展

印度芥菜可富集/忍耐Cd、Zn 等多种重金属, 是研究植物修复技术的一种模式植物。高浓度的重金属离子会改变植物的基因表达、细胞形态、细胞结构, 最终使植物生长受抑, 甚至死亡。印度芥菜高效的抗氧化系统、损伤修复系统以及对重金属的螯合、区域化可部分解除重金属的毒性, 缓解重金属离子的毒害作用。利用基因工程技术在印度芥菜中导入重金属耐性及运输相关基因可大幅度提高其重金属富集能力, 在重金属污染修复方面具有广阔的应用前景。     

香薷属植物在重金属修复中的应用进展

香薷属植物应用于重金属修复经历了矿区植物资源调查和比较、室内模拟研究、田间规模修复以及修复后处置研究,已经初步形成一个植物修复技术的完整体系。在现有技术条件下,把生态修复模式、品种驯化及诱导剂"配方"应用到香薷属植物修复土壤重金属污染对提高修复效率具有重要意义。     

蚯蚓在植物修复重金属污染土壤中的应用前景

重金属污染土壤的植物修复技术是绿色生物技术,该技术的应用受制于两个主要因素:超积累植物生物量小和土壤中重金属有效性低。本文在收集大量资料基础上,论述了蚯蚓与重金属的相互关系:重金属对蚯蚓的毒理效应和蚯蚓对重金属的忍耐力。根据在重金属污染土壤中,蚯蚓活动能提高植物生物量和土壤中的重金属的生物有效性,论证了在重金属污染土壤植物修复技术中引入蚯蚓的可行性,并指出引入蚯蚓的植物修复技术当前的研究热点及今后的研究方向。     

Advances in fungal-assisted phytoremediation of heavy metals: A review

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.     

Plant Growth-Promoting Rhizobacteria (PGPR) and Phosphorus Fertilizer-Assisted Phytoextraction of Toxic Heavy Metals from Contaminated Soils

Phytoremediation is a remediation technique that involves the use of plants to extract, sequester, and/or detoxify pollutants through physical, chemical, and biological processes. The use of phytoremediation is expanding due to its cost-effectiveness compared with conventional methods. This study was conducted to investigate the effects of autumn and spring application of plant growth-promoting rhizobacteria (PGPR, 10⁸ cfu mL^?1 Bacillus megaterium var. phosphaticum sprayed at 250 mL plot^?1) and phosphorus (P) fertilizer (0, 11, 22, 33, 44 kg P ha^?1) on dry matter yield and heavy metal uptake by plants in soils contaminated with heavy metals. Field experiments were conducted using a randomized complete block design with four replications between 2004 and 2007. The results of the study indicated that P fertilization, but not PGPR application, significantly affected dry matter yield. Application of PGPR increased heavy metal availability in soils and the heavy metal uptake of meadow plants. The heavy metal content of the meadow plants resulting from PGPR application was 4–6 times higher for the spring application than the autumn application. Approximately 16, 30, 10, 10, and 3 growing seasons without PGPR are necessary to remove all lead (Pb), nickel (Ni), boron (B), manganese (Mn), and zinc (Zn), respectively, from polluted soil. The time required for Pb, Ni, B, Mn, and Zn removal could be further decreased to approximately 4, 6, 3, 3, and 1 growing seasons, respectively, with 33 kg phosphorus pentoxide (P₂O₅) ha^?1 and 10⁸ cfu mL^?1 PGPR applications at rates of 250 mL plot^?1 in the spring season.     

抗重金属植物根际细菌的植物促生长特征以及它们对黑芥种子萌发的影响

Phytoremediation is an emerging technology that uses plants and their associated microbes to clean up pollutants from the soil, water, and air. In order to select the plant growth-promoting rhizobacteria(PGPR) for phytoremediation of heavy metal contamination, 60 bacterial strains were isolated from the rhizosphere of two endemic plants, Prosopis laevigata and Spharealcea angustifolia, in a heavy metal-contaminated zone in Mexico. These rhizobacterial strains were characterized for the growth at different pH and salinity, extracellular enzyme production, solubilization of phosphate, heavy metal resistance, and plant growth-promoting(PGP) traits, including production of siderophores and indol-3-acetic acid(IAA). Overall, the obtained rhizobacteria presented multiple PGP traits. These rhizobacteria were also resistant to high levels of heavy metals(including As as a metalloid)(up to 480 mmol L(-1)As(V), 24 mmol L(-1)Pb(Ⅱ), 21 mmol L(-1)Cu(Ⅱ), and 4.5 mmol L(-1)Zn(Ⅱ)). Seven rhizobacterial strains with the best PGP traits were identified as members of Alcaligenes, Bacillus, Curtobacterium, and Microbacterium, and were selected for further bioassay.The inoculation of Brassica nigra seeds with Microbacterium sp. CE3R2, Microbacterium sp. NE1R5, Curtobacterium sp. NM1R1,and Microbacterium sp. NM3E9 facilitated the root development; they significantly improved the B. nigra seed germination and root growth in the presence of heavy metals such as 2.2 mmol L(-1)Zn(Ⅱ). The rhizobacterial strains isolated in the present study had the potential to be used as efficient bioinoculants in phytorremediation of soils contaminated with multiple heavy metals.     

Spent mushroom compost enhances plant response and phytoremediation of heavy metal polluted soil

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.     

香薷植物修复铜污染土壤的研究进展

土壤铜污染有自然来源和人为来源。铜污染土壤中有机质、Fe／Al氧化物对铜的专性吸附，是影响土壤中铜生物有效性的主要因素。近年来，我国原生植物修复材料如海州香薷、鸭跖草、酸模、紫花香薷在国内铜污染土壤的研究中得到广泛应用。其中．采用海州香薷开展铜污染土壤植物修复机理和修复技术的研究，已从实验室水培、盆栽试验的生长反应特性、耐及解铜毒的生理生化反应，进展到室外大田修复的示范工程及技术推广阶段。紫花香薷在重金属复合污染土壤上，也有修复前景。开展植物修复材料的产后处置研究，综合利用和深加工，增大植物修复材料价值，对加强植物修复工程的示范和推广步伐，有重要意义。     

Stabilization of tannery sludge amended soil using Ricinus communis,Brassica juncea and Nerium oleander

Purpose

Characterization of tannery sludge (TS) for its plausible use in amelioration and phytoremediation of heavy metal rich TS treated soil by growing economically important plants (Ricinus communis, Brassica juncea and Nerium oleander).

Materials and methods

Treatments were prepared by amalgamation of TS (0, 5, 10, 20, 30, 50, 75, 100 %) with garden soil (GS). All treatments were analysed for chemical properties, total and DTPA (Diethylene triamine pentaacetic acid) extractable heavy metals (Cr, Pb, Cu, and Mn). Seed germination experiment was conducted; unvarying saplings were selected and planted in concerned pots and allowed to grow for 90 days in green house. At harvest, plant samples were washed with distilled water and used for determination of growth parameters (biomass of root, shoot and total biomass on dry weight basis) and metal accumulation in different parts of the plant. Translocation factor (TF) and bioconcentration factor (BCF) have been calculated to check the phytostabilization capability of studied plants.

Results and discussion

Application of TS in fixed quantity as an amendment resulted in significant improvements of GS characteristics (alkaline pH with high electrical conductivity, organic carbon, available NPK and heavy metals) and in treatments. DTPA extractable heavy metal concentrations were found very low and total heavy metal concentrations were also found under allowable range in control and treated soil (T-I to T-VI). The maximum seed germination percentage, plant growth, biomass production for all plant species were observed in T-III treatment (20 % TS + 80 % GS) with majority of the metal accumulation in underground part (BCF >1) and meagre translocation in aerial part (TF <1). From T-IV to T-VII treatment, accumulation of heavy metals in plant parts has generally increased; however, biomass has been tremendously decreased.

Conclusions

TS was found rich in NPK content with significant concentration of heavy metals. Pot growth experiment suggested amelioration of GS with specific quantity of 20 % TS can tremendously enhance the plant growth, help in the utilization of TS and can act as a substitute of synthetic fertilizer. Majority of the metals was accumulated in root part (BCF >1) and meagre translocation (TF <1) in aerial part, concludes R. communis and B. juncea could be suitable plant species to be grown in heavy metal rich TS treated soil, vis-à-vis for phytostabilization of heavy metals. In addition, these oil yielding and medicinal plants can also be used for phytoremediation of moderately contaminated tannery soils.