# Biochemical and Molecular Phylogenetic Study of Agriculturally Useful Association of a Nitrogen-Fixing Cyanobacterium and NoduleSinorhizobium with Medicago sativa L.

Authors: E. V. Karaushu; I. V. Lazebnaya; T. R. Kravzova; N. A. Vorobey; O. E. Lazebny; D. A. Kiriziy; O. P. Olkhovich; N. Yu. Taran; S. Ya. Kots; A. A. Popova; E. Omarova; O. A. Koksharova
Journal: BioMed Research International
 (2015)

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## Abstract

Seed inoculation with bacterial consortium was found to increase legume yield, providing a higher growth than the standard nitrogen treatment methods. Alfalfa plants were inoculated by mono- and binary compositions of nitrogen-fixing microorganisms. Their physiological and biochemical properties were estimated. Inoculation by microbial consortium ofSinorhizobium meliloti T17 together with a new cyanobacterial isolate Nostoc PTV was more efficient than the single-rhizobium strain inoculation. This treatment provides an intensification of the processes of biological nitrogen fixation by rhizobia bacteria in the root nodules and an intensification of plant photosynthesis. Inoculation by bacterial consortium stimulates growth of plant mass and rhizogenesis and leads to increased productivity of alfalfa and to improving the amino acid composition of plant leaves. The full nucleotide sequence of the rRNA gene cluster and partial sequence of the dinitrogenase reductase (nifH) gene of Nostoc PTV were deposited to GenBank (JQ259185.1, JQ259186.1). Comparison of these gene sequences of Nostoc PTV with all sequences present at the GenBank shows that this cyanobacterial strain does not have 100% identity with any organisms investigated previously. Phylogenetic analysis showed that this cyanobacterium clustered with high credibility values with Nostoc muscorum.


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## Body

## 1. Introduction

Continuous anthropogenic impact on the environment of different chemicals, fertilizers, herbicides, plant protection from pests and diseases, plant growth regulators, and so forth that are used in agriculture, makes it necessary to develop an alternative to agricultural production, which would be based on the use of cost-effective and environmentally friendly systems for land application of fertilizers and plant protection. An important role in this respect is given to the maximum use of the soil microflora.In many countries around the world, studies and implementation of the compositions consisting of symbiotic and free-living nitrogen-fixing microorganisms have started to increase productivity of crops. Among the wide range of diazotrophic microorganisms cyanobacteria are the most versatile for biochemical potential, since they do not need to be provided with soil organic substances for nitrogen fixation unlike heterotrophic nitrogen-fixing microorganisms.Positive ecological role of cyanobacteria in the soil as nitrogen-fixing bacteria which participate in deposition of organic matter is well known now, and besides they are the centers of microcosms as autotrophic organisms with amazing abilities for symbiotrophic relations [1, 2]. The last property of cyanobacteria is particularly interesting in case of using the consortia of microorganisms in biotechnology instead of monocultures [3]. In nature, cyanobacteria are never found in the form of cell populations of one species. They are in a close relationship with the microbial community, located in the mucus of the surrounding cells. Research in this field has shown that the composition of satellite cyanobacteria is very labile and it depends on changes in habitat conditions. Axenic cultures of cyanobacteria exist only in the laboratories. In nature, they form a community and, being the edificators of microbial communities, cyanobacteria can change the microbial composition [4]. It allows the constructing of artificial microbial consortium. Nitrogen-fixing activity (NFA) of soil compositions of diazotrophic microorganisms can be an effective way to supply the crop by environmentally friendly biological nitrogen. Use of this approach requires in-depth study of the relationship between bacteria, cyanobacteria, and plants, as well as compatibility of microorganisms-partners in created artificial associations. It is important to perform the screening of the most suitable strains of microorganisms, to create conditions for the effective functioning of these symbiotic consortia. It is necessary to select an optimal quantitative ratio of microorganisms and methods of their implantation into the rhizosphere.The goals of this research were the study of the effect of artificial stable microbial consortium based on nitrogen-fixing cyanobacteriumNostoc PTV and Tn5-mutant of nodule bacteriaSinorhizobium meliloti T17, on the physiological and biochemical characteristics of growth and development of alfalfa, and, finally, on its yield and product quality and the molecular typing and phylogenetic analysis of this new cyanobacterial isolateNostoc PTV.


## 2. Material and Methods

### 2.1. Organisms and Growth Conditions

Plant alfalfaMedicago sativa (L.) sort of Jaroslavna obtained from the NSC Institute of Agriculture of National Academy of Agrarian Sciences of Ukraine has been used in the experiments. For the inoculation of alfalfa seeds we used the strain of nodule bacteriaSinorhizobium (Rhizobium)meliloti T17 (patent of Ukraine number 55432) from the collection of nitrogen-fixing microorganisms of the Institute of Plant Physiology and Genetics, National Academy of Sciences of Ukraine (Kyiv) [6]. The strain ofS. meliloti T17 was obtained as a result of intergeneric conjugation ofEscherichia coli S17-1 (pSUP2021::Tn5) andS. meliloti 425a on agar medium TY (tryptone/yeast extract) as described in [7] and it was selected for improved symbiotic properties. To create the binary composition of nitrogen-fixing microorganisms the culture of cyanobacteriumNostoc PTV (from the collection of the Institute of Hydrobiology, National Academy of Sciences of Ukraine) was used. Cyanobacterium was grown on Fitzgerald medium with the modification by Zehnder and Gorham [8] in Erlenmeyer flask at 22°C ± 2°C and illumination of 2500 lux until the stationary growth phase. The concentration of chlorophyll (Chl) in cyanobacterial cells was determined by differential fluorometry (Fluorometer FL300 3M, Russia) [9]. The binary composition was prepared by mixing the bacterial suspensions consisting of nodule bacteria (1 × 109 cells/mL) and cyanobacteria (Chl, mg/L = 1506,6 ± 13,4, ΔF=0,088) in the ratio 1 : 1. In parallel, the viability of cyanobacterial cells was determined by the difference of fluorescence intensity (ΔF) before and after the addition of simazine, the inhibitor of cells photosynthetic electron transport [10, 11].Investigations were carried out in the model experiments in a growth area of Institute of Plant Physiology and Genetics with natural light and humidity of the substrate 60% of full capacity. Plastic containers with 10 kg of sand were used in experiments. 12 alfalfa plants were grown in each container. Containers were preliminarily sterilized with 20% solution of H2O2. Washed river sand with the mineral nutrient mixture of Gelrigel [12] containing the “start” of nitrogen (177 mg of Ca(NO3)2  × 4H2O per 1 kg of sand) was used as a substrate. This amount of nitrogen represents one-quarter of the normal nitrogen supply. Before sowing the seeds were sterilized with concentrated sulfuric acid for 5 minutes, and then they were washed in running water for 1 h. The treatment of seeds by microorganism compositions was continuing during 1 h.The controls in the experiments were the samples of seeds treated by monoculture of T17S. meliloti or only byN. PTV. We used samples of alfalfa seeds moisturized with tap water as an additional “absolute” control. Experiments were performed in seven replications. Plants for analysis were selected in phases of stem (32nd day of emergence), budding (40th day), and flowering (50th day).


### 2.2. Measurements of Nitrogen Activity, Pigments Content, and Efficiency of Photosynthesis

Nitrogen-fixing (nitrogenase) activity was determined by the level of activity of root nodules by acetylene method and expressed as micromoles of ethylene formed by nodules per plant for 1 h [13]. The gas mixture was analyzed by gas chromatography of Agilent Technologies 6855 Network GC System (USA). The measurements were performed in five replications.The content of the photosynthetic pigments in leaves of alfalfa plants was determined by the Wellburn method [14]. Pigments were extracted with dimethyl sulfoxide (0.1 g vegetable material was treated in 10 mL DMSO) of leaf cut for 3 h at +67°C until complete extraction. The absorbance of the solution was measured by spectrophotometer Smart Spec Plus (BioRad, USA) at 665 and 649 nm in a 1 cm cuvette. Leaves were collected from the middle tiers of the five randomized plants of the same version. Measurements were performed in triplicate.The net assimilation rate of shoots was determined in controlled environment with installation built on base of the photoacoustic infrared gas analyzer GIAM-5 M (Russia), which was connected by differential circuit. Container with plants was placed in sealed plexiglass chamber of 50 liters through which air was blown at rate of 15 L/min. At the outlet of chamber 1 L/min of air was taken to the gas analyzer, and the remaining air was discharged into atmosphere. The chamber was irradiated with light by the lamp CG-2000 through a water filter. The illumination on the substrate level was 250 W/m2; temperature was 25°  ±  2°C. After the adaptation of plants to the conditions of measurement (30–40 min after closing the chamber), the rate of absorption of CO2 by plants was recorded (it is an apparent photosynthesis). After this, shoots of plants were cut at the substrate level and respiration of soil with roots were measured. Net assimilation rate was calculated as sum of apparent photosynthesis and respiration. Calculations of gas exchange parameters were performed according to the standard procedure [15].The protein content was determined in leaves of alfalfa plants in the budding stage by Lowry method [16]. Qualitative and quantitative composition of amino acids was determined by liquid-ion exchange column chromatography with the use of automatic analyzer T339 (Czech) on the basis of ninhydrin detection method [17].


### 2.3. Plant Stress Resistance Determination

In order to study the effect of mono- and binary inoculation on plant resistance, the basic parameters of the stress state of alfalfa were determined. Plants in the budding stage were treated with herbicide diquat (100 pmol), which was used as a stress factor. Sampling was carried out after 30 minutes, 60 minutes, and 24 hours of diquat action on plants. Specific changes in the composition of the components of a lipid-pigment complex and antioxidant system were studied in photosynthetic tissues of alfalfa.Intensity of lipid peroxidation (LPO) was evaluated by the number of end-products of lipid oxidation based on the reaction with 2-thiobarbituric acid (TBA) [18]. The activity of antioxidant systems is determined by the activity of superoxide dismutase (SOD) [19].A statistical analysis of the experimental data was performed by standard methods, involving a package of special statistical functions of Microsoft Excel. Probability of differences between the variants was assessed byt-test and a significance level of P<0,05.


### 2.4. Scanning Electron Microscopy (SEM)

Cyanobacterial samples were fixed as described above and dehydrated through an ethanol series, with an overnight exposure in absolute acetone followed by critical-point drying in a Dryer HCP-2 (Hitachi, Japan), coated with Au-Pd alloy in an IB-3 Ion Coater (Eiko, Japan) and examined with a JSM-6380LA scanning electron microscope (JEOL, Japan).


### 2.5. DNA Isolation and PCR Amplification

For molecular typing cyanobacterial genomic DNA was isolated according to [20] and synthetic oligonucleotides (“Synthol,” Moscow, Russia) have been used as cyanobacterial primers for 16S–23S rRNA PCR, according to [21]. As a second molecular marker thenifH gene has been used with corresponding PCR primers [22]. PCR for 16S–23S rRNA gene cluster was carried out on a Tercik DNA amplifier (DNA Technology, Russia) by using DreamTaq PCR Master Mix (Fermentas, EU), under the following conditions: 1 cycle at 94°C for 10 min, 25 cycles at 94°C for 45 sec, 54°C for 45 sec, 68°C for 2 min, 1 cycle at 68°C for 7 min, and a final soak step at 4°C. PCR for partialnifH gene was performed under the following conditions: 1 cycle at 94°C for 4 min, 25 cycles at 94°C for 30 sec, 54°C for 30 sec, 68°C for 30 sec, 1 cycle at 68°C for 7 min, and a final soak step at 4°C. PCR products were resolved in 1.5% agarose gel containing ethidium bromide at 5 microgram mL−1.


### 2.6. Cloning and Sequencing of PCR Products

DNA fragments obtained during PCR were cloned with CloneJet PCR Cloning Kit # K1231 (Fermentas, EU). Transformation of competent XL-1 cells ofEscherichia coli and plasmid purification were performed according to [23]. DNA sequencing was performed with ABI PRISM BigDye Terminator version 3.1 at the Applied Biosystems 3730 DNA Analyzer (Center for Collective Use “Genome”). Sequences were edited and assembled with Bioedit (Invitrogen, Carlsbad, CA). The full nucleotide sequence of the rRNA gene cluster of cyanobacteriumNostoc PTV and a part of thenifH gene were accomplished and deposited to GenBank under accession numbers JQ259185.1 and JQ259186.1.


### 2.7. Phylogenetic Analysis

Search of the nucleotide sequences in the database GenBank, homologous to the sequenced genes of studied species of cyanobacteria, was performed using BLAST (https://blast.ncbi.nlm.nih.gov/Blast.cgi?PROGRAM=blastn&PAGE_TYPE=BlastSearch&LINK_LOC=blasthome) with the option: the least degree of similarity (Minimum Identity). The sequences of selected species were aligned using the algorithm Muscle (MEGA 6.0) [24]. Phylogenetic reconstructions were performed using Bayesian inference (MrBayes version 3.1.2) [25] with the preselection of an adequate model of nucleotide substitutions (MEGA 6.0).


### 2.8. Mating and Conjugal Transfer of Plasmid DNA

Transformations ofNostoc PTV through triparental conjugations followed published protocols [26] with minor modifications. Standard bacterial mating involved the cyanobacterial strainNostoc PTV andE. coli strains (DH10B) that harbored the following three plasmids: (i) the conjugal plasmid pRL443 [27], (ii) the “helper” plasmid pRL623, [27], and (iii) the cargo plasmid pRL692 that carries the mobile element Tn5-692 [28].E. coli strains were grown in 3 mL LB with the appropriate antibiotic(s) and incubated at 37°C overnight. Cells ofE. coli were diluted 1 : 20 and were grown for 1.5–2 h at 37°C. ThenE. coli cells were harvested from 1 mL of eachE. coli culture by centrifugation and resuspended in 1 mL fresh LB. This step was repeated twice to wash the cells. After the third centrifugation, the cells were resuspended in 200 mL BG-11. Five milliliters of a growingNostoc PTV culture was harvested by centrifugation at low speed (4000 g) and resuspended in 1 mL BG-11. Then the filaments were fragmented in a water bath sonicator for 2 to 5 min so that more than half of the filaments were shorter than 5 cells. The cyanobacterial cells were collected by centrifugation for 2 min and resuspended in 1 mL BG-11. The cargo strain, the conjugal strain (for triparental mating), andNostoc PTV were combined, pelleted by centrifugation, and finally resuspended in 200 mL BG-11. The conjugation mixture was incubated for about 1 h in low light at 28°C. Then the cells were spread on sterile nitrocellulose filters laid on BG11+ 5% (vol/vol) LB agar plates (mating plates). The mating plates were incubated without antibiotic selection for 18 to 24 h in low light at 28°C, and then the filters were transferred to BG-11 for 24 h and then to BG-11 agar with 10 μg/mL Spectinomycin (Sp10) and 2 μg/mL Streptomycin (Sm2). After incubation for 8 to 12 days, isolated antibiotic-resistant transconjugant colonies were patched on fresh selective BG-11 plates.


## 2.1. Organisms and Growth Conditions

Plant alfalfaMedicago sativa (L.) sort of Jaroslavna obtained from the NSC Institute of Agriculture of National Academy of Agrarian Sciences of Ukraine has been used in the experiments. For the inoculation of alfalfa seeds we used the strain of nodule bacteriaSinorhizobium (Rhizobium)meliloti T17 (patent of Ukraine number 55432) from the collection of nitrogen-fixing microorganisms of the Institute of Plant Physiology and Genetics, National Academy of Sciences of Ukraine (Kyiv) [6]. The strain ofS. meliloti T17 was obtained as a result of intergeneric conjugation ofEscherichia coli S17-1 (pSUP2021::Tn5) andS. meliloti 425a on agar medium TY (tryptone/yeast extract) as described in [7] and it was selected for improved symbiotic properties. To create the binary composition of nitrogen-fixing microorganisms the culture of cyanobacteriumNostoc PTV (from the collection of the Institute of Hydrobiology, National Academy of Sciences of Ukraine) was used. Cyanobacterium was grown on Fitzgerald medium with the modification by Zehnder and Gorham [8] in Erlenmeyer flask at 22°C ± 2°C and illumination of 2500 lux until the stationary growth phase. The concentration of chlorophyll (Chl) in cyanobacterial cells was determined by differential fluorometry (Fluorometer FL300 3M, Russia) [9]. The binary composition was prepared by mixing the bacterial suspensions consisting of nodule bacteria (1 × 109 cells/mL) and cyanobacteria (Chl, mg/L = 1506,6 ± 13,4, ΔF=0,088) in the ratio 1 : 1. In parallel, the viability of cyanobacterial cells was determined by the difference of fluorescence intensity (ΔF) before and after the addition of simazine, the inhibitor of cells photosynthetic electron transport [10, 11].Investigations were carried out in the model experiments in a growth area of Institute of Plant Physiology and Genetics with natural light and humidity of the substrate 60% of full capacity. Plastic containers with 10 kg of sand were used in experiments. 12 alfalfa plants were grown in each container. Containers were preliminarily sterilized with 20% solution of H2O2. Washed river sand with the mineral nutrient mixture of Gelrigel [12] containing the “start” of nitrogen (177 mg of Ca(NO3)2  × 4H2O per 1 kg of sand) was used as a substrate. This amount of nitrogen represents one-quarter of the normal nitrogen supply. Before sowing the seeds were sterilized with concentrated sulfuric acid for 5 minutes, and then they were washed in running water for 1 h. The treatment of seeds by microorganism compositions was continuing during 1 h.The controls in the experiments were the samples of seeds treated by monoculture of T17S. meliloti or only byN. PTV. We used samples of alfalfa seeds moisturized with tap water as an additional “absolute” control. Experiments were performed in seven replications. Plants for analysis were selected in phases of stem (32nd day of emergence), budding (40th day), and flowering (50th day).


## 2.2. Measurements of Nitrogen Activity, Pigments Content, and Efficiency of Photosynthesis

Nitrogen-fixing (nitrogenase) activity was determined by the level of activity of root nodules by acetylene method and expressed as micromoles of ethylene formed by nodules per plant for 1 h [13]. The gas mixture was analyzed by gas chromatography of Agilent Technologies 6855 Network GC System (USA). The measurements were performed in five replications.The content of the photosynthetic pigments in leaves of alfalfa plants was determined by the Wellburn method [14]. Pigments were extracted with dimethyl sulfoxide (0.1 g vegetable material was treated in 10 mL DMSO) of leaf cut for 3 h at +67°C until complete extraction. The absorbance of the solution was measured by spectrophotometer Smart Spec Plus (BioRad, USA) at 665 and 649 nm in a 1 cm cuvette. Leaves were collected from the middle tiers of the five randomized plants of the same version. Measurements were performed in triplicate.The net assimilation rate of shoots was determined in controlled environment with installation built on base of the photoacoustic infrared gas analyzer GIAM-5 M (Russia), which was connected by differential circuit. Container with plants was placed in sealed plexiglass chamber of 50 liters through which air was blown at rate of 15 L/min. At the outlet of chamber 1 L/min of air was taken to the gas analyzer, and the remaining air was discharged into atmosphere. The chamber was irradiated with light by the lamp CG-2000 through a water filter. The illumination on the substrate level was 250 W/m2; temperature was 25°  ±  2°C. After the adaptation of plants to the conditions of measurement (30–40 min after closing the chamber), the rate of absorption of CO2 by plants was recorded (it is an apparent photosynthesis). After this, shoots of plants were cut at the substrate level and respiration of soil with roots were measured. Net assimilation rate was calculated as sum of apparent photosynthesis and respiration. Calculations of gas exchange parameters were performed according to the standard procedure [15].The protein content was determined in leaves of alfalfa plants in the budding stage by Lowry method [16]. Qualitative and quantitative composition of amino acids was determined by liquid-ion exchange column chromatography with the use of automatic analyzer T339 (Czech) on the basis of ninhydrin detection method [17].


## 2.3. Plant Stress Resistance Determination

In order to study the effect of mono- and binary inoculation on plant resistance, the basic parameters of the stress state of alfalfa were determined. Plants in the budding stage were treated with herbicide diquat (100 pmol), which was used as a stress factor. Sampling was carried out after 30 minutes, 60 minutes, and 24 hours of diquat action on plants. Specific changes in the composition of the components of a lipid-pigment complex and antioxidant system were studied in photosynthetic tissues of alfalfa.Intensity of lipid peroxidation (LPO) was evaluated by the number of end-products of lipid oxidation based on the reaction with 2-thiobarbituric acid (TBA) [18]. The activity of antioxidant systems is determined by the activity of superoxide dismutase (SOD) [19].A statistical analysis of the experimental data was performed by standard methods, involving a package of special statistical functions of Microsoft Excel. Probability of differences between the variants was assessed byt-test and a significance level of P<0,05.


## 2.4. Scanning Electron Microscopy (SEM)

Cyanobacterial samples were fixed as described above and dehydrated through an ethanol series, with an overnight exposure in absolute acetone followed by critical-point drying in a Dryer HCP-2 (Hitachi, Japan), coated with Au-Pd alloy in an IB-3 Ion Coater (Eiko, Japan) and examined with a JSM-6380LA scanning electron microscope (JEOL, Japan).


## 2.5. DNA Isolation and PCR Amplification

For molecular typing cyanobacterial genomic DNA was isolated according to [20] and synthetic oligonucleotides (“Synthol,” Moscow, Russia) have been used as cyanobacterial primers for 16S–23S rRNA PCR, according to [21]. As a second molecular marker thenifH gene has been used with corresponding PCR primers [22]. PCR for 16S–23S rRNA gene cluster was carried out on a Tercik DNA amplifier (DNA Technology, Russia) by using DreamTaq PCR Master Mix (Fermentas, EU), under the following conditions: 1 cycle at 94°C for 10 min, 25 cycles at 94°C for 45 sec, 54°C for 45 sec, 68°C for 2 min, 1 cycle at 68°C for 7 min, and a final soak step at 4°C. PCR for partialnifH gene was performed under the following conditions: 1 cycle at 94°C for 4 min, 25 cycles at 94°C for 30 sec, 54°C for 30 sec, 68°C for 30 sec, 1 cycle at 68°C for 7 min, and a final soak step at 4°C. PCR products were resolved in 1.5% agarose gel containing ethidium bromide at 5 microgram mL−1.


## 2.6. Cloning and Sequencing of PCR Products

DNA fragments obtained during PCR were cloned with CloneJet PCR Cloning Kit # K1231 (Fermentas, EU). Transformation of competent XL-1 cells ofEscherichia coli and plasmid purification were performed according to [23]. DNA sequencing was performed with ABI PRISM BigDye Terminator version 3.1 at the Applied Biosystems 3730 DNA Analyzer (Center for Collective Use “Genome”). Sequences were edited and assembled with Bioedit (Invitrogen, Carlsbad, CA). The full nucleotide sequence of the rRNA gene cluster of cyanobacteriumNostoc PTV and a part of thenifH gene were accomplished and deposited to GenBank under accession numbers JQ259185.1 and JQ259186.1.


## 2.7. Phylogenetic Analysis

Search of the nucleotide sequences in the database GenBank, homologous to the sequenced genes of studied species of cyanobacteria, was performed using BLAST (https://blast.ncbi.nlm.nih.gov/Blast.cgi?PROGRAM=blastn&PAGE_TYPE=BlastSearch&LINK_LOC=blasthome) with the option: the least degree of similarity (Minimum Identity). The sequences of selected species were aligned using the algorithm Muscle (MEGA 6.0) [24]. Phylogenetic reconstructions were performed using Bayesian inference (MrBayes version 3.1.2) [25] with the preselection of an adequate model of nucleotide substitutions (MEGA 6.0).


## 2.8. Mating and Conjugal Transfer of Plasmid DNA

Transformations ofNostoc PTV through triparental conjugations followed published protocols [26] with minor modifications. Standard bacterial mating involved the cyanobacterial strainNostoc PTV andE. coli strains (DH10B) that harbored the following three plasmids: (i) the conjugal plasmid pRL443 [27], (ii) the “helper” plasmid pRL623, [27], and (iii) the cargo plasmid pRL692 that carries the mobile element Tn5-692 [28].E. coli strains were grown in 3 mL LB with the appropriate antibiotic(s) and incubated at 37°C overnight. Cells ofE. coli were diluted 1 : 20 and were grown for 1.5–2 h at 37°C. ThenE. coli cells were harvested from 1 mL of eachE. coli culture by centrifugation and resuspended in 1 mL fresh LB. This step was repeated twice to wash the cells. After the third centrifugation, the cells were resuspended in 200 mL BG-11. Five milliliters of a growingNostoc PTV culture was harvested by centrifugation at low speed (4000 g) and resuspended in 1 mL BG-11. Then the filaments were fragmented in a water bath sonicator for 2 to 5 min so that more than half of the filaments were shorter than 5 cells. The cyanobacterial cells were collected by centrifugation for 2 min and resuspended in 1 mL BG-11. The cargo strain, the conjugal strain (for triparental mating), andNostoc PTV were combined, pelleted by centrifugation, and finally resuspended in 200 mL BG-11. The conjugation mixture was incubated for about 1 h in low light at 28°C. Then the cells were spread on sterile nitrocellulose filters laid on BG11+ 5% (vol/vol) LB agar plates (mating plates). The mating plates were incubated without antibiotic selection for 18 to 24 h in low light at 28°C, and then the filters were transferred to BG-11 for 24 h and then to BG-11 agar with 10 μg/mL Spectinomycin (Sp10) and 2 μg/mL Streptomycin (Sm2). After incubation for 8 to 12 days, isolated antibiotic-resistant transconjugant colonies were patched on fresh selective BG-11 plates.


## 3. Results and Discussion

### 3.1. Effect of Microbial Inoculation on Plant Growth and Productivity

Earlier in the laboratory study of pure cultures ofN. PTV andS. meliloti [29], we found stimulation of cell growth area of nodule bacteria around the colonies of cyanobacteriumN. PTV on the surface of the agar medium. Our results are consistent with the literature data, since it is known that cyanobacteria are producers of a wide range of biologically active substances, which include a group of growth-stimulating compounds, analogues of phytohormone [30].In our previous study we have tested different associations of nitrogen-fixing microorganisms in the rhizosphere of alfalfa [29]. The most effective bacterial consortium included cyanobacteriumNostoc PTV and Tn5-mutants of nodule bacteriaS. meliloti. Usage of the optimal proportions of components in the inoculation mixtures promotes the absence of antagonism between microorganisms and provides the stimulating effect of these consortia on various physiological and biochemical features of alfalfa plants.In this study the possibility of the formation of artificial stable microbial consortium based on nitrogen-fixing cyanobacteriumN. PTV (Figure 1) and one Tn5-mutant of nodule bacteriaS. meliloti T17 was investigated. In pot experiments it was revealed that inoculation of alfalfa by binary mixture ofS. meliloti T17 +N. PTV has a stimulating effect on the growth of the vegetative mass of plants (Table 1). The increase of above-ground plant mass after application of the consortiumS. meliloti T17 +N. PTV in the phase of stem was 15.4% compared with rhizobial T17 monoinoculation and 21% compared withN. PTV monoinoculation, respectively. The growth of above-ground alfalfa plant mass was 13.8% and 10.4%, after application of theS. meliloti T17 +N. PTV consortium in the budding stage, and 5% and 13% in the beginning of flowering, in comparison with monoinoculations, correspondingly. It is known that cells of nitrogen-fixing cyanobacteria produce polypeptides, amino acids, polysaccharides, and vitamins. Due to this diverse biochemical activity in the mucous environment of cyanobacterial cells favorable conditions for growth and reproduction of other microorganisms were created. Perhaps, it could promote a more active cell proliferation of nodule bacteria T17 associated with cyanobacteria in the root zone of alfalfa and contribute to formation of efficientRhizobium-legume symbiosis.Table 1
Dynamics of accumulation of vegetative mass of alfalfa inoculated by mono- and binary suspensions of diazotrophic microorganisms.
Inoculants
Phase of plant development
Stooling
Budding
Flowering
Above-ground mass(g/plant)
Mass of roots(g/plant)
Above-ground mass(g/plant)
Mass of roots(g/plant)
Above-ground mass(g/plant)
Mass of roots(g/plant)
Without inoculation(control)
0,42 ± 0,02
0,12 ± 0,01
1,17 ± 0,06
1,12 ± 0,1
1,25 ± 0,02
2,25 ± 0,16
N.PTV
0,62 ± 0,02
0,18 ± 0,01
1,64 ± 0,09
1,79 ± 0,09
1,70 ± 0,07
2,11 ± 0,15
S. meliloti Т17
0,65 ± 0,04
0,15 ± 0,01
1,59 ± 0,13
1,22 ± 0,11
1,83 ± 0,04
2,59 ± 0,24
S. meliloti Т17 + N.PTV
0,75 ± 0,08
0,22 ± 0,01
1,81 ± 0,18
1,82 ± 0,10
1,92 ± 0,03
2,95 ± 0,29
P ≤ 0,05.Figure 1
A SEM image of theN. PTV cells. Scale bar: 5 μm.Rhizogenesis was positively affected in plants, the seeds of which were treated with suspensions of microorganisms (Table1). The largest increase of the plant root mass was detected after using the binary inoculation (S. meliloti T17 +N. PTV). Thus, in the phase of stem the mass of roots increased by 46.6% and 22.2%, in the budding stage by 49.2% and 13%, and in the early phase of flowering by 13.9% and 39.8%, compared with plants treated only byS. meliloti T17 or by onlyN. PTV, correspondingly.Effective collaboration between all partners of symbiosis provides the activation of several metabolic processes and, above all, the fixation of atmospheric nitrogen. As a result of improved plant nutrition, their productivity increased and the quality of bioproducts improved.In the phase of stem when the process of nitrogen fixation was still inactive, differences in NFA of nodules of alfalfa plants inoculated by mono- or binary bacterial complexes were not significant (Figure2). However, in the budding stage and in the early flowering stage a nitrogen fixation in root nodules of plants infected with a mixture ofS. meliloti T17 +N. PTV was more intensive. Positive regulatory role of cyanobacteriumN. PTV is obvious according to the results presented in Table 2. Only in case of binary inoculation, plants demonstrate an increase in number and in weight of formed nodules (Table 2). Thus, the application of this microbial consortium provided increased NFA in nodules of alfalfa at the budding stage and maintained its relatively high level at the beginning of the early flowering stage (Figure 2). Therefore, this data proves thatN. PTV has a stimulating effect on the functioning of root nodule bacteriaS. meliloti T17.Table 2
Number and mass of root nodules on alfalfa plants inoculated by mono- and binary suspensions of microorganisms.
Inoculants
Phase of plant development
Stooling
Budding
Flowering
Number of root nodules(pcs/plant)
Mass of root nodules(g/plant)
Number of root nodules(pcs/plant)
Mass of root nodules(g/plant)
Number of root nodules(pcs/plant)
Mass of rootnodules (g/plant)
Without inoculation (control)
0
0
0
0
0
0
N.PTV
0
0
0
0
0
0
S. meliloti Т17
12,0 ± 1,0
0,010 ± 0,00
30,0 ± 8,5
0,115 ± 0,002
45,0 ± 0,5
0,135 ± 0,02
S. meliloti Т17 + N.PTV
14,0 ± 0,6
0,017 ± 0,04
57,0 ± 8,0
0,130 ± 0,001
70,0 ± 7,5
0,160 ± 0,02
Note. 15 plants of each variant of the experiment were analyzed for determination the average number of nodules on the roots of one plant.
P ≤ 0,05.Figure 2
Dynamics of NFA of nodules of alfalfa plants inoculated by mono- and binary suspensions of microorganisms (micromoles of ethylene formed by nodules per plant per 1 h). 1: phase of stooling, 2: phase of budding, and 3: phase of flowering,P≤0,05.It is known that the use of active strains of root nodule bacteria and their associations with other microorganisms affect the formation and functioning of the photosynthetic complexes through the nitrogen status of a host plant. Presence of nitrogen available to plants determines the efficiency of symbiotic systems.Mono- and binary suspensions inoculations of seeds showed positive dynamics of accumulation of photosynthetic pigments in the leaves of alfalfa compared with the absolute control (Figure3). The most significant differences were observed in plants whose seeds had been inoculated with nitrogen-fixing consortium of microorganisms (chlorophylla and chlorophyllb increased by 114.6 and 82.9%) compared with the corresponding option of treatment only by strain T17. It is known that the content of chlorophyll in the leaves is directly proportional to the intensity of nitrogen fixation and depends on symbiotic properties of root nodule bacteria [31–33]. Increasing the number of pigments in the leaves of alfalfa inoculated with binary bacterial suspension indicates the ability ofN. PTV to enhance the functional activity of rhizobia, which are directly interfaced with the intensity of nitrogen fixation.Figure 3
(I): content of chlorophyll (mg/g of raw material) in leaves of alfalfa inoculated by mono- and binary suspensions of microorganismsS. meliloti Т17 andN. PTV. 1: control (without inoculation); 2: inoculation by N. PTV; 3: inoculation byS. meliloti Т17; 4: inoculation by consortium ofS. meliloti Т17 +N. PTV. II: net assimilation rate (mg СО2/( plant·hour)) of alfalfa inoculated by mono- and binary suspensions of microorganismsS. meliloti Т17 andN. PTV. 1: inoculation byN. PTV; 2a: inoculation byS. meliloti Т17; 2b: inoculation by consortium ofS. meliloti Т17 +N. PTV (II(a): phase of budding and II(b): phase of flowering).Available forms of nitrogen, such as mineral and symbiotrophic, positively affect not only the formation of high grade, but also functional state of the plant photosynthetic apparatus. The net assimilation rate also demonstrates the effectiveness of the binary compositionS. meliloti T17 +N. PTV. In particular, in the budding stage of these plants the net assimilation rate exceeded 12.7%, while in the phase of early flowering it increased by 43.7% of the corresponding rate during inoculation only by T17 (Figure 3).The net assimilation rate of plant leaves typically is closely correlated with the content of nitrogen, and nitrogen is presented mainly in amino acids and proteins. Rubisco, the major cell photosynthetic enzyme of CO2 assimilation, represents more than half of the soluble cell proteins in leaf. Obviously, the intensification of NFA in the binary composition was the main reason for the increase of plant assimilation rate. However, it is possible that more active symbiotic apparatus, which is formed on the roots of plants through binary inoculation, enhanced “request” on assimilates by the root system, thereby stimulating the photosynthetic activity of plant leaves. There is a gradient of transport forms of carbon, particularly sucrose, between roots and leaves in the conduction system and it accelerates the outflow of carbon from the leaves. This, in turn, eliminates restrictions by photosynthesis products imposed on the feedback principle and further accelerates photosynthetic carbon assimilation. Thus, the efficient operation of the symbiotic apparatus in inoculated plants greatly stimulated the accumulation of photosynthetic pigments and increased the net assimilation rate. The accumulation of organic matter contributes to the formation of the plant biomass, because the basis of the biological productivity of the plant organism, including those capable of symbiotic nitrogen fixation, is photosynthetic carbon assimilation [31].In consequence of artificial inoculation of alfalfa seeds by consortium of nitrogen-fixing microorganismsS. meliloti T17 +N. PTV the yield of green mass of plants increased by 17.9% and the protein content in the leaves increased by 12.0% compared to monoinoculation by strain T17 (Table 3). This is an evidence of the effective interaction of test organisms in the cyano-Rhizobium associations and their positive impact on the growth and physiological characteristics of alfalfa plants (Table 3).Table 3
Productivity and protein content in leaves of alfalfa, inoculated by mono- and binary suspensions of microorganisms.
Inoculants
Harvest of green mass of plant,g/vessel
Protein content in the leaves
I mowing
II mowing
Totalharvest
% to monoinoculationby rhizobium
% to monoinoculation by rhizobium
Control
17,68 ± 0,51
19,70 ± 0,64
37,38
13,2
N. PTV
21,40 ± 0,52
24,22 ± 0,76
45,62
14,6
S. meliloti Т17
21,81 ± 0,48
25,17 ± 0,30
46,98
18,32
S. meliloti Т17 + N.PTV
26,26 ± 0,37∗
29,15 ± 0,17∗
55,41
117,9
20,52
112,0The amino acid composition is the main criterion of the biological value of proteins. An index of a total amino acid composition of vegetative mass of the experimental inoculated variants of alfalfa plants increased in comparison to the control (without bacterial inoculation). The maximum quantity of lysine, the most essential and deficient amino acid in humans and animals, was recorded in leaves of alfalfa (Table4). As a result of using binary inoculation a total amino acid composition increased by 25.1%, compared with the case of inoculation only by T17. In particular, a quantity of essential amino acids increased by 33.9%, and a quantity of nonessential amino acids increased by 17.7% (Figure 4). At the same time, an increase of the content of methionine, histidine, arginine, and tyrosine was observed, which are present in small quantities in plant leaves, and this is one of the factors limiting the rate of biosynthesis of proteins, especially in generative organs. The results are a direct proof of the positive impact of cyanobacterial inoculation on the quality of agricultural products.Table 4
Amino acid content in leaves of alfalfa, inoculated by mono- and binary suspensions of microorganisms.
Amino acid
Content of amino acids (mg/100 mg DW)
Control
N. punctiforme
Т17
Т17 +N. punctiforme
Gamma-aminobutyric acid
0,065
0,088
0,085
0,123
Lysine
0,386
0,802
0,459
0,610
Histidine
0,094
0,301
0,171
0,232
Arginine
0,297
0,905
0,439
0,585
Asparagine
0,675
0,882
0,748
0,779
Threonine
0,278
0,623
0,383
0,496
Serine
0,321
0,698
0,413
0,533
Glutamic acid
0,876
1,931
1,083
1,395
Proline
0,376
0,610
0,419
0,548
Glycine
0,423
0,790
0,470
0,537
Alanine
0,479
0,895
0,581
0,644
Cysteine
0,054
0,262
0,057
0,079
Valine
0,245
0,651
0,301
0,423
Methionine
0,111
0,298
0,149
0,200
Isoleucine
0,175
0,439
0,233
0,273
Leucine
0,523
1,234
0,685
0,938
Tyrosine
0,201
0,534
0,285
0,253
Phenylalanine
0,398
0,835
0,453
0,626
Total
5,977
12,779
7,417
9,276Figure 4
Total content of essential and nonessential amino acids in leaves of alfalfa grown after mono- and binary inoculation by cyanorhizobial compositions of microorganisms: 1: control (without inoculation), 2: monoinoculation of alfalfa seeds by cyanobacteriumN. PTV, 3: inoculation of alfalfa seeds by Tn5-mutant strain ofS. meliloti T17, and 4: binary inoculation of alfalfa seeds by Tn5-mutant strain ofS. meliloti T17 +N. PTV.


### 3.2. Stress Response of Plants Inoculated with Microbial Consortium

It is known that the plant productivity rate and resistance index are inversely dependent values. A positive effect of the cyanobacterial consortium T17 +N. PTV on the productivity of alfalfa is shown in our study. It was logical to study the effect of the binary inoculation on plant resistance to the adverse effects of certain environmental factors. It is an extremely important issue. We have used herbicide diquat as a model stress factor. For a short duration (30 minutes) of diquat treatment the content of TBA-reactive products in photosynthetic tissues of plants that were inoculated with the strain T17 was reduced by 18% compared to plants without inoculation (control 2). In the case when plants were inoculated with the consortiumS. meliloti T17 +N. PTV the content of TBA-reactive products remained at the level of control. In the experiments with more prolonged action of the stress factor (60 min) the content of TBA-reactive products in plants inoculated only by the strain T17 decreased by 16.9% and in the case of binary inoculation the content of TBA-reactive products decreased by 25%. It should be noted that after 24 h of plants exposure with diquat, regardless of the inoculation agent used, reducing the amount of TBA-active products in photosynthetic tissues was not observed compared with the control. At the same time, in the experiment with the use of the consortium of microorganisms a difference (15.4%) with the inoculation only by strain T17 was marked (Figure 5). At short-term action of diquat (30 min) a rate of SOD activity in photosynthetic tissues of plants inoculated withS. meliloti T17 +N. PTV was 2.5 times higher than in controls and by 42.5% in plants, inoculated by strain T17. After herbicide treatment during 60 minutes a significant altering of SOD activity in inoculated plants (irrespective of whether a mono- or binary inoculation) was not observed. However, in comparison to the control, this difference was significant; the enzyme activity was increased by 54%. Under long-term stress (24 h) in plants inoculated with strain T17, SOD activity remained at the same level as for short-term exposure. In plants, the seeds were treated with consortiumS. meliloti T17 +N. PTV, for the same conditions; this index decreased by 23.4% compared with the control and 34.4%, in comparison with the plants inoculated by strain T17 (Figure 6). Thus, the plants inoculated with algae-rhizobial composition proved to be more resistant to oxidative stress. It is possible due to the increased level of NFA of their symbiotic system and thus the increase in the number of available forms of nitrogen for alfalfa plants and the possible participation of NO in the defense reactions. In the literature, there are two hypotheses about the mechanisms of NO action under conditions of stress. First, NO may act as an antioxidant, directly linking to ROS, thereby protecting cells from damaging their actions [34]. Secondly, NO can act as a signaling molecule that triggers a cascade of reactions that lead to the expression of specific genes [35]. In their chemical and physical properties small molecule, rapid metabolism, lack of charging, and high diffusion coefficient of NO are well suited for the role of intracellular signaling mediator of plant stress responses.Figure 5
Content of TBA-active products in alfalfa leaves after herbicide diquat treatment: А: for 30 min, B: for 60 min, and C: for 24 h. 1: control (without inoculation and herbicide diquat treatment); 2: control (without inoculation, with herbicide diquat treatment); 3: inoculation by Tn5-mutant ofS. meliloti Т17, with herbicide diquat treatment; 4: inoculation by Tn5-mutant ofS. meliloti Т17+N. PTV, with herbicide diquat treatment.Figure 6
SOD activity in alfalfa leaves after herbicide diquat treatment: А: in 30 min, B: in 60 min, and C: in 24 h. 1: control (without inoculation and herbicide diquat treatment); 2: control (without inoculation, with herbicide diquat treatment); 3: inoculation by Tn5-mutant ofS. meliloti Т17, with herbicide diquat treatment; 4: inoculation by Т17 +N. PTV, with herbicide diquat treatment.Thus, the inoculation of alfalfa seeds by a consortium of nitrogen-fixing microorganismsS. meliloti T17 +N. PTV increased the nitrogenase activity of root nodules, increased the net assimilation rate, and increased productivity and product quality, and also the stability of alfalfa plants under the influence of oxidative stress induced by herbicides.


### 3.3. Molecular Typing and Phylogenetic Analysis of CyanobacteriumNostoc PTV

One of the main goals of this study was the molecular typing and phylogenetic analysis of a new cyanobacterial isolateN. PTV originated from the Institute of Hydrobiology of Academy of Science of Ukraine. As it was shown above, this cyanobacterium is effective for soil algalization. As a component of algae-rhizobium compositions, this cyanobacterium stimulates germinative energy, growth, and productivity of legumes.To identify and to determine the phylogenetic positions of the new cyanobacterial isolateN. PTV we used a partial sequence of thenifH gene (342 bp), encoding nitrogenase reductase, and 16S ribosomal RNA gene cluster (1765 bp) as molecular markers. Comparison of thenifH gene sequence and rRNA gene cluster sequence of cyanobacteriumN. PTV with all the sequences present at the GenBank by using the program Blast (https://blast.ncbi.nlm.nih.gov/Blast.cgi?PROGRAM=blastn&PAGE_TYPE=BlastSearch&LINK_LOC=blasthome) shows that this strain has no full similarity with any of early investigated organisms.Comparison of rRNA gene cluster sequence (1765 bp) of the cyanobacteriumNostoc sp. PTV revealed that this cyanobacterium shows the highest similarity with several strains ofN. muscorum andN. commune (Table 5). In general, support for branching in the tree, based on a fragment of 16S rRNA gene sequence (Figure 7), is worse in comparison with the reconstruction of the phylogeny of cyanobacteria based on the sequence of the genenifH (Figure 8).Table 5
BLAST results obtained by querying the 16S–23S rRNA gene cluster ofNostocsp. PTV with GenBank and geographical and ecological origins of the hits.
Closest GenBank relative
GenBank access number
Query coverage, %
Score, %
Identity, %
E value
Origin of the strain and reference
Nostoc sp. HA4355-MV2 clone p9D
HQ847576
98
2872
97
0.0
Maniniholo Cave wall, near HaenaUSA: Kauai, Hawaii
Nostoc muscorum CCAP 1453/22
HF678509
98
2531
93
0.0
Scottish Association for Marine Science, Molecular and Microbial Biology, Dunstaffnage Marine Laboratory,  Oban, PA37 1QA, United Kingdom
Anabaena variabilis ATCC 29413
CP000117
98
2457
92
0.0
It has been studied extensively for over 40 years and is the strain of choice for many laboratories throughout the world
Nostoc sp. PCC 7120
BA000019
98
2453
92
0.0
Complete genomic sequence of the filamentous nitrogen-fixing cyanobacteriumAnabaena sp. (Nostoc) strain PCC 7120 is available
Nostoc commune NC1 clone 10
EU586726
98
2441
91
0.0
John Carroll University, 20700, North Park Boulevard, University Heights, OH 44118, USA
Nostoc commune NC1 clone M2
EU586725
98
2441
91
0.0
John Carroll University, 20700, North Park Boulevard, University Heights, OH 44118, USA
Nostoc commune NC5 clone 10
EU586727
98
2437
91
0.0
Biology, John Carroll University, 20700, North Park Boulevard, University Heights, OH 44118, USA
Nostoc commune NC1
EU784149
98
2428
91
0.0
Nostoc commune NC1 was isolated from soil (subaerophyt) in Třeboň/Czech republic in 2006.
Nostoc commune NC5 clone 11
EU586728
98
2423
91
0.0
Biology, John Carroll University, 20700,  North Park Boulevard, University Heights, OH 44118, USA
Nostoc ellipsosporum CCAP 1453/15
HE975023
94
2399
92
0.0
Scottish Association for Marine Science,  Molecular and Microbial Biology, Dunstaffnage Marine Laboratory, Oban PA37 1QA, United Kingdom
Nostoc cf. punctiforme Bashkir clone 6A
EU586732
96
2378
92
0.0
John Carroll University, 20700,  North Park Boulevard, University Heights, OH 44118, USA
Calothrix sp. HA4356-MV2 clone p8i
JN385289
98
2361
90
0.0
Cave wall scraping, Maniniholo Cave  near Haena, USA: Kauai, Hawaii
Calothrix sp. HA4340 LM2
KF417425
98
2361
90
0.0
Cave, USA: Kauai, Hawaii, Maniniholo Cave
Anabaena sp. CCAP 1403/4A
HE975015
93
2360
92
0.0
Scottish Association for Marine Science, Molecular and Microbial Biology, Dunstaffnage Marine Laboratory,  Oban PA37 1QA, United Kingdom
Nostoc muscorum CCAP 1453/8
HF678508
93
2358
92
0.0
United Kingdom: Scotland
Calothrix sp. HA4356-MV2 clone p8i
JN385289
98
2356
90
0.0
Cave wall scraping, Maniniholo Cave  near Haena, USA: Kauai, Hawaii
Cylindrospermum moravicum CCALA 993 clone operon 1
KF052607
97
2331
94
0.0
Cave sediment, Czech Republic: Amaterska Cave, South Moravia
Nostoc punctiforme PCC 73102
CP001037
97
2331
91
0.0
A symbiont from a cycad
Nostoc sp. Peltigera malacea DB3992 cyanobiont
JX219483
97
2322
91
0.0
Cyanobiont of lichenized fungiPeltigera malacea, Iceland
Nostoc muscorum CCAP 1453/20
HF678506
95
2318
91
0.0
Scottish Association for Marine Science, Molecular and Microbial Biology, Dunstaffnage Marine Laboratory, Oban PA37 1QA, United Kingdom
Nostoc sp. 10Dp66E
JQ259187
98
2318
90
0.0
From association withDynamena  pumila L., White Sea, Russia
Cylindrospermum catenatum CCALA 999 clone operon 1
KF052615
97
2309
94
0.0
Soil, Slovakia: forest above Stara Brzotinska Cave, Slovak Karst
Trichormus anomalus HA4352 LM2
KF417426
96
2309
92
0.0
Cave, USA: Kauai, Hawaii, Maniniholo Cave
Cylindrospermum sp. HA4236-MV2 clone p4
JN385290
98
2309
89
0.0
Taro field, Makiki Nature Center, USA: Oahu, Hawaii
Cylindrospermum  catenatum CCALA 996 clone operon 1
KF052611
97
2307
94
0.0
Soil, Czech Republic: Amaterska Cave, South Moravia
Tolypothrix campylonemoides FI5-MK38 clone p10D
JQ083654
98
2305
90
0.0
Sand, USA: Fort Irwin NTC, San Bernardino Co., California
Cylindrospermum catenatum CCALA 990 clone operon 1
KF052601
95
2302
94
0.0
Soil, Czech Republic: Benešov nad Černou, South  Bohemia
Spirirestis rafaelensis WJT-71-NPBG6 clone p1B
JQ083656
98
2300
90
0.0
Joshua Tree National Park, USA: Joshua Tree Forest, San Bernardino Co., California
Cylindrospermum badium CCALA 1000 clone operon 1
KF052616
97
2298
94
0.0
Reclaimed coal mine soil, USA: Pyramid State Recreation Area, Illinois
Cylindrospermum catenatum CCALA 991 clone operon 1
KF052603
97
2293
94
0.0
Soil, Czech Republic: Most Region, North Bohemia
Spirirestis rafaelensisWJT-71-NPBG6 clone p1A
JQ083655
98
2291
89
0.0
Joshua Tree National Park, USA: Joshua Tree Forest, San Bernardino Co., California
Nostoc sp. Peltigera membranacea cyanobiont N6
JX975209
97
2289
91
0.0
Symbiont ofPeltigera membranacea lichen, Iceland
Cylindrospermum pellucidum CCALA 992 clone operon 1
KF052605
97
2287
94
0.0
Cave sediment, Slovakia: Dlha chodba in Domica Cave system, Slovak Karst
Hassallia sp. EM2-HA1 clone p4B
HQ847555
98
2282
89
0.0
Soil, Mojave National Preserve, USA: San Bernardino Co., California
Tolypothrix tenuis f. terrestris UFS-BI-NPMV-1A2-F06 clone p13E
JQ083651
98
2277
89
0.0
Arid soil after a burn, foothills of  the Onaquee Mts. USA: Utah
Nostoccf.commune 257-16
HQ877826
96
2271
90
0.0
Subaerial, on Bonampak's archeological building walls, Mexico: Chiapas
Hassallia sp. CNP3-B3-C04 clone p5D
HQ847556
98
2271
89
0.0
Soil, Needles District, Virginia Park, Canyonlands National Park, USA: San Bernardino Co., California
Uncultured cyanobacterium clone Emix3.12
JX887892
92
2269
91
0.0
Freshwater microbial matKonstanz,  Germany
Cylindrospermum muscicola SAG 44.79 clone operon 1
KF111150
96
2268
93
0.0
SoilFrance: Gif-Sur-Yvette, Ile-de-France Region
Tolypothrix tenuis f. terrestris UFS-BI-NPMV-1A2-F06 clone p13F
JQ083652
98
2268
89
0.0
Arid soil after a burn, foothills ofthe Onaquee Mts.USA: Utah
Hassallia sp. CM1-HA11 clone p8A
JQ083650
98
2268
89
0.0
Sandy loam near gypsum mine,USA: Clark Mountains, San Bernardino Co.,California
Hassallia sp. CM1-HA08 clone p7B
JQ083648
98
2268
89
0.0
Sandy loam near gypsum mine,USA: Clark Mountains, San Bernardino Co.,California
Nostoc cf. commune 257-20
HQ877827
94
2266
91
0.0
Biofilms of N. cf. commune were collected at Bonampak archeological area in 2008 from two sites on the building walls (Chiapas, Mexico).
Tolypothrix campylonemoides FI5-MK38 clone p10A
JQ083653
98
2266
89
0.0
SandUSA: Fort Irwin NTC, San Bernardino Co.,California
Hassallia sp. CM1-HA08 clone p7F
HQ847554
98
2266
89
0.0
Soil, Clark Mountains, near gypsummineUSA: San Bernardino Co., California
Desmonostoc sp. HA7617 LM4
KF417429
96
2241
90
0.0
USA: Kauai, Hawaii, Waikapalae Cave
Camptylonemopsis sp. HA4241-MV5 clone B2-3 + p4
JN385292
96
2223
93
0.0
Moleka streamUSA: Oahu, Hawaii
Anabaena circinalis 33-10 isolate
EF634474
98
2199
88
0.0
Ohau Channel,  New Zealand
Tolypothrix sp. PCC 7504 isolate DBSU 18
FJ660999
90
2194
92
0.0
FreshwaterAquarium, Sweden
Nostoc sp. UAM 307
HM623782
70
2111
98
0.0
Rock surface of calcareous riverSpain: Matarranya River, Teruel, East Spain
Rivularia sp. 1PA23
FJ660980
92
2021
88
0.0
Pozas Azules I, MexicoMicrobialitefreshwater
Nostoc sp. 8964:3
AM711541
66
2006
99
0.0
Host isGunneraprorepens (Angiospermae), New Zealand
Rivularia sp. 1PA21
FJ660978
92
2004
88
0.0
Institute of Ecology,UNAM (Mexico)
Nostoc linckia var. arvense IAM M-30
AB325907
65
1999
99
0.0
Cultivated samples from the Institute ofMolecular Biosciences at the University of Tokyo
Aphanizomenon ovalisporum ILC-164
JF768745
92
1988
93
0.0
Lake Kinneret, Israel; Banker et al., 1997 [5]
Nostoc muscorum Ind33
HM573462
65
1988
99
0.0
Paddy field,India: Agricultural Farms, Banaras Hindu University, Varanasi, Uttar PradeshFigure 7
Phylogenetic relationships ofNostoc sp. PTV (designated by black square) inferred under the posterior probability criterion (MrBayes) from the gene for 16S rRNA, partial sequence information. Numbers at the nodes indicate the Bayesian statistical support values (posterior probabilities multiplied by 100); only values higher than 50% are given. The scale bar indicates the number of substitutions per nucleotide position.Figure 8
Phylogenetic relationships ofNostoc sp. PTV (designated by black square) inferred under the posterior probability criterion (MrBayes) from the gene fornifH, partial sequence information. Numbers at the nodes indicate the Bayesian statistical support values (posterior probabilities multiplied by 100); only values higher than 50% are given. The scale bar indicates the number of substitutions per nucleotide position.The group ofNostoc strains and species, which includesNostoc PTV, forms a cluster with the minimum of allowable support, 0.95. Hierarchy of strains (HA 4355-MV2, PTV, and 8964) andNostoc species (N. muscorum andN. linckia) cannot be evaluated because of the low topological support of this site of the tree: credibility values range from 0.56 to 0.94. It is difficult to discuss a relation ofNostocPTV strain to strain HA 4355-MV2, due to the very low values ​​of the other branches in the cluster, and very scarce information about the HA-MV2 4355 strain clearly does not help to solve the problem of their possible relationship.N. muscorum is discussed below.N. linckia is also a freshwater strain and could be isolated in some terrestrial niches. Interestingly, theNostoc strain UAM 307 is quite clearly differentiated from the other representatives of Nostocaceae (0.95). Being sufficiently close to strain ofNostoc PTV, this cyanobacterium has some significant features that provided the separation of this strain into the other branch of the common withNostoc PTV cluster.Even more interesting detail is that the last significant branch (credibility value is equal to unity) of the cluster is formed by the strain ofN. muscorum Ind33, which is significantly aside not only from the desired strain of PTV, but also from the different strains of the same species (CCAP 1453-22). Thus, the strain ofNostoc PTV has teamed up with members of their own genus.Outgroup of this dendrogram is represented by two strains ofRivularia (this kind of cyanobacteria forms heteropolar threads; their trichomes are densely agglomerated, covered with a total mucus). The genus is represented only by the species often living on calcareous substrates, but there are rare epilithic and epiphytic species.Comparison ofnifH sequence of cyanobacterium PTV revealed that this strain shows the highest similarity with several strains ofNostoc (Table 6). The closest relative isNostoc muscorum UTAD N213, purified from rice paddy in Mondego River Basin (Portugal). Phylogenetic analysis (Figure 8) revealed that the cyanobacterium PTV forms a minicluster withNostoc muscorum UTAD N213.N. muscorum is a free-living filamentous cyanobacterium, which inhabits both terrestrial and freshwater aquatic environments. They are phototrophic organisms performing photosynthesis and also fixing atmospheric nitrogen [36].Table 6
BLAST results obtained by querying thenifH gene of Nostocsp.PTV with GenBank and geographical and ecological origins of the hits.
Closest GenBankrelative
GenBank number
Query coverage %
Score %
Identity %
E value
Origin of the strain and reference
Nostoc muscorum UTAD N213
GQ443450.1
100
612
99
7
e
-
172
Rice paddy in Mondego River Basin, Portugal
Nostoc muscorumclone CC1090A1
AY221814.1
94
576
99
5
e
-
161
Ocean Sciences Department, University ofCalifornia, Santa Cruz, CA 95064, USA
Nostoc commune (UTEX 584)
L23514.1
99
565
97
9
E
-
158
Scotland
Nostoc sp. UAM 362
JQ514115.1
99
553
96
5
e
-
154
Rock surface of calcareous river with brackish water,Spain: Muga, Girona (Northeast Spain)
Nostoc sp. Baikal
JN887856.1
99
517
94
4
e
-
143
Nitrogen-fixing cyanobacteria from Lake Baikal
Nodularia spumigena AV1
GQ456132.1
99
511
93
2
e
-
141
The surface waters of the Baltic Sea, Stockholm, Sweden
Tolypothrix sp. UAM 379
JQ514114.1
99
462
90
8
E
-
127
Rock surface of calcareous river with brackish water,Spain: Muga, Girona (Northeast Spain)
Tolypothrix sp. UAM 378
JQ514113.1
99
462
90
8
E
-
127
Rock surface of calcareous river with brackish water,Spain: Muga, Girona (Northeast Spain)
Tolypothrix sp. UAM 415
JQ514120.1
99
453
89
4
E
-
124
Rock surface of calcareous river with brackish water,Spain: Muga, Girona (Northeast Spain)
Tolypothrix sp. UAM 413
JQ514119.1
99
453
89
4
E
-
124
Rock surface of calcareous river with brackish water,Spain: Muga, Girona (Northeast Spain)
Nostoc PCC 6720
Z31716.1
99
430
88
4
E
-
117
Nostoc PCC 6720 was previously known as Anabaenopsis circularis.This is a freshwater species
Anabaena sp. L-31
L04499.1
99
426
88
5
E
-
116
The filamentous, heterocystous, nitrogen-fixing freshwater cyanobacterium
Anabaena PCC7120
J05111.1
99
426
88
5
E
-
116
http://wiki.annotation.jp/Kazusa:CyanoBase:Anabaena_sp._PCC_7120
Nostoc sp. UAM 367
JQ514116.1
100
423
87
7
E
-
115
Rock surface of calcareous river with brackish water,Spain: Muga, Girona (Northeast Spain)
Anabaena siamensis TISTR 8012
DQ176436.2
100
414
87
3
E
-
112
Anabaena siamensis is a filamentous heterocystous nitrogen-fixing cyanobacterium which originally was isolated from a rice paddy field in Thailand
Mastigocladus laminosus CCMEE 5324
EF570558.1
100
414
87
3
E
-
112
The cosmopolitan thermophilic cyanobacteriumMastigocladus laminosus from the University of Oregon's Culture Collection of Microorganisms from Extreme Environments (CCMEE)
Fischerella UTEX1931
U49514.1
100
414
87
3
E
-
112
Thermophilic cyanobacterium (synonym:Mastigocladus laminosus)
Anabaena sphaerica UTEX “B 1616”
DQ439648.1
99
408
87
1
E
-
110
Department of Chemistry and Chemical Engineering, University of Sheffield, Mappin Street, Sheffield,South Yorkshire S1 3JD, United Kingdom
Anabaena sp. A2
AF124377.1
99
408
87
1
.
E
-
110
Molecular Evolution, BMC, Uppsala University, Husargatan 3, 751 24 Uppsala,  Sweden
Anabaena azollae
L34879.1
99
435
88
1
E
-
118
Anabaena azollae 1a, a putative symbiont of Azolla caroliniana
Anabaena variabilis
U89346.1
99
435
88
1
E
-
118
Anabaena variabilis ATCC 29413 is a filamentous cyanobacterium that produces heterocysts and fixes nitrogen under a variety of environmental conditionsN. muscorum is the most common type ofNostoc in terrestrial ecosystems and is widely spread, due to the adaptability to many adverse conditions. It forms a symbiotic relationship with many types of terrestrial plants and fungi.It is known thatN. muscorum has great effect on soil biology and productivity which makes it an attractive soil inoculant. This cyanobacterium is able to obtain carbon and nitrogen from the air and has an advantage over heterotrophic soil inoculants, which are usually limited by carbon [37].It also benefits plants and other soil bacteria by increasing soil organic matter in the form of carbohydrates and provides biological organic nitrogen that can be assimilated by plants [38].N. muscorum helps to create the environment conditions to further colonization and growth by plants and other microorganisms [39].Inoculation of theN. muscorum isolates caused a significant effect on growth of wheat and maize plants. Cyanobacterial inoculation positively affected pigment content, increased plant shoot and root dry weight, and increased leaf area [40].In general, the topology of the dendrogram (Figure8) has a good support; the main branch nodes are characterized by high credibility values.Nostoc PTV is in the same cluster withNostoc sp. UAM-362 andNostoc commune.Nostoc sp. UAM-362 was isolated from the rock surface of calcareous river with brackish water in Spain: Muga, Girona (Northeast Spain).N. commune is a colonial species of cyanobacterium. As well asN. punctiforme, N. communeis able to survive in extreme conditions such as polar regions and arid areas.Three more clusters are presented as the parts of the large one: two single clusters, represented byNostoc sp. Baikal (nitrogen-fixing cyanobacteria from Lake Baikal) and byNodularia spumigena from family Nostocaceae.Nodularia occurs mainly in brackish or saline waters.Nodularia cells occasionally can form heavy algal blooms. Some strains produce a toxin (nodularin), which is harmful to human health [41].The third cluster is formed by four strains ofTolypothrix and by one strain ofNostoc sp. UAM-367 (isolated from rock surface of calcareous river with brackish water in Spain: Muga, Girona). CyanobacteriaTolypothrix grow in unpolluted waters; several species are found in swamps, known aerophilic species growing on the bark of trees, in the wet sands, on wet rocks, and so forth.Two species, and one strain (PCC 7120) ofAnabaena, representing a family of filamentous cyanobacteria Nostocaceae, belong to this large cluster with a poor resolution (a credibility value of branching is 0.71). These cyanobacteria exist in the form of plankton; some species are symbionts of plants.Anabaena is one of the four genera of cyanobacteria that produce neurotoxins.Anabaena is a model for the study of cell differentiation and differential gene expression during nitrogen fixation [42].A. siamensis andA. sphaerica are freshwater species. This mega cluster consisting of described species of cyanobacteria is well differentiated from the other two clusters: a single one represented by strainAnabaena L-31 (freshwater cyanobacterium) and a poorly differentiated cluster, which consists of two strains ofAnabaena (A2 and PCC 7120) and two well-differentiated species ofAnabaena, A. azollae andA. variabilis.A. azollae forms symbiosis with water fernAzolla.Outgroup for the described species ofNostoc andAnabaena is represented by ​​Mastigocladus laminosus and by member of the genusFischerella (strain UTEX 1931). The first organism is a typical representative of the genusMastigocladus.Fischerella represents another squad, Stigonematales. Both types of reference are truly branching filamentous forms of thermophilic cyanobacteria.


### 3.4. Gene Transfer intoNostoc PTV Cells

Nostoc PTV cells were tested for their ability to conjugational DNA transfer. As a result of plasmid pRL692 transfer into cyanobacterial cells several hundred transconjugant colonies were selected on selective plates that contained solid BG-11 medium and antibiotics (Sp10 and Sm2). On control plates antibiotic-resistant colonies were absent (data not shown). In future experiments we plan to use this experimental approach for transposon mutagenesis ofNostoc PTV and selection of the new mutants with interesting characteristics.


## 3.1. Effect of Microbial Inoculation on Plant Growth and Productivity

Earlier in the laboratory study of pure cultures ofN. PTV andS. meliloti [29], we found stimulation of cell growth area of nodule bacteria around the colonies of cyanobacteriumN. PTV on the surface of the agar medium. Our results are consistent with the literature data, since it is known that cyanobacteria are producers of a wide range of biologically active substances, which include a group of growth-stimulating compounds, analogues of phytohormone [30].In our previous study we have tested different associations of nitrogen-fixing microorganisms in the rhizosphere of alfalfa [29]. The most effective bacterial consortium included cyanobacteriumNostoc PTV and Tn5-mutants of nodule bacteriaS. meliloti. Usage of the optimal proportions of components in the inoculation mixtures promotes the absence of antagonism between microorganisms and provides the stimulating effect of these consortia on various physiological and biochemical features of alfalfa plants.In this study the possibility of the formation of artificial stable microbial consortium based on nitrogen-fixing cyanobacteriumN. PTV (Figure 1) and one Tn5-mutant of nodule bacteriaS. meliloti T17 was investigated. In pot experiments it was revealed that inoculation of alfalfa by binary mixture ofS. meliloti T17 +N. PTV has a stimulating effect on the growth of the vegetative mass of plants (Table 1). The increase of above-ground plant mass after application of the consortiumS. meliloti T17 +N. PTV in the phase of stem was 15.4% compared with rhizobial T17 monoinoculation and 21% compared withN. PTV monoinoculation, respectively. The growth of above-ground alfalfa plant mass was 13.8% and 10.4%, after application of theS. meliloti T17 +N. PTV consortium in the budding stage, and 5% and 13% in the beginning of flowering, in comparison with monoinoculations, correspondingly. It is known that cells of nitrogen-fixing cyanobacteria produce polypeptides, amino acids, polysaccharides, and vitamins. Due to this diverse biochemical activity in the mucous environment of cyanobacterial cells favorable conditions for growth and reproduction of other microorganisms were created. Perhaps, it could promote a more active cell proliferation of nodule bacteria T17 associated with cyanobacteria in the root zone of alfalfa and contribute to formation of efficientRhizobium-legume symbiosis.Table 1
Dynamics of accumulation of vegetative mass of alfalfa inoculated by mono- and binary suspensions of diazotrophic microorganisms.
Inoculants
Phase of plant development
Stooling
Budding
Flowering
Above-ground mass(g/plant)
Mass of roots(g/plant)
Above-ground mass(g/plant)
Mass of roots(g/plant)
Above-ground mass(g/plant)
Mass of roots(g/plant)
Without inoculation(control)
0,42 ± 0,02
0,12 ± 0,01
1,17 ± 0,06
1,12 ± 0,1
1,25 ± 0,02
2,25 ± 0,16
N.PTV
0,62 ± 0,02
0,18 ± 0,01
1,64 ± 0,09
1,79 ± 0,09
1,70 ± 0,07
2,11 ± 0,15
S. meliloti Т17
0,65 ± 0,04
0,15 ± 0,01
1,59 ± 0,13
1,22 ± 0,11
1,83 ± 0,04
2,59 ± 0,24
S. meliloti Т17 + N.PTV
0,75 ± 0,08
0,22 ± 0,01
1,81 ± 0,18
1,82 ± 0,10
1,92 ± 0,03
2,95 ± 0,29
P ≤ 0,05.Figure 1
A SEM image of theN. PTV cells. Scale bar: 5 μm.Rhizogenesis was positively affected in plants, the seeds of which were treated with suspensions of microorganisms (Table1). The largest increase of the plant root mass was detected after using the binary inoculation (S. meliloti T17 +N. PTV). Thus, in the phase of stem the mass of roots increased by 46.6% and 22.2%, in the budding stage by 49.2% and 13%, and in the early phase of flowering by 13.9% and 39.8%, compared with plants treated only byS. meliloti T17 or by onlyN. PTV, correspondingly.Effective collaboration between all partners of symbiosis provides the activation of several metabolic processes and, above all, the fixation of atmospheric nitrogen. As a result of improved plant nutrition, their productivity increased and the quality of bioproducts improved.In the phase of stem when the process of nitrogen fixation was still inactive, differences in NFA of nodules of alfalfa plants inoculated by mono- or binary bacterial complexes were not significant (Figure2). However, in the budding stage and in the early flowering stage a nitrogen fixation in root nodules of plants infected with a mixture ofS. meliloti T17 +N. PTV was more intensive. Positive regulatory role of cyanobacteriumN. PTV is obvious according to the results presented in Table 2. Only in case of binary inoculation, plants demonstrate an increase in number and in weight of formed nodules (Table 2). Thus, the application of this microbial consortium provided increased NFA in nodules of alfalfa at the budding stage and maintained its relatively high level at the beginning of the early flowering stage (Figure 2). Therefore, this data proves thatN. PTV has a stimulating effect on the functioning of root nodule bacteriaS. meliloti T17.Table 2
Number and mass of root nodules on alfalfa plants inoculated by mono- and binary suspensions of microorganisms.
Inoculants
Phase of plant development
Stooling
Budding
Flowering
Number of root nodules(pcs/plant)
Mass of root nodules(g/plant)
Number of root nodules(pcs/plant)
Mass of root nodules(g/plant)
Number of root nodules(pcs/plant)
Mass of rootnodules (g/plant)
Without inoculation (control)
0
0
0
0
0
0
N.PTV
0
0
0
0
0
0
S. meliloti Т17
12,0 ± 1,0
0,010 ± 0,00
30,0 ± 8,5
0,115 ± 0,002
45,0 ± 0,5
0,135 ± 0,02
S. meliloti Т17 + N.PTV
14,0 ± 0,6
0,017 ± 0,04
57,0 ± 8,0
0,130 ± 0,001
70,0 ± 7,5
0,160 ± 0,02
Note. 15 plants of each variant of the experiment were analyzed for determination the average number of nodules on the roots of one plant.
P ≤ 0,05.Figure 2
Dynamics of NFA of nodules of alfalfa plants inoculated by mono- and binary suspensions of microorganisms (micromoles of ethylene formed by nodules per plant per 1 h). 1: phase of stooling, 2: phase of budding, and 3: phase of flowering,P≤0,05.It is known that the use of active strains of root nodule bacteria and their associations with other microorganisms affect the formation and functioning of the photosynthetic complexes through the nitrogen status of a host plant. Presence of nitrogen available to plants determines the efficiency of symbiotic systems.Mono- and binary suspensions inoculations of seeds showed positive dynamics of accumulation of photosynthetic pigments in the leaves of alfalfa compared with the absolute control (Figure3). The most significant differences were observed in plants whose seeds had been inoculated with nitrogen-fixing consortium of microorganisms (chlorophylla and chlorophyllb increased by 114.6 and 82.9%) compared with the corresponding option of treatment only by strain T17. It is known that the content of chlorophyll in the leaves is directly proportional to the intensity of nitrogen fixation and depends on symbiotic properties of root nodule bacteria [31–33]. Increasing the number of pigments in the leaves of alfalfa inoculated with binary bacterial suspension indicates the ability ofN. PTV to enhance the functional activity of rhizobia, which are directly interfaced with the intensity of nitrogen fixation.Figure 3
(I): content of chlorophyll (mg/g of raw material) in leaves of alfalfa inoculated by mono- and binary suspensions of microorganismsS. meliloti Т17 andN. PTV. 1: control (without inoculation); 2: inoculation by N. PTV; 3: inoculation byS. meliloti Т17; 4: inoculation by consortium ofS. meliloti Т17 +N. PTV. II: net assimilation rate (mg СО2/( plant·hour)) of alfalfa inoculated by mono- and binary suspensions of microorganismsS. meliloti Т17 andN. PTV. 1: inoculation byN. PTV; 2a: inoculation byS. meliloti Т17; 2b: inoculation by consortium ofS. meliloti Т17 +N. PTV (II(a): phase of budding and II(b): phase of flowering).Available forms of nitrogen, such as mineral and symbiotrophic, positively affect not only the formation of high grade, but also functional state of the plant photosynthetic apparatus. The net assimilation rate also demonstrates the effectiveness of the binary compositionS. meliloti T17 +N. PTV. In particular, in the budding stage of these plants the net assimilation rate exceeded 12.7%, while in the phase of early flowering it increased by 43.7% of the corresponding rate during inoculation only by T17 (Figure 3).The net assimilation rate of plant leaves typically is closely correlated with the content of nitrogen, and nitrogen is presented mainly in amino acids and proteins. Rubisco, the major cell photosynthetic enzyme of CO2 assimilation, represents more than half of the soluble cell proteins in leaf. Obviously, the intensification of NFA in the binary composition was the main reason for the increase of plant assimilation rate. However, it is possible that more active symbiotic apparatus, which is formed on the roots of plants through binary inoculation, enhanced “request” on assimilates by the root system, thereby stimulating the photosynthetic activity of plant leaves. There is a gradient of transport forms of carbon, particularly sucrose, between roots and leaves in the conduction system and it accelerates the outflow of carbon from the leaves. This, in turn, eliminates restrictions by photosynthesis products imposed on the feedback principle and further accelerates photosynthetic carbon assimilation. Thus, the efficient operation of the symbiotic apparatus in inoculated plants greatly stimulated the accumulation of photosynthetic pigments and increased the net assimilation rate. The accumulation of organic matter contributes to the formation of the plant biomass, because the basis of the biological productivity of the plant organism, including those capable of symbiotic nitrogen fixation, is photosynthetic carbon assimilation [31].In consequence of artificial inoculation of alfalfa seeds by consortium of nitrogen-fixing microorganismsS. meliloti T17 +N. PTV the yield of green mass of plants increased by 17.9% and the protein content in the leaves increased by 12.0% compared to monoinoculation by strain T17 (Table 3). This is an evidence of the effective interaction of test organisms in the cyano-Rhizobium associations and their positive impact on the growth and physiological characteristics of alfalfa plants (Table 3).Table 3
Productivity and protein content in leaves of alfalfa, inoculated by mono- and binary suspensions of microorganisms.
Inoculants
Harvest of green mass of plant,g/vessel
Protein content in the leaves
I mowing
II mowing
Totalharvest
% to monoinoculationby rhizobium
% to monoinoculation by rhizobium
Control
17,68 ± 0,51
19,70 ± 0,64
37,38
13,2
N. PTV
21,40 ± 0,52
24,22 ± 0,76
45,62
14,6
S. meliloti Т17
21,81 ± 0,48
25,17 ± 0,30
46,98
18,32
S. meliloti Т17 + N.PTV
26,26 ± 0,37∗
29,15 ± 0,17∗
55,41
117,9
20,52
112,0The amino acid composition is the main criterion of the biological value of proteins. An index of a total amino acid composition of vegetative mass of the experimental inoculated variants of alfalfa plants increased in comparison to the control (without bacterial inoculation). The maximum quantity of lysine, the most essential and deficient amino acid in humans and animals, was recorded in leaves of alfalfa (Table4). As a result of using binary inoculation a total amino acid composition increased by 25.1%, compared with the case of inoculation only by T17. In particular, a quantity of essential amino acids increased by 33.9%, and a quantity of nonessential amino acids increased by 17.7% (Figure 4). At the same time, an increase of the content of methionine, histidine, arginine, and tyrosine was observed, which are present in small quantities in plant leaves, and this is one of the factors limiting the rate of biosynthesis of proteins, especially in generative organs. The results are a direct proof of the positive impact of cyanobacterial inoculation on the quality of agricultural products.Table 4
Amino acid content in leaves of alfalfa, inoculated by mono- and binary suspensions of microorganisms.
Amino acid
Content of amino acids (mg/100 mg DW)
Control
N. punctiforme
Т17
Т17 +N. punctiforme
Gamma-aminobutyric acid
0,065
0,088
0,085
0,123
Lysine
0,386
0,802
0,459
0,610
Histidine
0,094
0,301
0,171
0,232
Arginine
0,297
0,905
0,439
0,585
Asparagine
0,675
0,882
0,748
0,779
Threonine
0,278
0,623
0,383
0,496
Serine
0,321
0,698
0,413
0,533
Glutamic acid
0,876
1,931
1,083
1,395
Proline
0,376
0,610
0,419
0,548
Glycine
0,423
0,790
0,470
0,537
Alanine
0,479
0,895
0,581
0,644
Cysteine
0,054
0,262
0,057
0,079
Valine
0,245
0,651
0,301
0,423
Methionine
0,111
0,298
0,149
0,200
Isoleucine
0,175
0,439
0,233
0,273
Leucine
0,523
1,234
0,685
0,938
Tyrosine
0,201
0,534
0,285
0,253
Phenylalanine
0,398
0,835
0,453
0,626
Total
5,977
12,779
7,417
9,276Figure 4
Total content of essential and nonessential amino acids in leaves of alfalfa grown after mono- and binary inoculation by cyanorhizobial compositions of microorganisms: 1: control (without inoculation), 2: monoinoculation of alfalfa seeds by cyanobacteriumN. PTV, 3: inoculation of alfalfa seeds by Tn5-mutant strain ofS. meliloti T17, and 4: binary inoculation of alfalfa seeds by Tn5-mutant strain ofS. meliloti T17 +N. PTV.


## 3.2. Stress Response of Plants Inoculated with Microbial Consortium

It is known that the plant productivity rate and resistance index are inversely dependent values. A positive effect of the cyanobacterial consortium T17 +N. PTV on the productivity of alfalfa is shown in our study. It was logical to study the effect of the binary inoculation on plant resistance to the adverse effects of certain environmental factors. It is an extremely important issue. We have used herbicide diquat as a model stress factor. For a short duration (30 minutes) of diquat treatment the content of TBA-reactive products in photosynthetic tissues of plants that were inoculated with the strain T17 was reduced by 18% compared to plants without inoculation (control 2). In the case when plants were inoculated with the consortiumS. meliloti T17 +N. PTV the content of TBA-reactive products remained at the level of control. In the experiments with more prolonged action of the stress factor (60 min) the content of TBA-reactive products in plants inoculated only by the strain T17 decreased by 16.9% and in the case of binary inoculation the content of TBA-reactive products decreased by 25%. It should be noted that after 24 h of plants exposure with diquat, regardless of the inoculation agent used, reducing the amount of TBA-active products in photosynthetic tissues was not observed compared with the control. At the same time, in the experiment with the use of the consortium of microorganisms a difference (15.4%) with the inoculation only by strain T17 was marked (Figure 5). At short-term action of diquat (30 min) a rate of SOD activity in photosynthetic tissues of plants inoculated withS. meliloti T17 +N. PTV was 2.5 times higher than in controls and by 42.5% in plants, inoculated by strain T17. After herbicide treatment during 60 minutes a significant altering of SOD activity in inoculated plants (irrespective of whether a mono- or binary inoculation) was not observed. However, in comparison to the control, this difference was significant; the enzyme activity was increased by 54%. Under long-term stress (24 h) in plants inoculated with strain T17, SOD activity remained at the same level as for short-term exposure. In plants, the seeds were treated with consortiumS. meliloti T17 +N. PTV, for the same conditions; this index decreased by 23.4% compared with the control and 34.4%, in comparison with the plants inoculated by strain T17 (Figure 6). Thus, the plants inoculated with algae-rhizobial composition proved to be more resistant to oxidative stress. It is possible due to the increased level of NFA of their symbiotic system and thus the increase in the number of available forms of nitrogen for alfalfa plants and the possible participation of NO in the defense reactions. In the literature, there are two hypotheses about the mechanisms of NO action under conditions of stress. First, NO may act as an antioxidant, directly linking to ROS, thereby protecting cells from damaging their actions [34]. Secondly, NO can act as a signaling molecule that triggers a cascade of reactions that lead to the expression of specific genes [35]. In their chemical and physical properties small molecule, rapid metabolism, lack of charging, and high diffusion coefficient of NO are well suited for the role of intracellular signaling mediator of plant stress responses.Figure 5
Content of TBA-active products in alfalfa leaves after herbicide diquat treatment: А: for 30 min, B: for 60 min, and C: for 24 h. 1: control (without inoculation and herbicide diquat treatment); 2: control (without inoculation, with herbicide diquat treatment); 3: inoculation by Tn5-mutant ofS. meliloti Т17, with herbicide diquat treatment; 4: inoculation by Tn5-mutant ofS. meliloti Т17+N. PTV, with herbicide diquat treatment.Figure 6
SOD activity in alfalfa leaves after herbicide diquat treatment: А: in 30 min, B: in 60 min, and C: in 24 h. 1: control (without inoculation and herbicide diquat treatment); 2: control (without inoculation, with herbicide diquat treatment); 3: inoculation by Tn5-mutant ofS. meliloti Т17, with herbicide diquat treatment; 4: inoculation by Т17 +N. PTV, with herbicide diquat treatment.Thus, the inoculation of alfalfa seeds by a consortium of nitrogen-fixing microorganismsS. meliloti T17 +N. PTV increased the nitrogenase activity of root nodules, increased the net assimilation rate, and increased productivity and product quality, and also the stability of alfalfa plants under the influence of oxidative stress induced by herbicides.


## 3.3. Molecular Typing and Phylogenetic Analysis of CyanobacteriumNostoc PTV

One of the main goals of this study was the molecular typing and phylogenetic analysis of a new cyanobacterial isolateN. PTV originated from the Institute of Hydrobiology of Academy of Science of Ukraine. As it was shown above, this cyanobacterium is effective for soil algalization. As a component of algae-rhizobium compositions, this cyanobacterium stimulates germinative energy, growth, and productivity of legumes.To identify and to determine the phylogenetic positions of the new cyanobacterial isolateN. PTV we used a partial sequence of thenifH gene (342 bp), encoding nitrogenase reductase, and 16S ribosomal RNA gene cluster (1765 bp) as molecular markers. Comparison of thenifH gene sequence and rRNA gene cluster sequence of cyanobacteriumN. PTV with all the sequences present at the GenBank by using the program Blast (https://blast.ncbi.nlm.nih.gov/Blast.cgi?PROGRAM=blastn&PAGE_TYPE=BlastSearch&LINK_LOC=blasthome) shows that this strain has no full similarity with any of early investigated organisms.Comparison of rRNA gene cluster sequence (1765 bp) of the cyanobacteriumNostoc sp. PTV revealed that this cyanobacterium shows the highest similarity with several strains ofN. muscorum andN. commune (Table 5). In general, support for branching in the tree, based on a fragment of 16S rRNA gene sequence (Figure 7), is worse in comparison with the reconstruction of the phylogeny of cyanobacteria based on the sequence of the genenifH (Figure 8).Table 5
BLAST results obtained by querying the 16S–23S rRNA gene cluster ofNostocsp. PTV with GenBank and geographical and ecological origins of the hits.
Closest GenBank relative
GenBank access number
Query coverage, %
Score, %
Identity, %
E value
Origin of the strain and reference
Nostoc sp. HA4355-MV2 clone p9D
HQ847576
98
2872
97
0.0
Maniniholo Cave wall, near HaenaUSA: Kauai, Hawaii
Nostoc muscorum CCAP 1453/22
HF678509
98
2531
93
0.0
Scottish Association for Marine Science, Molecular and Microbial Biology, Dunstaffnage Marine Laboratory,  Oban, PA37 1QA, United Kingdom
Anabaena variabilis ATCC 29413
CP000117
98
2457
92
0.0
It has been studied extensively for over 40 years and is the strain of choice for many laboratories throughout the world
Nostoc sp. PCC 7120
BA000019
98
2453
92
0.0
Complete genomic sequence of the filamentous nitrogen-fixing cyanobacteriumAnabaena sp. (Nostoc) strain PCC 7120 is available
Nostoc commune NC1 clone 10
EU586726
98
2441
91
0.0
John Carroll University, 20700, North Park Boulevard, University Heights, OH 44118, USA
Nostoc commune NC1 clone M2
EU586725
98
2441
91
0.0
John Carroll University, 20700, North Park Boulevard, University Heights, OH 44118, USA
Nostoc commune NC5 clone 10
EU586727
98
2437
91
0.0
Biology, John Carroll University, 20700, North Park Boulevard, University Heights, OH 44118, USA
Nostoc commune NC1
EU784149
98
2428
91
0.0
Nostoc commune NC1 was isolated from soil (subaerophyt) in Třeboň/Czech republic in 2006.
Nostoc commune NC5 clone 11
EU586728
98
2423
91
0.0
Biology, John Carroll University, 20700,  North Park Boulevard, University Heights, OH 44118, USA
Nostoc ellipsosporum CCAP 1453/15
HE975023
94
2399
92
0.0
Scottish Association for Marine Science,  Molecular and Microbial Biology, Dunstaffnage Marine Laboratory, Oban PA37 1QA, United Kingdom
Nostoc cf. punctiforme Bashkir clone 6A
EU586732
96
2378
92
0.0
John Carroll University, 20700,  North Park Boulevard, University Heights, OH 44118, USA
Calothrix sp. HA4356-MV2 clone p8i
JN385289
98
2361
90
0.0
Cave wall scraping, Maniniholo Cave  near Haena, USA: Kauai, Hawaii
Calothrix sp. HA4340 LM2
KF417425
98
2361
90
0.0
Cave, USA: Kauai, Hawaii, Maniniholo Cave
Anabaena sp. CCAP 1403/4A
HE975015
93
2360
92
0.0
Scottish Association for Marine Science, Molecular and Microbial Biology, Dunstaffnage Marine Laboratory,  Oban PA37 1QA, United Kingdom
Nostoc muscorum CCAP 1453/8
HF678508
93
2358
92
0.0
United Kingdom: Scotland
Calothrix sp. HA4356-MV2 clone p8i
JN385289
98
2356
90
0.0
Cave wall scraping, Maniniholo Cave  near Haena, USA: Kauai, Hawaii
Cylindrospermum moravicum CCALA 993 clone operon 1
KF052607
97
2331
94
0.0
Cave sediment, Czech Republic: Amaterska Cave, South Moravia
Nostoc punctiforme PCC 73102
CP001037
97
2331
91
0.0
A symbiont from a cycad
Nostoc sp. Peltigera malacea DB3992 cyanobiont
JX219483
97
2322
91
0.0
Cyanobiont of lichenized fungiPeltigera malacea, Iceland
Nostoc muscorum CCAP 1453/20
HF678506
95
2318
91
0.0
Scottish Association for Marine Science, Molecular and Microbial Biology, Dunstaffnage Marine Laboratory, Oban PA37 1QA, United Kingdom
Nostoc sp. 10Dp66E
JQ259187
98
2318
90
0.0
From association withDynamena  pumila L., White Sea, Russia
Cylindrospermum catenatum CCALA 999 clone operon 1
KF052615
97
2309
94
0.0
Soil, Slovakia: forest above Stara Brzotinska Cave, Slovak Karst
Trichormus anomalus HA4352 LM2
KF417426
96
2309
92
0.0
Cave, USA: Kauai, Hawaii, Maniniholo Cave
Cylindrospermum sp. HA4236-MV2 clone p4
JN385290
98
2309
89
0.0
Taro field, Makiki Nature Center, USA: Oahu, Hawaii
Cylindrospermum  catenatum CCALA 996 clone operon 1
KF052611
97
2307
94
0.0
Soil, Czech Republic: Amaterska Cave, South Moravia
Tolypothrix campylonemoides FI5-MK38 clone p10D
JQ083654
98
2305
90
0.0
Sand, USA: Fort Irwin NTC, San Bernardino Co., California
Cylindrospermum catenatum CCALA 990 clone operon 1
KF052601
95
2302
94
0.0
Soil, Czech Republic: Benešov nad Černou, South  Bohemia
Spirirestis rafaelensis WJT-71-NPBG6 clone p1B
JQ083656
98
2300
90
0.0
Joshua Tree National Park, USA: Joshua Tree Forest, San Bernardino Co., California
Cylindrospermum badium CCALA 1000 clone operon 1
KF052616
97
2298
94
0.0
Reclaimed coal mine soil, USA: Pyramid State Recreation Area, Illinois
Cylindrospermum catenatum CCALA 991 clone operon 1
KF052603
97
2293
94
0.0
Soil, Czech Republic: Most Region, North Bohemia
Spirirestis rafaelensisWJT-71-NPBG6 clone p1A
JQ083655
98
2291
89
0.0
Joshua Tree National Park, USA: Joshua Tree Forest, San Bernardino Co., California
Nostoc sp. Peltigera membranacea cyanobiont N6
JX975209
97
2289
91
0.0
Symbiont ofPeltigera membranacea lichen, Iceland
Cylindrospermum pellucidum CCALA 992 clone operon 1
KF052605
97
2287
94
0.0
Cave sediment, Slovakia: Dlha chodba in Domica Cave system, Slovak Karst
Hassallia sp. EM2-HA1 clone p4B
HQ847555
98
2282
89
0.0
Soil, Mojave National Preserve, USA: San Bernardino Co., California
Tolypothrix tenuis f. terrestris UFS-BI-NPMV-1A2-F06 clone p13E
JQ083651
98
2277
89
0.0
Arid soil after a burn, foothills of  the Onaquee Mts. USA: Utah
Nostoccf.commune 257-16
HQ877826
96
2271
90
0.0
Subaerial, on Bonampak's archeological building walls, Mexico: Chiapas
Hassallia sp. CNP3-B3-C04 clone p5D
HQ847556
98
2271
89
0.0
Soil, Needles District, Virginia Park, Canyonlands National Park, USA: San Bernardino Co., California
Uncultured cyanobacterium clone Emix3.12
JX887892
92
2269
91
0.0
Freshwater microbial matKonstanz,  Germany
Cylindrospermum muscicola SAG 44.79 clone operon 1
KF111150
96
2268
93
0.0
SoilFrance: Gif-Sur-Yvette, Ile-de-France Region
Tolypothrix tenuis f. terrestris UFS-BI-NPMV-1A2-F06 clone p13F
JQ083652
98
2268
89
0.0
Arid soil after a burn, foothills ofthe Onaquee Mts.USA: Utah
Hassallia sp. CM1-HA11 clone p8A
JQ083650
98
2268
89
0.0
Sandy loam near gypsum mine,USA: Clark Mountains, San Bernardino Co.,California
Hassallia sp. CM1-HA08 clone p7B
JQ083648
98
2268
89
0.0
Sandy loam near gypsum mine,USA: Clark Mountains, San Bernardino Co.,California
Nostoc cf. commune 257-20
HQ877827
94
2266
91
0.0
Biofilms of N. cf. commune were collected at Bonampak archeological area in 2008 from two sites on the building walls (Chiapas, Mexico).
Tolypothrix campylonemoides FI5-MK38 clone p10A
JQ083653
98
2266
89
0.0
SandUSA: Fort Irwin NTC, San Bernardino Co.,California
Hassallia sp. CM1-HA08 clone p7F
HQ847554
98
2266
89
0.0
Soil, Clark Mountains, near gypsummineUSA: San Bernardino Co., California
Desmonostoc sp. HA7617 LM4
KF417429
96
2241
90
0.0
USA: Kauai, Hawaii, Waikapalae Cave
Camptylonemopsis sp. HA4241-MV5 clone B2-3 + p4
JN385292
96
2223
93
0.0
Moleka streamUSA: Oahu, Hawaii
Anabaena circinalis 33-10 isolate
EF634474
98
2199
88
0.0
Ohau Channel,  New Zealand
Tolypothrix sp. PCC 7504 isolate DBSU 18
FJ660999
90
2194
92
0.0
FreshwaterAquarium, Sweden
Nostoc sp. UAM 307
HM623782
70
2111
98
0.0
Rock surface of calcareous riverSpain: Matarranya River, Teruel, East Spain
Rivularia sp. 1PA23
FJ660980
92
2021
88
0.0
Pozas Azules I, MexicoMicrobialitefreshwater
Nostoc sp. 8964:3
AM711541
66
2006
99
0.0
Host isGunneraprorepens (Angiospermae), New Zealand
Rivularia sp. 1PA21
FJ660978
92
2004
88
0.0
Institute of Ecology,UNAM (Mexico)
Nostoc linckia var. arvense IAM M-30
AB325907
65
1999
99
0.0
Cultivated samples from the Institute ofMolecular Biosciences at the University of Tokyo
Aphanizomenon ovalisporum ILC-164
JF768745
92
1988
93
0.0
Lake Kinneret, Israel; Banker et al., 1997 [5]
Nostoc muscorum Ind33
HM573462
65
1988
99
0.0
Paddy field,India: Agricultural Farms, Banaras Hindu University, Varanasi, Uttar PradeshFigure 7
Phylogenetic relationships ofNostoc sp. PTV (designated by black square) inferred under the posterior probability criterion (MrBayes) from the gene for 16S rRNA, partial sequence information. Numbers at the nodes indicate the Bayesian statistical support values (posterior probabilities multiplied by 100); only values higher than 50% are given. The scale bar indicates the number of substitutions per nucleotide position.Figure 8
Phylogenetic relationships ofNostoc sp. PTV (designated by black square) inferred under the posterior probability criterion (MrBayes) from the gene fornifH, partial sequence information. Numbers at the nodes indicate the Bayesian statistical support values (posterior probabilities multiplied by 100); only values higher than 50% are given. The scale bar indicates the number of substitutions per nucleotide position.The group ofNostoc strains and species, which includesNostoc PTV, forms a cluster with the minimum of allowable support, 0.95. Hierarchy of strains (HA 4355-MV2, PTV, and 8964) andNostoc species (N. muscorum andN. linckia) cannot be evaluated because of the low topological support of this site of the tree: credibility values range from 0.56 to 0.94. It is difficult to discuss a relation ofNostocPTV strain to strain HA 4355-MV2, due to the very low values ​​of the other branches in the cluster, and very scarce information about the HA-MV2 4355 strain clearly does not help to solve the problem of their possible relationship.N. muscorum is discussed below.N. linckia is also a freshwater strain and could be isolated in some terrestrial niches. Interestingly, theNostoc strain UAM 307 is quite clearly differentiated from the other representatives of Nostocaceae (0.95). Being sufficiently close to strain ofNostoc PTV, this cyanobacterium has some significant features that provided the separation of this strain into the other branch of the common withNostoc PTV cluster.Even more interesting detail is that the last significant branch (credibility value is equal to unity) of the cluster is formed by the strain ofN. muscorum Ind33, which is significantly aside not only from the desired strain of PTV, but also from the different strains of the same species (CCAP 1453-22). Thus, the strain ofNostoc PTV has teamed up with members of their own genus.Outgroup of this dendrogram is represented by two strains ofRivularia (this kind of cyanobacteria forms heteropolar threads; their trichomes are densely agglomerated, covered with a total mucus). The genus is represented only by the species often living on calcareous substrates, but there are rare epilithic and epiphytic species.Comparison ofnifH sequence of cyanobacterium PTV revealed that this strain shows the highest similarity with several strains ofNostoc (Table 6). The closest relative isNostoc muscorum UTAD N213, purified from rice paddy in Mondego River Basin (Portugal). Phylogenetic analysis (Figure 8) revealed that the cyanobacterium PTV forms a minicluster withNostoc muscorum UTAD N213.N. muscorum is a free-living filamentous cyanobacterium, which inhabits both terrestrial and freshwater aquatic environments. They are phototrophic organisms performing photosynthesis and also fixing atmospheric nitrogen [36].Table 6
BLAST results obtained by querying thenifH gene of Nostocsp.PTV with GenBank and geographical and ecological origins of the hits.
Closest GenBankrelative
GenBank number
Query coverage %
Score %
Identity %
E value
Origin of the strain and reference
Nostoc muscorum UTAD N213
GQ443450.1
100
612
99
7
e
-
172
Rice paddy in Mondego River Basin, Portugal
Nostoc muscorumclone CC1090A1
AY221814.1
94
576
99
5
e
-
161
Ocean Sciences Department, University ofCalifornia, Santa Cruz, CA 95064, USA
Nostoc commune (UTEX 584)
L23514.1
99
565
97
9
E
-
158
Scotland
Nostoc sp. UAM 362
JQ514115.1
99
553
96
5
e
-
154
Rock surface of calcareous river with brackish water,Spain: Muga, Girona (Northeast Spain)
Nostoc sp. Baikal
JN887856.1
99
517
94
4
e
-
143
Nitrogen-fixing cyanobacteria from Lake Baikal
Nodularia spumigena AV1
GQ456132.1
99
511
93
2
e
-
141
The surface waters of the Baltic Sea, Stockholm, Sweden
Tolypothrix sp. UAM 379
JQ514114.1
99
462
90
8
E
-
127
Rock surface of calcareous river with brackish water,Spain: Muga, Girona (Northeast Spain)
Tolypothrix sp. UAM 378
JQ514113.1
99
462
90
8
E
-
127
Rock surface of calcareous river with brackish water,Spain: Muga, Girona (Northeast Spain)
Tolypothrix sp. UAM 415
JQ514120.1
99
453
89
4
E
-
124
Rock surface of calcareous river with brackish water,Spain: Muga, Girona (Northeast Spain)
Tolypothrix sp. UAM 413
JQ514119.1
99
453
89
4
E
-
124
Rock surface of calcareous river with brackish water,Spain: Muga, Girona (Northeast Spain)
Nostoc PCC 6720
Z31716.1
99
430
88
4
E
-
117
Nostoc PCC 6720 was previously known as Anabaenopsis circularis.This is a freshwater species
Anabaena sp. L-31
L04499.1
99
426
88
5
E
-
116
The filamentous, heterocystous, nitrogen-fixing freshwater cyanobacterium
Anabaena PCC7120
J05111.1
99
426
88
5
E
-
116
http://wiki.annotation.jp/Kazusa:CyanoBase:Anabaena_sp._PCC_7120
Nostoc sp. UAM 367
JQ514116.1
100
423
87
7
E
-
115
Rock surface of calcareous river with brackish water,Spain: Muga, Girona (Northeast Spain)
Anabaena siamensis TISTR 8012
DQ176436.2
100
414
87
3
E
-
112
Anabaena siamensis is a filamentous heterocystous nitrogen-fixing cyanobacterium which originally was isolated from a rice paddy field in Thailand
Mastigocladus laminosus CCMEE 5324
EF570558.1
100
414
87
3
E
-
112
The cosmopolitan thermophilic cyanobacteriumMastigocladus laminosus from the University of Oregon's Culture Collection of Microorganisms from Extreme Environments (CCMEE)
Fischerella UTEX1931
U49514.1
100
414
87
3
E
-
112
Thermophilic cyanobacterium (synonym:Mastigocladus laminosus)
Anabaena sphaerica UTEX “B 1616”
DQ439648.1
99
408
87
1
E
-
110
Department of Chemistry and Chemical Engineering, University of Sheffield, Mappin Street, Sheffield,South Yorkshire S1 3JD, United Kingdom
Anabaena sp. A2
AF124377.1
99
408
87
1
.
E
-
110
Molecular Evolution, BMC, Uppsala University, Husargatan 3, 751 24 Uppsala,  Sweden
Anabaena azollae
L34879.1
99
435
88
1
E
-
118
Anabaena azollae 1a, a putative symbiont of Azolla caroliniana
Anabaena variabilis
U89346.1
99
435
88
1
E
-
118
Anabaena variabilis ATCC 29413 is a filamentous cyanobacterium that produces heterocysts and fixes nitrogen under a variety of environmental conditionsN. muscorum is the most common type ofNostoc in terrestrial ecosystems and is widely spread, due to the adaptability to many adverse conditions. It forms a symbiotic relationship with many types of terrestrial plants and fungi.It is known thatN. muscorum has great effect on soil biology and productivity which makes it an attractive soil inoculant. This cyanobacterium is able to obtain carbon and nitrogen from the air and has an advantage over heterotrophic soil inoculants, which are usually limited by carbon [37].It also benefits plants and other soil bacteria by increasing soil organic matter in the form of carbohydrates and provides biological organic nitrogen that can be assimilated by plants [38].N. muscorum helps to create the environment conditions to further colonization and growth by plants and other microorganisms [39].Inoculation of theN. muscorum isolates caused a significant effect on growth of wheat and maize plants. Cyanobacterial inoculation positively affected pigment content, increased plant shoot and root dry weight, and increased leaf area [40].In general, the topology of the dendrogram (Figure8) has a good support; the main branch nodes are characterized by high credibility values.Nostoc PTV is in the same cluster withNostoc sp. UAM-362 andNostoc commune.Nostoc sp. UAM-362 was isolated from the rock surface of calcareous river with brackish water in Spain: Muga, Girona (Northeast Spain).N. commune is a colonial species of cyanobacterium. As well asN. punctiforme, N. communeis able to survive in extreme conditions such as polar regions and arid areas.Three more clusters are presented as the parts of the large one: two single clusters, represented byNostoc sp. Baikal (nitrogen-fixing cyanobacteria from Lake Baikal) and byNodularia spumigena from family Nostocaceae.Nodularia occurs mainly in brackish or saline waters.Nodularia cells occasionally can form heavy algal blooms. Some strains produce a toxin (nodularin), which is harmful to human health [41].The third cluster is formed by four strains ofTolypothrix and by one strain ofNostoc sp. UAM-367 (isolated from rock surface of calcareous river with brackish water in Spain: Muga, Girona). CyanobacteriaTolypothrix grow in unpolluted waters; several species are found in swamps, known aerophilic species growing on the bark of trees, in the wet sands, on wet rocks, and so forth.Two species, and one strain (PCC 7120) ofAnabaena, representing a family of filamentous cyanobacteria Nostocaceae, belong to this large cluster with a poor resolution (a credibility value of branching is 0.71). These cyanobacteria exist in the form of plankton; some species are symbionts of plants.Anabaena is one of the four genera of cyanobacteria that produce neurotoxins.Anabaena is a model for the study of cell differentiation and differential gene expression during nitrogen fixation [42].A. siamensis andA. sphaerica are freshwater species. This mega cluster consisting of described species of cyanobacteria is well differentiated from the other two clusters: a single one represented by strainAnabaena L-31 (freshwater cyanobacterium) and a poorly differentiated cluster, which consists of two strains ofAnabaena (A2 and PCC 7120) and two well-differentiated species ofAnabaena, A. azollae andA. variabilis.A. azollae forms symbiosis with water fernAzolla.Outgroup for the described species ofNostoc andAnabaena is represented by ​​Mastigocladus laminosus and by member of the genusFischerella (strain UTEX 1931). The first organism is a typical representative of the genusMastigocladus.Fischerella represents another squad, Stigonematales. Both types of reference are truly branching filamentous forms of thermophilic cyanobacteria.


## 3.4. Gene Transfer intoNostoc PTV Cells

Nostoc PTV cells were tested for their ability to conjugational DNA transfer. As a result of plasmid pRL692 transfer into cyanobacterial cells several hundred transconjugant colonies were selected on selective plates that contained solid BG-11 medium and antibiotics (Sp10 and Sm2). On control plates antibiotic-resistant colonies were absent (data not shown). In future experiments we plan to use this experimental approach for transposon mutagenesis ofNostoc PTV and selection of the new mutants with interesting characteristics.


## 4. Conclusions

The use of microbial consortium newly identifiedNostoc PTV strain together withSinorhizobium meliloti T17 was more efficient than the use of the single-rhizobium strain for alfalfa plant inoculation. This treatment provides an intensification of the processes of nitrogen fixation and photosynthesis and stimulates growth of above-ground plant mass and rhizogenesis and leads to increased productivity ofMedicago sativa L. and improved amino acid composition of plant leaves. Phylogenetic analysis by using two different molecular markers showed that this new cyanobacterium belongs to a cluster of the genusNostoc, with the closest relative ofNostoc muscorum. Gene transfer of transposon bearing plasmid DNA has been shown for cyanobacteriumNostoc PTV. It makes this strain very attractive model for future genetic and physiological experiments and biotechnological applications.



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*Source: 202597-2015-05-31.xml*