MICROBIAL INTERACTIONS IN THE DEVELOPMENT OF THE BIOMASS OF GLIRICIDIA

The objective of this work was to evaluate the interaction of microorganisms and phosphorus dosages in the development of gliricidia. The experimental design was completely randomized with six treatments (control, native microbial inoculant, and four arbuscular mycorrhizal fungi isolates: UFLA05 Gigaspora albida, UFLA351 Rhizoglomus clarum, UFLA372 Claroideoglomus etunicatum, and UFLA401 Acaulospora morrowiae), with four replicates. The parameters evaluated were: height plant, the number of branches, shoot and root dry mass matter, root length and volume, leaf phosphorus, mycorrhizal colonization, the number of spores of the arbuscular mycorrhizal fungi, the number of nodules of nitrogen fixing bacteria, and the presence of endophytic dark septate fungi, after 95 days of inoculation. The high mycorrhizal colonization of gliricidia does not guarantee an increase in biomass, which depends on the interaction of the arbuscular mycorrhizal fungi, the endophytic dark septate fungi, the nitrogen fixing bacteria, and the endophytic bacteria. Gliricidia was responsive to the inoculation of the native microbiota, UFLA372 and UFLA401. Mycorrhizal colonization by UFLA401 was influenced by the presence of nitrogen fixing bacteria. Gliricidia was not responsive to the inoculation of UFLA05 and UFLA351. The presence of the endophytic dark septate fungi did not inhibit mycorrhization and the formation of nodules of nitrogen fixing bacteria in gliricidia.


INTRODUCTION
The Gliricidia sepium (Jacq.)Walp is a treesized species belonging to the family Fabaceae that originated in Central America.It has been used for green manuring, wind breaking, hedging, wood production, and for recovery of degraded areas, since it tolerates acidic and low fertility (EIRAS; COELHO, 2011).In addition, due to its high protein content, gliricidia is used as a forage in the Brazilian Northeast (MARIN et al., 2006).
The protein content present in the biomass of the Fabaceae members is related to the biological fixation of nitrogen by diazotrophic bacteria, which are responsible for the amount of nitrogen that is directly available to the plant.Specifically in nutrient-poor soils, the fixation of nitrogen by the bacteria allows the plant to grow by promoting a buildup of mass matter via synthesis of amino acids and proteins (MOREIRA;SIQUEIRA, 2006).Florentino et al. (2014) cites that gliricia preferentially symbioses with the fast-growing rhizobia isolates, whose potential in the biological fixation of nitrogen can vary with the edaphoclimatic conditions of the region where the plant is grown.Further, a study by E Mello, Silva and Saggin-Júnior (2012) emphasizes that depending on the microorganism-plant interaction, the formation of nodules of nitrogen-fixing bacteria in the gliricidia can be stimulated by the presence of an arbuscular mycorrhizal fungi (AMF).Lastly, Tavares et al. (2012) observed that with a mycorrhizal colonization in Mimosa caesalpinaefolia Benth, there was an increase in the dry matter mass of the root nodules of the nitrogen-fixing bacteria by 1900%.
The symbiosis between the mycorrhizal fungi and the fabaceae is important for the supply of nitrogen and phosphorus to the plant and to the nitrogen-fixing bacteria (TWUM-AMPOFO, 2008;JALONEN et al., 2013).Together, such symbiosis may favor growth and survival of plants in adverse conditions, such as drought (AUGÉ, 2001), a common occurrence in the Northeastern Brazil.However, the benefits of the fungi-plant interaction are not only related to nutrition.The arbuscular mycorrhizal fungi can promote soil aggregation through the action of a glycoprotein called glomalin, excreted by mycelia, which contributes to soil conservation (RUBIN;STÜRMER, 2015).
In addition to the nitrogen-fixing bacteria and the arbuscular mycorrhizal fungi, plants can be colonized by other microorganisms such as the endophytes.Santos and Varavallo (2011), in their literature review, report that the endophytes develop within the plant, without any visible symptoms of their presence, although they can promote the growth of the host plant by increasing the photosynthetic efficiency.In addition, these authors point out that some endophytes may favor the survival of plants under conditions of drought, salinity, and / or induce resistance to phytopathogens.Among these microorganisms, the endophytic dark septate fungi, characterized by the presence of a septate and a melanized hyphae, are able to promote growth, inhibit phytopathogenic agents (RIBEIRO et al., 2011;YAN et al., 2015), and influence the mycorrhizal-plant symbiosis.Therefore, depending on microbial interaction and environmental conditions, all these factors may contribute to the host plant's growth, (LINGFEI; ANNA; ZHIWEI, 2005).
In the existing literature, there are no studies related to the interaction of the diazotrophic bacteria, the mycorrhizal fungi, and the endophytic dark septate fungi in the development of gliricidia.Therefore, the objective of this study was to evaluate the interaction of these endophytic microorganisms in the development of the biomass of Gliricidia sepium, grown in a greenhouse.The experiment was conducted from August to December 2016, in the municipality of São Cristóvão, Sergipe -Brazil, where the climate is classified as tropical with dry summer and rainy winter, according to Köppen (ALVARES et al., 2014).

MATERIAL AND METHODS
The isolates of arbuscular mycorrhizal fungi UFLAs were donated by the Laboratory of Soil Microbiology, belonging to the Federal University of Lavras.The native microbial inoculant was obtained from a collection of 3 kg of rhizospheric soil from an adult gliricidia cultivated in an area adjacent to the Department of Agronomic Engineering, at the Federal University of Sergipe, Campus de São Cristóvão, Sergipe, Brazil.
The multiplication of the UFLAs mycorrhizal isolates was performed on a substrate based on sandy soil autoclaved at 120ºC and 1 atm for one hour and repeated after 24 h.The autoclaved soil was distributed in disinfested plastic vessels with 0.5% sodium hypochlorite for 20 minutes in a 2:1 ratio (sand: mycorrhizal inoculum).The inoculant, composed of spores of mycorrhizal fungi, colonized root fragments, and sand, was distributed among the layers of the autoclaved sand.Seeds of Sorghum bicolor L. Moench, was sown and the incubated in a greenhouse with micro sprinkler irrigation.After 60 days of cultivation, the aerial part of the sorghum was cut and the irrigation suspended for 15 days to stimulate sporulation.
The multiplication of the native mycorrhizal inoculant was carried out by incubation of the rhizospheric soil collected from an adult gliricidia, in a covered plastic tray, without irrigation or the host plant, for induction of sporulation for 25 days.
To obtain the seedlings the gliricidia, the seeds were submitted for disinfestation by treating with 70% alcohol for one minute, followed by immersion in 0.1% sodium hypochlorite solution for one minute, with a subsequent triple wash in autoclaved distilled water, for one minute (ALFENAS; MAFIA, 2007).The disinfested seeds were arranged on an autoclaved filter paper to remove the excess water and then transferred to gearbox type plastic boxes containing approximately 200 g of autoclaved sandy soil.The plastic boxes with the soil and the seeds were transferred to a incubator maintained at a temperature of 25 ± 1ºC, with photoperiod of 10 hours of light, until the seedlings reached the final two pairs of leaves.Next, the seedlings were transplanted into disposable 50 mL plastic cups containing autoclaved sandy soil and incubated in the incubator for another six days under the same conditions described for germination.Every two days, 2.0 mL of autoclaved distilled water was applied per cup.On the sixth day, the plastic cups with the sandy soil and the seedlings were transferred to a greenhouse for acclimatization for seven days.
After the acclimation period, the seedlings were transplanted into 500 mL disposable plastic cups, and autoclaved sandy soil mixed with 50 g of microbial inoculant was added.The inoculant was composed of soil, spores from the mycorrhizal isolates, and root fragments of the mycorrhizal multiplier host plant.The sandy soil that used was classified as sandy-loam with a pH 6.9, 4.7 g kg -1 organic matter, 1.3 cmolc dm -3 CTC, 76.5% V, 8.0 mg kg -1 of potassium, and 8.0 mg kg -1 phosphorus.
The number of spores in the inoculants of UFLA05, UFLA351, UFLA372, and UFLA401 was, on average, 35.7 spores per 50 g of soil.In the native microbial inoculant, the number of spores of the arbuscular mycorrhizal fungi was 76.7 spores per 50 g of soil.The number of spores of the mycorrhizal fungi used as an inoculant was determined according to Gerdemann and Nicolson (1963).
The gliricidia seedlings were transplanted from cups to soil and inoculant, according to the specified treatments and distributed randomly in the greenhouse and cultivated for 90 days.The humidity of the greenhouse was maintained through irrigation by micro sprinkler, with flow rate of 45 liters per hour.The irrigation was triggered for one minute, four times a day, with an interval of three hours.The covering fertilization was carried out in the soil around the plants 21 days after transplant and inoculation, by the addition of 3.0 mL of a solution prepared with 10.0 g L -1 of a commercial fertilizer diluted in distilled water.This was repeated weekly for up to 60 days post inoculation.The chemical composition of the commercial fertilizer applied was 13% nitrogen (N), 5% phosphorus (P 2 O 5 ), 13% potassium (K 2 O), 5% sulfur, 1% calcium, 0.2% iron, 0.15% zinc, 0.08% manganese, 0.04% boron, 0.05% copper, and 0.005% molybdenum.After 20 days of inoculation, a leaf application of 2.0 g L -1 of copper sulfate was carried out to control bacterial blight.
The gliricidia cultivated in the greenhouse were evaluated for the following: plant height, the number of branches, shoot and root dry mass matter, root length and volume, leaf phosphorus levels, mycorrhizal dependency, mycorrhizal colonization, presence of endophytic dark septate fungi, the number of nodules of nitrogen fixing bacteria, and the number of mycorrhizal spores, after 95 days at inoculation.The surrounding field was evaluated for the presence of any endophytic microorganisms from the leaf tissue of an adult gliricidia.
To determine the height of the plant, a millimeter ruler was used and the measurements were made from the lap of the plant to its main bifurcation.The number of branches was obtained by direct counting.The root length was determined with a millimeter ruler and the root volume was analyzed by the principle of water displacement.The root cut at the height of the colon, was washed in running water and then transferred to a beaker containing 500 mL of distilled water.The volume of the displaced water was recorded.The resulting difference in volume was calculated (in mL).The shoot and root dry mass matter were determined using a semi-analytical balance after cutting at the height of the colon and drying the plant material in a forced air circulation oven at 60 o C until constant weight was attained.
The mycorrhizal dependency (MD) was evaluated for each parameter including, the number of branches, the shoot and root dry mass matter, the root length and volume, with respect to the control (without inoculation), using equation 1: , where PM = value of the parameter analyzed in the mycorrhizal plant and PC = value of the parameter analyzed in the control plant (without mycorrhizal).The mycorrhizal dependency has been classified by Machineski, Ballot and Souza (2011), where plants that presented values > 75% were classified as excessively dependent; from 50 to 75% as highly dependent; 25 to 50% as moderately dependent, and < 25% as marginally dependent or not respondent to inoculation.
The leaf phosphorus content of the gliricidia was determined after drying the leaves in a forced air circulation oven at 60ºC for three days.Afterwards, the leaves were ground in a knife mill with a 1 mm diameter sieve and submitted for the analysis of its phosphorus content, according to Malavolta, Vitti and Oliveira (1997).
To assess colonization, the intersection method was used, according to Giovannetti and Mosse (1980).The percentage of mycorrhizal colonization (MC) was calculated using equation 2: , where TNCRF is the total number of colonized root fragments and TNC is the total number of colonized and non-colonized root fragments.The intensity of mycorrhizal colonization (IMC) was evaluated from the root fragment analysis, as a function of the number of structures such as hyphae, vesicles, arbuscules, appressorium, and spores, according to a subjective scale: (+) presence of the 1 to 5 structures; (++) presence of 5 to 10 structures; (+++) presence of 10 to 20 structures; (+++++) presence of > 20 structures.The number of spores in the tested mycorrhizal isolates were evaluated in 50 g of the culture substrate by the wet sieving method according to Gerdemann and Nicolson (1963).
The number of nitrogen fixing bacteria nodules and the presence of endophytic dark septate fungi in all treatments, since they may be associated with the seeds was determined.The number of nodules of nitrogen fixing bacteria was evaluated by direct counting at the root level.The nodulation rate (TNOD) of the nitrogen-fixing bacteria in the mycorrhizal treatments was evaluated in relation to the control, by equation 3: , where NODmp is the number of mycorrhizal plant nodules, and NODcp is the number of control plant nodules.The presence of an endophytic dark septate was calculated as a percentage in relation to the number of root fragments analyzed, as previously described by Ribeiro et al. (2011).
The endophytic microorganisms present in the leaf tissue of the gliricidia from which the rhizospheric soil was collected to be used as a native inoculant, were isolated according to the methodology of Ribeiro et al. (2011), with some modifications.The endophytes were isolated in a commercial potato-dextrose-agar medium (39.0 g L -1 ), after disinfestation by immersing the leaf fragments (0.25 mm 2 ) in alcohol for 1 minute, followed by immersion in 0.1% sodium hypochlorite  % = ( )  100  % = [  −  ]  100 for 1 minute, and then triple washed in autoclaved distilled water (1 minute per wash).The incubation was performed in the incubator at 25 ± 1°C, without any photoperiod, for 7 days.In the culture medium, two distinct bacterial colonies were grown, whose taxonomic identification was performed by sequencing the Ribosomal 16S Gene (16S rRNA), following standard operating procedure BS.ME.017, at Embrapa Soja, Londrina, Paraná, Brazil, with certificate of analysis (CAS n.001/16).
The results were submitted for an Analysis of Variance (ANOVA) and in the cases where there was a significant difference, the Tukey Test was applied at 5% of significance to compare the means.
In the correlation analysis between the evaluated parameters, the t-Test was applied.The correlation and variance analyses were performed using the Assistat program.

RESULTS AND DISCUSSION
The mycorrhizal colonization of the gliricidia ranged from 58.6 to 82.7% when treated with native and UFLAs, with no difference between native inoculant and UFLAs tested (Table 1).Likewise, Sugai, Collier and Saggin-Júnior (2011) observed a high rate of mycorrhizal colonization of Anadenanthera macrocarpa (Benth) Brenam, with no difference between native and mycorrhizal isolates when tested on anthropic soil.These authors cited that this result may have been due to the absence of any diversity in the native arbuscular mycorrhizal fungi species in the anthropic soils.These authors also failed to identify the native microbial community and proposed the existence of one or more mycorrhizal species, similar to our work with gliricidia.
In gliricidia the values of mycorrhizal colonization observed to be above 50% is classified as high (CARNEIRO et al., 1998) and were similar to those found by Fagbola et al. ( 2001) on gliricidia inoculated with Glomus deserticola.However, Twum-Ampofo (2008) observed that the mycorrhizal colonization of gliricidia with Glomus clarum (92.2 to 96.4%) was significantly higher than the values observed with G. etunicatum (35.9 to 77.4%) and Gigaspora rosea (32.8 to 45.3%), which differs from the results obtained with the isolates UFLA351, UFLA372 and UFLA05, which did not present significant difference (Table 1).2013) observed that the greatest mycorrhizal colonization of gliricidia occurred up to 1 m away from the plant, probably due to the fact that the roots here are metabolically more active (ANGELINI et al., 2012).Thus, the cultivation of gliricidia in the 500 mL plastic cups may have favored high colonization, due to the lower depth and distance of the roots, even in the substrates with low organic matter and phosphorus content (Table 1).
The gliricidia inoculated with UFLA351 presented a mycorrhizal colonization with a higher percentage of hyphae compared UFLA05, UFLA372, and UFLA401 treatment, but did not show any difference compared to the control and the native inoculant (Table 1).The presence of this extra-radicular hyphae probably increased the area of water and nutrient absorption favoring the development of the plant (AUGÉ, 2001; SUGAI; COLLIER; SAGGIN-JÚNIOR, 2011).Moreover, the higher percent of hyphae also contributed to the formation of micro aggregates, which are important in the conservation of soil (RUBIN; STÜRMER, 2015), thereby facilitating the recovery of degraded areas.
Inoculation with UFLA05, UFLA372, UFLA401, and native the inoculant resulted in a higher percentage of vesicles than with the control and UFLA351 (Table 1).The presence of these vesicles in the UFLA05 was characterized by a contamination from the isolates UFLA351, UFLA372 and/or native, because this structure is characteristic of the genus Glomus and Paraglomus (MOREIRA; SIQUEIRA, 2006).The lower percentage of vesicles in the gliricidia inoculated with UFLA351 may be associated with a low organic matter content in the culture substrate (Table 1).Jalonen et al. (2013), andStürmer andSiqueira (2008) mentioned that carbon limitation often reduced the percentage of vesicles, a glycogen granules and lipids storage structure in fungi.However, the limitation of carbon and phosphorus in the culture substrate did not influence the intensity of colonization of gliricidia with the native treatments including UFLA372 (C.etunicatum) and UFLA401 (Table 1), suggesting that the formation of vesicles may depend on the AMF-plant interactions.
Evaluation of the fragments of the roots of gliricidia did not reveal any arbuscules, probably due to the presence of thick roots, which increases makes identification of this structure difficult.Similar obstacle was also reported by Sugai, Collier and Saggin-Júnior (2011) in their study on Anadenanthera macrocarpa (Benth) Brenam.However, Ferdousee, Misbahuzzaman and Hoque (2012) have reported the presence of arbuscules in gliricidia.Moreover, Walter et al. (2016), and earlier Mandyam and Jumpponen (2008), cited that the arbuscules are formed in poaceae under extreme environmental conditions, such as drought/excess rainfall or due to the seasonality.However, for Fabaceae spp.no such association between the time of the year and the formation of the arbuscules have been reported.
Mello, Silva and Saggin-Júnior (2012) emphasized that any evaluation of the functional compatibility between arbuscular mycorrhizal fungi and plants, should consider the sporulation capacity in the rhizosphere.In this context, the sporulation was 365.5 spores per 50 g of soil, on an average, without measurable difference between the treatments, except between UFLA05 (544 spores/50g) and UFLA351 (174, 3 spores/50g) (Table 1).Ferdousee, Misbahuzzaman and Hoque (2012) reported that the sporulation of the native mycorrhizal isolates inoculated in gliricidia was 60 spores per 100 grams of the substrate, with the presence of the genera Glomus, Acaulospora, and Entrophospora in the soil at a pH of 5.8.These authors mentioned that the Acaulospora is more tolerant to acidic pH, whereas Glomus species prefer neutral to alkaline soils.Such preferences may also influence the AMF-plant interaction, since the pH of the cultivation substrate was kept at 6.9 on our study.The presence of high humidity in the incubation oven during the experiment might have stimulated the sporulation of the fungal isolates tested.
The gliricidia was also colonized by the endophytic dark septate fungi without any detectable difference between the treatments (Table 1).
However, the presence of these endophytes did not influence the mycorrhizal colonization, except in the control treatment that presented a positive correlation (Table 2).Additionally, the gliricidia was colonized by nitrogen-fixing bacteria, without any significant difference in the number of nodules produced with or without the mycorrhiza, even though were not inoculated with the nitrogen-fixing bacteria.Compared to the control, the presence of the nitrogen fixing bacteria nodules was about 50% in the native inoculant treated.In this treatment, the nitrogenfixing bacteria nodules may have occurred due to the use of rhizospheric soil of the non-autoclaved as an inoculant of the gliricidia.Compared to the controls, the inoculation with the isolates from UFLA372 and UFLA401 favored an increase in nodulation up to 35.7 and 40.0%, respectively.In gliricidia inoculated with UFLA05 and UFLA351 the increase in nodulation was 7.0 and 2.0% respectively.In these treatments, the nodules of nitrogen-fixing bacteria were produced by an internal colonization of the seeds of the gliricidia by the bacteria.In addition, the lowest increase in the nodulation obtained with UFLA05 and UFLA351 treatment, was attributed to the smaller increment of mycorrhizal structures (ICM) observed in the gliricidia inoculated with these mycorrhizal isolates (Table 1).This observation differs from the results cited by Mello, Silva and Saggin-Júnior (2012), where they found that G. clarum stimulated more than five times the nodulation of the arboreal legume, Mimosa artemisiana compared to inoculation free control.
There was no correlation between the mycorrhizal colonization and the number of nodules of the nitrogen fixing bacteria in all the treatments.The observed high percentage of vesicles did not correlate with the number of nodules, except for UFLA401treatment, that presented negative correlation between these two parameters (Table 2).There was probably an antagonistic action between the mycorrhizal isolate and the nitrogen fixing bacteria.Similarly, Twum-Ampofo (2008) reported that the mycorrhizal colonization of gliricidia by Glomus clarum, G. etunicatum, G. intraradices, and Gigaspora rosea was inhibited by the inoculation of Rhizobium strains.
From the leaf tissue of the gliricidia growing in the fields, two endophytic bacteria namely, Paenibacillus illinoisensis and Pantoea stewartii were isolated.These bacterial species might be present in the soil of the native inoculant used for this work.In the literature, no interaction between gliricidia and P. stewartii or P. illinoisensis have been found.However, the presence of such asymptomatic bacteria in the plant may characterize a beneficial interaction as mentioned by Santos and Varavallo (2011).
According to Silva et al. (2016), the endophytic bacteria P. stewartii, isolated from sugar cane presented the ability to fix nitrogen and to solubilize the inorganic phosphate in the soil, which can positively influence the biomass of the gliricidia and mask the effects of the mycorrhizal inoculants tested.The endophytic bacteria P. illinoisensis produces chitinases, which can inhibit or degrade mycelium of phytopathogenic fungi such as Rhizoctonia solani, Fusarium solani, and Sclaretium rolfsi (SUBBANNA; KHAN; SHIVASHANKARA, 2016) thus ensuring the survival of the gliricidia in the field.
However, inoculation of the gliricidia with the native microbiota and UFLAs did not increase the height of plant, number of branches, or the shoot and root dry mass matter when compared to the control (Table 3).Similar findings were reported by Walter et al. (2016), with another fabaceae, namely the Holcus lanatus, which was inoculated with arbuscular mycorrhizal fungi.One potential explanation for these results could be the diversity in the microorganisms found in all the treatments, namely, mycorrhizal isolates, endophytic dark septate fungi, and nitrogen-fixing bacteria, that when interacting with one another, may be antagonistic or not (YAN et al., 2015).Graham et al. (1982) mentioned that the mycorrhizal colonization of a plant does not increase its biomass, but depends on the fungi-plant interaction.Among the parameters analyzed, despite the absence of any difference, the use of the UFLA401 treatment increased the number of branches by 37.6% compared to the control, thus contributing to vegetative propagation (Table 3).
Table 3. Height plant (H), number of branches (NB), shoot dry mass matter (SDMM), root dry mass matter (RDMM), root length (RL), root volume (RV) and leaf phosphorus (P leaf) of Gliricidia sepium inoculated with FMAs, after 95 days of inoculation.Analyzing the phosphorus content in the leaves, an inoculation with UFLA05, UFLA351, and UFLA372 resulted in an increase of 171.4%, 242.9%, and 333.3% respectively compared to controls.However, no difference in the leaf phosphorus content was noted the mycorrhizal treatment (Table 3).Similar finding was previously reported by Twum-Ampofo ( 2008) with the Glomus sp.This increase in the leaf phosphorus content may contribute to the systemic defense mechanism, as mentioned by Gerlach et al. (2015) with corn plants, which may be an important factor for survival in the field.
Treatment with the isolate from UFLA351 presented a lower root length in the gliricidia compared to treatment with UFLA372, but without a significant difference in the root length and volume relation to other treatments (Table 3, Figures 1b and  1e).This was probably due to the formation of fine secondary roots.The presence of fine secondary roots may contribute to a greater resistance to soil shear (MACHADO et al., 2015) and favor soil and water conservation.The root dry mass matter of the gliricidia treated with the native inoculant and UFLAs did not correlate with the mycorrhizal colonization, the number of nodules, and the presence of any endophytic dark septate fungi.In the control treatment, a mycorrhizal colonization of 3.8% and the presence of endophytic dark septate fungi in 15.5% of the root fragments, showed a negative correlation with the root dry mass matter, supporting an inhibition in the formation of the root biomass (Tables 1 and 4).
The correlation between an increase in the biomass and mycorrhizal colonization depends on the fungi-plant interaction (MOREIRA; SIQUEIRA, 2006), but it is important to note that the efficiency of the symbiosis is not always correlated to a high mycorrhizal colonization (GRAHAM et al., 1982), as observed in this work with the native inoculant and UFLAs.However, it should be considered that the gliricidia may have been colonized by endophytic bacteria, such as Pantoea stewartii and Paenibacillus illinoisensis, arbuscular mycorrhizal fungi, endophytic dark septate fungi, and nitrogen-fixing bacteria, and that the isolated evaluation of only one of the symbiotic microorganisms did not permit the evaluation of all the microbial interactions that contribute to the development of the dry matter mass of the root.In relation to the endophytic fungi, Santos and Varavallo (2011) proposed that these microorganisms are growth promoters and can be used for the biological control of pathogens, but Yan et al. (2015) suggested that the endophytic bacteria may be antagonistic to other species of microorganisms and therefore, negatively influence the interaction of the mycorrhizal fungi, and, consequently impact the vegetal development of gliricidia.
Literature strongly supports that the mycorrhizal dependency evaluates how much the plant responds to the inoculation but all the data is only in terms of the total dry mass matter.In this work, the dependency was also evaluated for the number of branches, shoot and root dry mass matter, root length and volume, which allows one to evaluate the influence of microorganisms on plant growth with greater precision.In this context, the gliricidia was responsive to the use of the native inoculant according Machineski, Balota and Souza (2011), because it presented a 39.4% increase in the shoot dry mass matter, 45.6% increase in the root dry mass matter, and 31.4% increase in the root volume.The use of the isolate UFLA372 favored a 39.7% increase in root dry mass matter, and gliricidia should be considered responsive only to this parameter.Treatment with UFLA401, increased the number of branches by 27.3%, the shoot dry mass matter by 27.0%, and the root volume by 25.8% and the gliricidia was responsible for the inoculation of this isolate.The gliricidia was not responsive to the inoculation of the isolates from UFLA05 and UFLA351, due to the mycorrhizal dependency being lower than 25% in the tested parameters namely, the number of branches, shoot and root dry mass matter, root length, and volume (Figure 2).This result may have been due to the presence of a diverse group of microorganisms in addition to the mycorrhizal inoculant, which may inhibit or stimulate mycorrhizal dependency of the fungi-plant interaction (YAN et al., 2015).The effect of microbial interaction on the development of gliricidia biomass may have been influenced by the time of cultivation as observed by Mello, Silva and Saggin-Júnior (2012), with the fabaceae tree, Mimosa artemesiana.Sugai, Collier and Saggin-Júnior (2011) observed a synergism between the arbuscular mycorrhizal fungi and the nitrogen-fixing bacteria, but this cooperation may be influenced by other microorganisms and soil type (natural or anthropic).Thus, studies on gliricidia and the association of mycorrhizal fungi, nitrogen fixing bacteria, and endophytic dark septate fungi should be explored, since they may contribute to the a better utilization of this fabaceae in the recovery of degraded areas, as well as an important source of nutrients for the animals under drought conditions, mainly in the Northeastern Brazil.