Efeitos da toxicidade por metais pesados em Rhizobium leguminosarum bv. trifolii: diversidade e resposta de população isoladas de uma mina de chumbo

Nas últimas décadas verificou-se um aumento da contaminação dos solos com metais pesados resultante de processos antropogénicos. As descargas de efluentes industriais, a actividade mineira e a aplicação de lamas residuais e de fertilizantes são as principais fontes de metais pesados. Em certas regiões, a acumulação destes elementos nos solos tem atingido níveis preocupantes para o equilíbrio dos ecossistemas. Vários estudos têm demonstrado que os metais influenciam os microrganismos afectando adversamente o seu crescimento, morfologia e actividades bioquímicas resultando num decréscimo da biomassa e diversidade. Entre os microrganismos do solo, as bactérias pertencentes ao género Rhizobium têm um elevado interesse científico, económico e ecológico devido à sua capacidade para fixar azoto. Deste modo, o trabalho desenvolvido ao longo desta tese incidiu sobre o efeito da toxicidade imposta pelos metais nas bactérias fixadoras de azoto, em particular em Rhizobium leguminosarum bv. trifolii e teve como principais objectivos: determinar o efeito dos metais pesados na sobrevivência e na capacidade de fixar azoto dos isolados de rizóbio; avaliar a influência dos metais na diversidade das populações de rizóbio isoladas de solos contaminados; determinar os níveis de tolerância do rizóbio a diferentes metais e analisar a resposta ao stresse oxidativo imposto pelo cádmio. A Mina do Braçal foi o local de estudo escolhido uma vez que os seus solos estão muito contaminados com metais em resultado da extracção de minério durante mais de 100 anos. Foram escolhidos 3 solos com diferentes graus de contaminação, o solo BC com concentrações reduzidas de metais, escolhido por estar numa zona já fora da mina e designado por solo controlo e os solos BD e BA considerados medianamente e muito contaminados, respectivamente. O Pb e o Cd foram os metais predominantes nestes solos, assim como o metalóide As, cujas concentrações ultrapassaram largamente os limites previstos na lei. Sendo as enzimas do solo boas indicadoras da qualidade do mesmo, foi determinada a actividade de algumas como a desidrogenase (DHA) e a catalase (CAT). Ambas as enzimas correlacionaramse negativamente com as concentrações de metais nos solos. A dimensão das populações indígenas de rizóbio nos solos contaminados (BD e BA) foi bastante baixa, 9,1 bactérias g-1 de solo e 7,3 bactérias g-1 de solo, respectivamente, quando em comparação com a população do solo BC (4,24x104 bactérias g-1 de solo). Estes resultados parecem estar relacionados com o elevado conteúdo em metais e com o pH ácido dos solos. A capacidade simbiótica também foi afectada pela presença de metais, uma vez que os isolados originários do solo BD mostraram menor capacidade em fixar azoto do que os isolados do solo controlo. A diversidade das populações de rizóbio foi determinada com recurso à análise dos perfis de plasmídeos, perfis de REP e ERIC-PCR de DNA genómico e perfis de proteínas e lipopolissacarídeos. No conjunto dos 35 isolados analisados foram identificados 11 plasmídeos com pesos moleculares entre 669 kb e 56 kb. Embora a incidência de plasmídeos tenha sido superior nos isolados do solo BC verificou-se maior diversidade plasmídica na população isolada do solo BD. Resultados similares foram obtidos com os perfis de REP e ERIC-PCR e perfis de proteínas, que indicaram maior diversidade nas populações dos solos contaminados (BD e BA), contrariamente ao verificado por outros autores. O grau de tolerância aos metais pesados e ao arsénio dos vários isolados testados dependeu do metal e do local de origem. No geral, os isolados do solo BD mostraram maior tolerância aos metais do que os isolados do solo controlo, o que está de acordo com o esperado uma vez que geralmente as populações dos locais contaminados são mais tolerantes. Contudo, os isolados do local mais contaminado (BA) foram muito tolerantes apenas ao chumbo mostrando-se sensíveis aos restantes metais. A inoculação dos solos BC, BD e BA após irradiação com estirpes seleccionadas de rizóbio permitiu avaliar a sua sobrevivência ao longo de 12 meses em condições mais realistas. Verificou-se que após um decréscimo inicial, os isolados inoculados no solo BC conseguiram recuperar a dimensão das suas populações para números similares aos inicialmente introduzidos, contrariamente ao verificado no solo BD onde o número de rizóbios decresceu ao longo dos 12 meses. As condições adversas do solo BA apenas permitiram a sobrevivência de 4 isolados até aos 3 meses e apenas dois deles conseguiram sobreviver após 12 meses, designadamente C 3-1 e A 17-3. Estes isolados possuem um plasmídeo de 669 kb que poderá estar na base da sobrevivência destas estirpes. Por outro lado, o último isolado é originário do solo contaminado e por isso estará também mais adaptado a sobreviver às elevadas concentrações de Pb existentes no solo BA. Por fim, constatou-se que o cádmio, um dos metais presente em concentrações mais elevadas nos solos em estudo, é um indutor de stresse oxidativo nos isolados de rizóbio menos tolerantes o que foi confirmado pelo aumento de ROS e danos celulares ao nível dos lípidos.

Transcriptomic analysis of rhizobium leguminosarum biovar viciae in symbiosis with host plants pisum sativum and Vicia cracca

Rhizobium leguminosarum bv. viciae forms nitrogen-fixing nodules on several legumes, including pea (Pisum sativum) and vetch (Vicia cracca), and has been widely used as a model to study nodule biochemistry. To understand the complex biochemical and developmental changes undergone by R. leguminosarum bv. viciae during bacteroid development, microarray experiments were first performed with cultured bacteria grown on a variety of carbon substrates (glucose, pyruvate, succinate, inositol, acetate, and acetoacetate) and then compared to bacteroids. Bacteroid metabolism is essentially that of dicarboxylate-grown cells (i.e., induction of dicarboxylate transport, gluconeogenesis and alanine synthesis, and repression of sugar utilization). The decarboxylating arm of the tricarboxylic acid cycle is highly induced, as is gamma-aminobutyrate metabolism, particularly in bacteroids from early (7-day) nodules. To investigate bacteroid development, gene expression in bacteroids was analyzed at 7, 15, and 21 days postinoculation of peas. This revealed that bacterial rRNA isolated from pea, but not vetch, is extensively processed in mature bacteroids. In early development (7 days), there were large changes in the expression of regulators, exported and cell surface molecules, multidrug exporters, and heat and cold shock proteins. fix genes were induced early but continued to increase in mature bacteroids, while nif genes were induced strongly in older bacteroids. Mutation of 37 genes that were strongly upregulated in mature bacteroids revealed that none were essential for nitrogen fixation. However, screening of 3,072 mini-Tn5 mutants on peas revealed previously uncharacterized genes essential for nitrogen fixation. These encoded a potential magnesium transporter, an AAA domain protein, and proteins involved in cytochrome synthesis.

In vivo expression technology (IVET) selection of genes of Rhizobium leguminosarum biovar viciae A34 expressed in the rhizosphere

IVET was used to identify genes that are specifically expressed in the rhizosphere of the pea-nodulating bacterium Rhizobium leguminosarum A34. A library of R. leguminosarum A34 cloned in the integration vector pIE1, with inserts upstream of a promoter-less purN:gfp:gusA, was conjugated into purN host RU2249 and recombined into the genome. After removal of colonies that expressed the reporter genes of the vector under laboratory conditions, the library was inoculated into a nonsterile pea rhizosphere. The key result is that 29 rhizosphere-induced loci were identified. Sequence analysis of these clones showed that a wide variety of R. leguminosarum A34 genes are expressed specifically in the rhizosphere including those encoding proteins involved in environmental sensing, control of gene expression, metabolic reactions and membrane transport. These genes are likely to be important for survival and colonization of the pea rhizosphere.

Arabinose and protocatechuate catabolism genes are important for growth of Rhizobium leguminosarum biovar viciae in the pea rhizosphere

Background and aims: To form nitrogen-fixing nodules on pea roots, Rhizobium leguminosarum biovar viciae must be competitive in the rhizosphere. Our aim was to identify genes important for rhizosphere fitness. Methods: Signature-tagged mutants were screened using microarrays to identify mutants reduced for growth in pea rhizospheres. Candidate mutants were assessed relative to controls for growth in minimal medium, growth in pea rhizospheres and for infection of peas in mixed inoculants. Mutated genes were identified by DNA sequencing and confirmed by transduction. Results: Of 5508 signature-tagged mutants, microarrays implicated 50 as having decreased rhizosphere fitness. Growth tests identified six mutants with rhizosphere-specific phenotypes. The mutation in one of the genes (araE) was in an arabinose catabolism operon and blocked growth on arabinose. The mutation in another gene (pcaM), encoding a predicted solute binding protein for protocatechuate and hydroxybenzoate uptake, decreased growth on protocatechuate. Both mutants were decreased for nodule infection competitiveness with mixed inoculants, but nodulated peas normally when inoculated alone. Other mutants with similar phenotypes had mutations predicted to affect secondary metabolism. Conclusions: Catabolism of arabinose and protocatechuate in the pea rhizosphere is important for competitiveness of R.l. viciae. Other genes predicted to be involved in secondary metabolism are also important.

Lipid A biosynthesis in Rhizobium leguminosarum: role of a 2-keto-3-deoxyoctulosonate-activated 4' phosphatase.

Lipid A from several strains of the N2-fixing bacterium Rhizobium leguminosarum displays significant structural differences from Escherichia coli lipid A, one of which is the complete absence of phosphate groups. However, the first seven enzymes of E. coli lipid A biosynthesis, leading from UDP-GlcNAc to the phosphorylated intermediate, 2-keto-3-deoxyoctulosonate (Kdo2)-lipid IVA, are present in R. leguminosarum. We now describe a membrane-bound phosphatase in R. leguminosarum extracts that removes the 4' phosphate of Kdo2-lipid IVA. The 4' phosphatase is selective for substrates containing the Kdo domain. It is present in extracts of R. leguminosarum biovars phaseoli, viciae, and trifolii but is not detectable in E. coli and Rhizobium meliloti. A nodulation-defective strain (24AR) of R. leguminosarum biovar trifolii, known to contain a 4' phosphatase residue on its lipid A, also lacks measurable 4' phosphatase activity. The Kdo-dependent 4' phosphatase appears to be a key reaction in a pathway for generating phosphate-deficient lipid A.

PGPRs and nitrogen-fixing legumes: a perfect team for efficient Cd phytoremediation?

Cadmium (Cd) is a toxic, biologically non-essential and highly mobile metal that has become an increasingly important environmental hazard to both wildlife and humans. In contrast to conventional remediation technologies, phytoremediation based on legume rhizobia symbiosis has emerged as an inexpensive decontamination alternative which also revitalize contaminated soils due to the role of legumes in nitrogen cycling. In recent years, there is a growing interest in understanding symbiotic legume rhizobia relationship and its interactions with Cd. The aim of the present review is to provide a comprehensive picture of the main effects of Cd in N-2-fixing leguminous plants and the benefits of exploiting this symbiosis together with plant growth promoting rhizobacteria to boost an efficient reclamation of Cd-contaminated soils.

Bioremediation of PAHs - Limitations and soultions

Introduction 1.1 Occurrence of polycyclic aromatic hydrocarbons (PAH) in the environment Worldwide industrial and agricultural developments have released a large number of natural and synthetic hazardous compounds into the environment due to careless waste disposal, illegal waste dumping and accidental spills. As a result, there are numerous sites in the world that require cleanup of soils and groundwater. Polycyclic aromatic hydrocarbons (PAHs) are one of the major groups of these contaminants (Da Silva et al., 2003). PAHs constitute a diverse class of organic compounds consisting of two or more aromatic rings with various structural configurations (Prabhu and Phale, 2003). Being a derivative of benzene, PAHs are thermodynamically stable. In addition, these chemicals tend to adhere to particle surfaces, such as soils, because of their low water solubility and strong hydrophobicity, and this results in greater persistence under natural conditions. This persistence coupled with their potential carcinogenicity makes PAHs problematic environmental contaminants (Cerniglia, 1992; Sutherland, 1992). PAHs are widely found in high concentrations at many industrial sites, particularly those associated with petroleum, gas production and wood preserving industries (Wilson and Jones, 1993). 1.2 Remediation technologies Conventional techniques used for the remediation of soil polluted with organic contaminants include excavation of the contaminated soil and disposal to a landfill or capping - containment - of the contaminated areas of a site. These methods have some drawbacks. The first method simply moves the contamination elsewhere and may create significant risks in the excavation, handling and transport of hazardous material. Additionally, it is very difficult and increasingly expensive to find new landfill sites for the final disposal of the material. The cap and containment method is only an interim solution since the contamination remains on site, requiring monitoring and maintenance of the isolation barriers long into the future, with all the associated costs and potential liability. A better approach than these traditional methods is to completely destroy the pollutants, if possible, or transform them into harmless substances. Some technologies that have been used are high-temperature incineration and various types of chemical decomposition (for example, base-catalyzed dechlorination, UV oxidation). However, these methods have significant disadvantages, principally their technological complexity, high cost , and the lack of public acceptance. Bioremediation, on the contrast, is a promising option for the complete removal and destruction of contaminants. 1.3 Bioremediation of PAH contaminated soil & groundwater Bioremediation is the use of living organisms, primarily microorganisms, to degrade or detoxify hazardous wastes into harmless substances such as carbon dioxide, water and cell biomass Most PAHs are biodegradable unter natural conditions (Da Silva et al., 2003; Meysami and Baheri, 2003) and bioremediation for cleanup of PAH wastes has been extensively studied at both laboratory and commercial levels- It has been implemented at a number of contaminated sites, including the cleanup of the Exxon Valdez oil spill in Prince William Sound, Alaska in 1989, the Mega Borg spill off the Texas coast in 1990 and the Burgan Oil Field, Kuwait in 1994 (Purwaningsih, 2002). Different strategies for PAH bioremediation, such as in situ , ex situ or on site bioremediation were developed in recent years. In situ bioremediation is a technique that is applied to soil and groundwater at the site without removing the contaminated soil or groundwater, based on the provision of optimum conditions for microbiological contaminant breakdown.. Ex situ bioremediation of PAHs, on the other hand, is a technique applied to soil and groundwater which has been removed from the site via excavation (soil) or pumping (water). Hazardous contaminants are converted in controlled bioreactors into harmless compounds in an efficient manner. 1.4 Bioavailability of PAH in the subsurface Frequently, PAH contamination in the environment is occurs as contaminants that are sorbed onto soilparticles rather than in phase (NAPL, non aqueous phase liquids). It is known that the biodegradation rate of most PAHs sorbed onto soil is far lower than rates measured in solution cultures of microorganisms with pure solid pollutants (Alexander and Scow, 1989; Hamaker, 1972). It is generally believed that only that fraction of PAHs dissolved in the solution can be metabolized by microorganisms in soil. The amount of contaminant that can be readily taken up and degraded by microorganisms is defined as bioavailability (Bosma et al., 1997; Maier, 2000). Two phenomena have been suggested to cause the low bioavailability of PAHs in soil (Danielsson, 2000). The first one is strong adsorption of the contaminants to the soil constituents which then leads to very slow release rates of contaminants to the aqueous phase. Sorption is often well correlated with soil organic matter content (Means, 1980) and significantly reduces biodegradation (Manilal and Alexander, 1991). The second phenomenon is slow mass transfer of pollutants, such as pore diffusion in the soil aggregates or diffusion in the organic matter in the soil. The complex set of these physical, chemical and biological processes is schematically illustrated in Figure 1. As shown in Figure 1, biodegradation processes are taking place in the soil solution while diffusion processes occur in the narrow pores in and between soil aggregates (Danielsson, 2000). Seemingly contradictory studies can be found in the literature that indicate the rate and final extent of metabolism may be either lower or higher for sorbed PAHs by soil than those for pure PAHs (Van Loosdrecht et al., 1990). These contrasting results demonstrate that the bioavailability of organic contaminants sorbed onto soil is far from being well understood. Besides bioavailability, there are several other factors influencing the rate and extent of biodegradation of PAHs in soil including microbial population characteristics, physical and chemical properties of PAHs and environmental factors (temperature, moisture, pH, degree of contamination). Figure 1: Schematic diagram showing possible rate-limiting processes during bioremediation of hydrophobic organic contaminants in a contaminated soil-water system (not to scale) (Danielsson, 2000). 1.5 Increasing the bioavailability of PAH in soil Attempts to improve the biodegradation of PAHs in soil by increasing their bioavailability include the use of surfactants , solvents or solubility enhancers.. However, introduction of synthetic surfactant may result in the addition of one more pollutant. (Wang and Brusseau, 1993).A study conducted by Mulder et al. showed that the introduction of hydropropyl-ß-cyclodextrin (HPCD), a well-known PAH solubility enhancer, significantly increased the solubilization of PAHs although it did not improve the biodegradation rate of PAHs (Mulder et al., 1998), indicating that further research is required in order to develop a feasible and efficient remediation method. Enhancing the extent of PAHs mass transfer from the soil phase to the liquid might prove an efficient and environmentally low-risk alternative way of addressing the problem of slow PAH biodegradation in soil.

Incremento de la productividad de frijol (Phaseolus vulgaris L.) a nivel de finca mediante la inoculación con Rhizobium leguminosarum bv. phaseoli

El efecto de una mezcla de tres cepas de Rhizobium leguminosarum biovar phaseoll (CIAT-613, CR-477 y KIM-5) relacionado con los factores limitantes del suelo (P, Ca, Cu, y Zn) sobre la simbiosis en tres variedades de Phaseolus vulgaris L. (DOR-364, ESTELI-90B y FIEVOLUCION-84) fue estudiado en un suelo Molisol y un Aluvial en las localidades de San Diego (Nandaime) y San Lorenzo (La Trinidad, Estelí), respectivamente, bajo condiciones de labranza convencional para ambas localidades. En la localidad de San Lorenzo se trabajó con las variedades DOR-364 y EST-908 con la corrección del cobre (factor A) y el zinc (factor 8), mientras que en la localidad de San Diego, el trabajo se realizó con las variedades DOR-364 y REVOLUCION-84 y la corrección del calcio (factor A) y el fósforo (factor 8), Ambos estudios se llevaron a cabo en época de postrera de 1994. En los dos ensayos la inoculación se hizo directamente a la semilla. Los tratamientos a evaluar fueron los siguientes: Alto nitrógeno, bajo nitrógeno como testigos (sin inocular), mezcla de inoculantes con (-A,-B), (+A,-B), (-A,+B), y (+A,+B) para un total de seis tratamientos por cada variedad. El diseño usado fue de bloques completos al azar (B.C.A). Las variables evaluadas fueron: Número y peso seco de nódulos, peso de materia seca de la planta en R6, peso de mil granos y rendimiento de grano en R9. Los datos se procesaron usando análisis de varianza (ANDEVA) y se utilizó la prueba de rangos múltiples de DUNCAN (P ≤ 0,05). Se observó a nivel general en ambos experimentos que la variedad introducida mostró un mayor rendimiento y que el mejor rendimiento de grano se obtuvo con el tratamiento en el que se usó alta dosis de nitrógeno y sin inocular. Por otro lado el rendimiento de frijol fue afectado negativamente por las aplicaciones de zinc en el caso del experimento en San Lorenzo. Para la localidad de San Diego se obtuvo respuesta positiva a las aplicaciones de fósforo junto con la mezcla de inoculantes usados. En los dos experimentos no se encontró respuesta significativa con el uso de la mezcla de inoculantes relacionados con los elementos limitantes del suelo comparado con los testigos.

Incremento de la productividad de frijol común (Phaseolus vulgaris L.) a nivel de finca mediante la inoculación con Rhizobium leguminosarum bv. Phaseoli

En el presente trabajo experimental se evaluó la respuesta a la inoculación de dos variedades de frijol común Phaseolus vulgaris L. con el objetivo de incrementar los rendimientos unitarios. Las variedades fueron DOR-364 y EST-90B, inoculadas con tres cepas de Rhizobium leguminosarum biovar phaseoli (CR-477, KIM-5 y CIAT-613) bajo condiciones de labranza convencional en la localidad de San Lorenzo, ubicada a 1O km del municipio de La Trinidad en el departamento de Estelí. Este estudio se realizó en dos etapas, postrera (1993) y primera (1994). En la primera etapa experimental se aplicó el inoculante al suelo al momento de la siembra y en la segunda etapa la inoculación se hizo a la semilla. En la primera etapa se utilizaron dos inoculantes (KIM-5 y CR-477) comparados con dos testigos sin inocular, con bajo nitrógeno (20 kg/ha de N) y el testigo sin inocular y el otro con alto nitrógeno (90 kg/ha de N en forma fraccionada). En la segunda etapa experimental, los tratamientos inoculados (KIM-5, CR-477, CIAT-613 y mezcla de las tres cepas), se compararon siempre con dos testigos sin inocular, uno sin nitrógeno y otro con alto nitrógeno (50 kg/ha de N). El diseño utilizado para ambas fases fue el de parcelas divididas (DPD). En el primer ensayo las variables medidas fueron número y peso seco de nódulos, peso seco de la parte aérea en las etapas R6 y R8 así como el rendimiento de grano. En el segundo ensayo se hicieron las mismas mediciones con la excepción del peso seco de la parte aérea en la etapa R8 del cultivo. En el primer experimento hubo respuesta significativa a la inoculación con las cepas evaluadas en la etapa R8 del cultivo, mientras que en el segundo experimento no hubo respuesta significativa en el peso seco de la parte aérea en esta etapa, en donde el mejor tratamiento fue el fertilizado con alto nitrógeno en el primer ensayo. En la primera fase del estudio, el rendimiento aunque no significativo, se vio favorecido con la fertilización nitrogenada para ambas variedades. En el segundo experimento se observó diferencias significativas en el rendimiento de grano, obteniéndose los más altos rendimientos con el tratamiento CR-477 en ambas variedades. En este estudio los tratamientos fertilizados presentaron menor rendimiento comparado con los tratamientos sin nitrógeno.

The genome of Rhizobium leguminosarum has recognizable core and accessory components

Background: Rhizobium leguminosarum is an alpha-proteobacterial N-2-fixing symbiont of legumes that has been the subject of more than a thousand publications. Genes for the symbiotic interaction with plants are well studied, but the adaptations that allow survival and growth in the soil environment are poorly understood. We have sequenced the genome of R. leguminosarum biovar viciae strain 3841. Results: The 7.75 Mb genome comprises a circular chromosome and six circular plasmids, with 61% G+C overall. All three rRNA operons and 52 tRNA genes are on the chromosome; essential protein-encoding genes are largely chromosomal, but most functional classes occur on plasmids as well. Of the 7,263 protein-encoding genes, 2,056 had orthologs in each of three related genomes ( Agrobacterium tumefaciens, Sinorhizobium meliloti, and Mesorhizobium loti), and these genes were overrepresented in the chromosome and had above average G+C. Most supported the rRNA-based phylogeny, confirming A. tumefaciens to be the closest among these relatives, but 347 genes were incompatible with this phylogeny; these were scattered throughout the genome but were over-represented on the plasmids. An unexpectedly large number of genes were shared by all three rhizobia but were missing from A. tumefaciens. Conclusion: Overall, the genome can be considered to have two main components: a 'core', which is higher in G+C, is mostly chromosomal, is shared with related organisms, and has a consistent phylogeny; and an 'accessory' component, which is sporadic in distribution, lower in G+C, and located on the plasmids and chromosomal islands. The accessory genome has a different nucleotide composition from the core despite a long history of coexistence.

Adaptation of Rhizobium leguminosarum to pea, alfalfa and sugar beet rhizospheres investigated by comparative transcriptomics

Background The rhizosphere is the microbe-rich zone around plant roots and is a key determinant of the biosphere's productivity. Comparative transcriptomics was used to investigate general and plant-specific adaptations during rhizosphere colonization. Rhizobium leguminosarum biovar viciae was grown in the rhizospheres of pea (its legume nodulation host), alfalfa (a non-host legume) and sugar beet (non-legume). Gene expression data were compared to metabolic and transportome maps to understand adaptation to the rhizosphere. Results Carbon metabolism was dominated by organic acids, with a strong bias towards aromatic amino acids, C1 and C2 compounds. This was confirmed by induction of the glyoxylate cycle required for C2 metabolism and gluconeogenesis in all rhizospheres. Gluconeogenesis is repressed in R. leguminosarum by sugars, suggesting that although numerous sugar and putative complex carbohydrate transport systems are induced in the rhizosphere, they are less important carbon sources than organic acids. A common core of rhizosphere-induced genes was identified, of which 66% are of unknown function. Many genes were induced in the rhizosphere of the legumes, but not sugar beet, and several were plant specific. The plasmid pRL8 can be considered pea rhizosphere specific, enabling adaptation of R. leguminosarum to its host. Mutation of many of the up-regulated genes reduced competitiveness for pea rhizosphere colonization, while two genes specifically up-regulated in the pea rhizosphere reduced colonization of the pea but not alfalfa rhizosphere. Conclusions Comparative transcriptome analysis has enabled differentiation between factors conserved across plants for rhizosphere colonization as well as identification of exquisite specific adaptation to host plants.

Diversity, phylogeny and distribution of bean rhizobia in salt-affected soils of North-West Morocco

Different molecular methods: BOX-PCR fingerprinting, R-FLP-PCR and sequencing of the 16S rDNA as well as the symbiotic genes nodC and nifH, were used to study the genetic diversity within a collection of nodulating bean rhizobia isolated from five soils of North-West Morocco. BOX fingerprints analysis of 241 isolates revealed 19 different BOX profiles. According to the PFLP-PCR and sequencing of 16S rDNA carried out on 45 representative isolates, 5 genotypes were obtained corresponding to the species Rhizobium etli, R. tropici, R. gallicum, R. leguminosarum and Sinorhizobium meliloti. The most abundant species were R. etli and R. tropici (61% and 24%, respectively). A high intraspecific diversity was observed among the R. etli isolates, while the R. tropici group was homogeneous. Most of the rhizobia studied belong to species known to nodulate common bean, while 2 species were unconventional microsymbionts: R. leguminosarum biovar viciae and S. meliloti. Our results, especially the nodulation promiscuity of common bean and the relation between the predominance of some species of rhizobia in particular soils and the salt content of these soils, indicate that there is a real need for a better understanding of the distribution of common bean rhizobia species in the soils of Morocco before any inoculation attempt.

Inoculações de bactérias promotoras de crescimento no cultivo de arroz em solução nutrtiva

Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)

Comparação filogenética de genomas de rizóbios por hibridização através de microarray

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Short root mutant of Lotus japonicus with a dramatically altered symbiotic phenotype

Legume plants carefully control the extent of nodulation in response to rhizobial infection. To examine the mechanism underlying this process we conducted a detailed analysis of the Lotus japonicus hypernodulating mutants, har1-1, 2 and 3 that define a new locus, HYPERNODULATION ABERRANT ROOT FORMATION (Har1), involved in root and symbiotic development. Mutations in the Har1 locus alter root architecture by inhibiting root elongation, diminishing root diameter and stimulating lateral root initiation. At the cellular level these developmental alterations are associated with changes in the position and duration of root cell growth and result in a premature differentiation of har1-1 mutant root. No significant differences between har1-1 mutant and wild-type plants were detected with respect to root growth responses to 1-aminocyclopropane1-carboxylic acid, the immediate precursor of ethylene, and auxin; however, cytokinin in the presence of AVG (aminoetoxyvinylglycine) was found to stimulate root elongation of the har1-1 mutant but not the wild-type. After inoculation with Mesorhizobium loti, the har1 mutant lines display an unusual hypernodulation (HNR) response, characterized by unrestricted nodulation (hypernodulation), and a concomitant drastic inhibition of root and shoot growth. These observations implicate a role for the Har1 locus in both symbiotic and non-symbiotic development of L. japonicus, and suggest that regulatory processes controlling nodule organogenesis and nodule number are integrated in an overall mechanism governing root growth and development.