几种生态因素对西北干旱地区豆科植物结瘤固氮的影响

通过对西北干旱地区栽培和野生豆科植物不同环境条件固氮状况的调查表明,栽培豆科植物一般能自然结瘤,野生豆科植物种的结瘤率极低。根瘤颜色栽培植物多为粉红色,而野生植物多为白色、黄色或棕色。通过对水分、光照强度和温度等不同条件下根瘤ARA测定,表明根瘤固氮活性与生态条件关系密切,而土壤水分是限制根瘤固氮活性表达的主要因素。     

根瘤菌共生固氮能力的进化模式

根瘤菌-豆科植物共生固氮体系对农业的可持续性发展至关重要,也是研究原核与真核生物互利共生的模式体系之一。长期以来,根瘤菌共生固氮相关研究主要集中在结瘤因子与固氮酶合成及调控等少数关键基因,但仅获得这些关键基因却不能保证细菌获得结瘤固氮能力。随着比较和功能基因组学的快速发展和应用,越来越多的研究发现根瘤菌使用了很多系统发育分支特异的遗传机制与豆科植物建立有效的共生关系,进一步揭示了双方互利共生的复杂性。本综述总结了近年来比较基因组学、遗传学以及实验进化等方面的相关研究进展,在此基础上讨论根瘤菌共生固氮能力的进化模式。     

湿润持续时间对生物土壤结皮固氮活性的影响

土壤可利用氮是干旱半干旱区生态系统中除水分之外的关键限制因子,研究湿润持续时间和温度变化对温性荒漠藻类结皮和藓类结皮固氮活性的影响,对于深入认识和准确评价全球变化大背景下生物土壤结皮对区域生态系统的氮贡献至关重要。通过野外调查采样,在一次较大降水事件发生后,利用开顶式生长室,采用乙炔还原法连续测定了沙坡头地区人工植被区和天然植被区两类典型生物土壤结皮固氮活性的变化,分析了湿润持续时间和模拟增温对其固氮活性的影响。研究结果表明:在经历31d持续干旱,降水发生后第4天两类结皮的固氮活性达到最大,此后随样品水分含量下降,至第10天其固氮活性将至最低;结皮固氮活性与水分含量之间呈显著的二次函数关系,其固氮活性随水分含量的增加呈先上升后下降的趋势,藻类结皮的固氮活性显著高于藓类结皮;短期模拟增温并不能显著提高其固氮活性,增温主要通过加速结皮水分散失来影响其固氮活性。上述结果反映了水分是控制生物土壤结皮固氮活性的关键因子,而实验前样品所经历的环境条件则决定了降水发生后其到达最大固氮速率的时间,野外长期观测结合控制严格的室内实验才能准确评价生物土壤结皮对区域生态系统的氮贡献。     

一氧化氮对豆科植物结瘤及固氮的影响机制

豆科植物-根瘤菌共生过程受双方基因复杂且精细的调控, 能够产生特异的根瘤结构并可将大气中的惰性氮气(N₂)转化为可被植物直接利用的氨态氮。结瘤与固氮受多种因素影响, 其中, 一氧化氮(NO)作为一种自由基反应性气体信号分子, 可参与调节植物的许多生长发育过程, 如植物的呼吸、光形态建成、种子萌发、组织和器官发育、衰老以及响应各种生物及非生物胁迫。在豆科植物中, NO不仅影响寄主与菌共生关系的建立, 还参与调控根瘤菌对氮气的固定并提高植株氮素营养利用效率。该文主要从豆科植物及共生菌内NO的产生、降解及其对结瘤、共生固氮的影响和对环境胁迫的响应, 阐述了NO调控豆科植物共生体系中根瘤形成和共生固氮过程的作用机制, 展望了NO信号分子在豆科植物共生固氮体系中的研究前景。     

泛析提高共生固氮效率

泛析提高共生固氮效率徐秀华（辽宁省农业管理干部学院,沈阳１１０１６１）当前人们对共生固氮效率与豆科植物种类、根瘤菌品系、固氮环境的关系已具有深刻的认识。值得探讨的是如何深入地发掘共生固氮潜力,提高共生固氮效率,为创造真正的＂绿色食品＂开拓门路。一共生...     

共生固氮体系中的豆科植物基因

豆科根瘤菌发现的近百年历史以来,共生固氮作用一直受到人们的瞩目。近廿几年来对根痛瘤—豆科植物共生体的研究进展迅速,对共生体中根瘤菌本身的固氮基因(nif)和结瘤基因的编码、定位等有了较深入的了解。然而,共生体系中基因的调控是比较复杂的,环境因素和寄生植物基因对共生固氮的调控也起着重要作用。人们对豆科寄主结瘤和固氮遗传进行了一系列研究,并力图选育高固氮的豆科品种资源。本文仅就豆科植物—根瘤菌共生固氮体系中寄主植物基因及它在共生固氮体系研究中的作用和意义作简要的概述。     

豆科植物SHR-SCR模块——根瘤“奠基细胞”的命运推手

豆科植物-根瘤菌共生固氮是可持续性农业氮肥的最重要来源。根瘤作为豆科植物共生固氮的一种特化植物侧生器官, 提供了根瘤菌生物固氮必需的微环境, 是根瘤菌的安身之本, 因此, 根瘤的正常发育是实现豆科植物-根瘤菌共生固氮的结构基础。根瘤器官的从头发生主要起始于根瘤菌诱导的根皮层细胞分裂。通常认为豆科植物的根皮层具备有别于非豆科植物根皮层的某种特异属性, 从而响应根瘤菌并与之建立固氮共生, 但长期以来该属性决定的分子机制一直不明确。近日, 中国科学院分子植物科学卓越创新中心王二涛团队以蒺藜苜蓿(Medicago truncatula)等豆科植物和拟南芥(Arabidopsis thaliana)等非豆科植物为研究对象, 发现豆科植物中保守的SHR-SCR干细胞模块决定了其皮层细胞分裂潜能从而赋予根瘤器官发生的命运。该研究揭示了豆科植物根瘤发育的全新机制, 提供了研究和理解植物-根瘤菌固氮共生进化的重要线索, 对提高豆科作物固氮效率和非豆科作物固氮工程具有重要意义。     

根瘤菌-豆科植物共生体系在重金属污染环境修复中的地位、应用及潜力

土壤重金属污染严重影响了人类健康和生态系统稳定,已成为亟待解决的现实问题。在重金属污染地,氮素的极端不足是植被恢复主要限制因子之一。根瘤菌-豆科植物共生体系是固氮能力最强的生物固氮体系,在促进重金属污染地氮素循化和营养元素积累中具有重要作用。本文阐述土壤重金属污染的修复方法及其特点,微生物抗重金属的机理及促植物生长和重金属积累的特性,根瘤菌-豆科植物共生体系在土壤重金属污染修复中的优越性,研究现状及应用潜力。提出应用"豆科植物-根瘤菌共生体系"修复重金属污染土壤的新思路和新任务。     

非豆科固氮树种-沙棘与微生物联合共生体的纯培养研究

Ｆｒａｎｋｉａ 非豆科树木共生固氮体系是自然界中重要的固氮生物资源 ,具有与Ｒｈｉｚｏｂｉｕｍ 豆科植物相似的固氮能力 ,在自然界能量循环和生态平衡中起着重要作用 ,而且与形成共生固氮的非豆科植物其抗逆性强 ,耐干旱、盐碱 ,抗高寒、瘠薄 ,能在一般豆科植物不能生长的环境下正常生长结瘤固氮。非豆科固氮树种 沙棘是三北地区重要垦荒先锋树种1) ,其果实富含多种维生素 ,具有重要的经济开发价值。同时 ,沙棘又是具有内生菌根真菌的固氮树种[1] 。本文通过对沙棘菌根、根瘤联合共生体人工构建技术以及沙棘联合共生的增效作用的研究 ,…     

豆科植物共生结瘤的分子基础和调控研究进展

豆科植物与根瘤菌共生互作的结果导致了一个新的植物器官——根瘤的形成,根瘤菌生活在根瘤中,它们具有将氮气转化为能被植物同化的氨的能力。该文阐述了根瘤的形成过程和类型,并主要以模式豆科植物蒺藜苜蓿(Medicago truncatula)和日本百脉根(Lotus japonicus)为例,对近年来共生结瘤过程中宿主植物对根瘤菌结瘤因子的识别和信号传递、侵入线形成和固氮的分子基础,以及宿主植物对根瘤形成的自主调控机制、环境中氮素营养对结瘤的影响研究进行了综述,指出当前豆科植物与根瘤菌共生互作研究存在的问题,并对今后的研究方向作了分析与展望。     

植物的血红蛋白

近几年来,植物血红蛋白的研究进展十分迅速,豆科植物中与共生固氮无关的血红蛋白基因和包括禾本科植物在内的许多非豆科植物血红蛋白基因的发现使人们对植物血红蛋白有了新的认识,进而把植物血红蛋白分为共生血红蛋白和非共生血红蛋白两种类型。对这两种血红蛋白的性质、功能、基因结构及表达等方面的研究不仅对共生固氮中植物与微生物的相互关系和固氮工程研究;而且对植物细胞的呼吸代谢和耐涝机理等研究有重要价值。     

Rhizobium-Legume Symbiosis and Nitrogen Fixation under Severe Conditions and in an Arid Climate

Biological N₂ fixation represents the major source of N input in agricultural soils including those in arid regions. The major N₂-fixing systems are the symbiotic systems, which can play a significant role in improving the fertility and productivity of low-N soils. The Rhizobium-legume symbioses have received most attention and have been examined extensively. The behavior of some N₂-fixing systems under severe environmental conditions such as salt stress, drought stress, acidity, alkalinity, nutrient deficiency, fertilizers, heavy metals, and pesticides is reviewed. These major stress factors suppress the growth and symbiotic characteristics of most rhizobia; however, several strains, distributed among various species of rhizobia, are tolerant to stress effects. Some strains of rhizobia form effective (N₂-fixing) symbioses with their host legumes under salt, heat, and acid stresses, and can sometimes do so under the effect of heavy metals. Reclamation and improvement of the fertility of arid lands by application of organic (manure and sewage sludge) and inorganic (synthetic) fertilizers are expensive and can be a source of pollution. The Rhizobium-legume (herb or tree) symbiosis is suggested to be the ideal solution to the improvement of soil fertility and the rehabilitation of arid lands and is an important direction for future research.     

Effectiveness of nitrogen fixation in rhizobia

Biological nitrogen fixation in rhizobia occurs primarily in root or stem nodules and is induced by the bacteria present in legume plants. This symbiotic process has fascinated researchers for over a century, and the positive effects of legumes on soils and their food and feed value have been recognized for thousands of years. Symbiotic nitrogen fixation uses solar energy to reduce the inert N₂ gas to ammonia at normal temperature and pressure, and is thus today, especially, important for sustainable food production. Increased productivity through improved effectiveness of the process is seen as a major research and development goal. The interaction between rhizobia and their legume hosts has thus been dissected at agronomic, plant physiological, microbiological and molecular levels to produce ample information about processes involved, but identification of major bottlenecks regarding efficiency of nitrogen fixation has proven to be complex. We review processes and results that contributed to the current understanding of this fascinating system, with focus on effectiveness of nitrogen fixation in rhizobia.     

Phytoremediation of Heavy and Transition Metals Aided by Legume-Rhizobia Symbiosis

Legumes are important for nitrogen cycling in the environment and agriculture due to the ability of nitrogen fixation by rhizobia. In this review, we introduce an important and potential role of legume-rhizobia symbiosis in aiding phytoremediation of some metal contaminated soils as various legumes have been found to be the dominant plant species in metal contaminated areas. Resistant rhizobia used for phytoremediation could act on metals directly by chelation, precipitation, transformation, biosorption and accumulation. Moreover, the plant growth promoting (PGP) traits of rhizobia including nitrogen fixation, phosphorus solubilization, phytohormone synthesis, siderophore release, and production of ACC deaminase and the volatile compounds of acetoin and 2, 3-butanediol may facilitate legume growth while lessening metal toxicity. The benefits of using legumes inoculated with naturally resistant rhizobia or recombinant rhizobia with enhanced resistance, as well as co-inoculation with other plant growth promoting bacteria (PGPB) are discussed. However, the legume-rhizobia symbiosis appears to be sensitive to metals, and the effect of metal toxicity on the interaction between legumes and rhizobia is not clear. Therefore, to obtain the maximum benefits from legumes assisted by rhizobia for phytoremediation of metals, it is critical to have a good understanding of interactions between PGP traits, the symbiotic plant-rhizobia relationship and metals.     

Nodulation and nitrogen fixation in extreme environments

Biological nitrogen fixation is a phenomenon occurring in all known ecosystems. Symbiotic nitrogen fixation is dependent on the host plant genotype, theRhizobium strain, and the interaction of these symbionts with the pedoclimatic factors and the environmental conditions. Extremes of pH affect nodulation by reducing the colonization of soil and the legume rhizosphere by rhizobia. Highly acidic soils (pH<4.0) frequently have low levels of phosphorus, calcium, and molybdenum and high concentrations of aluminium and manganese which are often toxic for both partners; nodulation is more affected than host-plant growth and nitrogen fixation. Highly alkaline soils (pH>8.0) tend to be high in sodium chloride, bicarbonate, and borate, and are often associated with high salinity which reduce nitrogen fixation. Nodulation and N-fixation are observed under a wide range of temperatures with optima between 20–30°C. Elevated temperatures may delay nodule initiation and development, and interfere with nodule structure and functioning in temperate Iegumes, whereas in tropical legumes nitrogen fixation efficiency is mainly affected. Furthermore, temperature changes affect the competitive ability ofRhizobium strains. Low temperatures reduce nodule formation and nitrogen fixation in temperate legumes; however, in the extreme environment of the high arctic, native legumes can nodulate and fix nitrogen at rates comparable to those observed with legumes in temperate climates, indicating that both the plants and their rhizobia have successfully adapted to arctic conditions. In addition to low temperatures, arctic legumes are exposed to a short growing season, a long photoperiod, low precipitation and low soil nitrogen levels. In this review, we present results on a number of structural and physiological characteristics which allow arctic legumes to function in extreme environments.     

Improvement of symbiotic nitrogen fixation in plants: molecular-genetic approaches and evolutionary models

Efficiency of symbiotic nitrogen fixation in legumes depends on bringing together the processes of N₂ fixation, assimilation of its products, supply of nitrogenase with energy, and development of nodule tissue and cellular structures. Coordination of these processes could arise from the evolutionary old functions of the nodules associated with deposition of the products of photosynthesis governed by systemic signals traveling between the above-ground organs and the roots. Further increase in symbiotic efficiency was associated with a pronounced ability to fix N₂ by intracellular bacteroids that lost capability to propagate (as observed in galegoid legumes from the tribes Viciae, Trifolieae, and Galegae producing indeterminate nodules). However, efficiency of these symbioses is restricted by a slow removal from the nodules of the products of N₂ fixation, which are assimilated along the same amide pathway as nitrogen compounds arriving from the soil. In legumes from the tribe Phaseoleae, such a restriction was overcome owing to a particular way of nitrogen assimilation via its incorporation into ureides (in determinate nodules). Development of symbioses where specialization of bacteroids in symbiotic fixation of atmospheric nitrogen is combined with its ureide assimilation will make it possible to produce new forms of plants highly efficient in symbiotic nitrogen fixation.     

Impacts of fly-ash on soil and plant responses

Coal combustion produces carbon dioxides, SOx, NOx and a variety of byproducts, including fly-ash, flue gas and scrubber sludge. Fly-ash consists of minute glass-like particles and its deposition on leaves inhibits the normal transpiration and photosynthesis of plants. Fly-ash also affects the physicochemical characteristics of soil because it is generally very basic, rich in various essential and non-essential elements, but poor in both nitrogen and available phosphorus. The massive fly-ash materials have been a potential resource for the agricultural activities as well as the other industrial purposes. Practical value of fly-ash in agriculture as an 'effective and safe' fertiliser or soil amendment can be established after repeated field experiments. Here remains to be disclosed the biological processes and interactions due to 'lack and excess' of the fly-ash exposures along with abiotic and biotic factors. These may involve the symbiotic fixation of nitrogen and the biological extraction of metals following immobilisation of toxic heavy metal ions, as well as other neutralisation and equilibration processes during weathering. Nitrogen-fixing plants with an apparent heavy metal-tolerance can be helpful as the early colonisers of fly-ash dumps and nearby areas. Electronic Publication     

Biological nitrogen fixation for sustainable agriculture: A perspective

The economic and environmental costs of the heavy use of chemical N fertilizers in agriculture are a global concern. Sustainability considerations mandate that alternatives to N fertilizers must be urgently sought. Biological nitrogen fixation (BNF), a microbiological process which converts atmospheric nitrogen into a plant-usable form, offers this alternative. Nitrogen-fixing systems offer an economically attractive and ecologically sound means of reducing external inputs and improving internal resources. Symbiotic systems such as that of legumes and Rhizobium can be a major source of N in most cropping systems and that of Azolla and Anabaena can be of particular value to flooded rice crop. Nitrogen fixation by associative and free-living microorganisms can also be important. However, scientific and socio-cultural constraints limit the utilization of BNF systems in agriculture. While several environmental factors that affect BNF have been studied, uncertainties still remain on how organisms respond to a given situation. In the case of legumes, ecological models that predict the likelihood and the magnitude of response to rhizobial inoculation are now becoming available. Molecular biology has made it possible to introduce choice attributes into nitrogen-fixing organisms but limited knowledge on how they interact with the environment makes it difficult to tailor organisms to order. The difficulty in detecting introduced organisms in the field is still a major obstacle to assessing the success or failure of inoculation. Production-level problems and socio-cultural factors also limit the integration of BNF systems into actual farming situations. Maximum benefit can be realized only through analysis and resolution of major constraints to BNF performance in the field and adoption and use of the technology by farmers.