Abstract
Plant growth promoting rhizobacteria (PGPR) are bioresources with potential application in ecofriendly agricultural practices. The beneficial effects of PGPR have been attributed to their ability to produce phytohormone, organic acid, siderophore, and also due to nitrogen fixation among others. In the present study, previously isolated plant growth promoting rhizospheric Pseudomonas spp. were evaluated for growth enhancement effect in Vigna unguiculata seedlings. Elemental profiling of treated plant was further carried out by inductively coupled plasma-mass spectroscopy. Results of the study showed significant increase in growth parameters such as shoot length, root length and root numbers for treated plants when compared to control. Most of the macro and micro elements were also found to get modulated by interaction with applied Pseudomonas spp. However, a differential modulation was observed for plants when treated with each of the Pseudomonas spp., which could be due to their variable interaction with the selected plant. The results of the study indicate the role of each of the associated microbial partner to specifically influence the plant nutrient mobilization along the soil plant axis. The cumulative effect of the plant microbiome hence may decide the global nutritional status of plants as per the available environmental conditions.
Keywords: Rhizobacteria, ICP-MS, V. unguiculata, Plant growth promotion
Introduction
Plant–rhizobacterial interactions have been studied extensively for various agrological as well as environmental aspects (Chandra and Kumari 2017). Plant growth promoting rhizobacteria (PGPR) can be extracellular (Agrobacterium, Arthrobacter, Azotobacter, Azospirillum, Bacillus, Burkholderia, Caulobacter, Chromobacterium, Erwinia, Flavobacterium, Micrococcus, Pseudomonas and Serratia) or intracellular (Allorhizobium, Bradyrhizobium, Mesorhizobium and Rhizobium, endophytes and Frankia) (Gupta et al. 2015). The diverse mechanisms employed by these organisms include the production of phytohormones, ACC deaminase, siderophore, nitrogen fixation, enhanced mineral uptake and biocontrol against numerous phytopathogens (Vacheron et al. 2013). By IAA production, they have been demonstrated to modulate the cell elongation, division and differentiation in plants. Microbial population also secrete organic acids which convert the insoluble phosphates into soluble monobasic and dibasic ions and thereby making it available to plants. Siderophore producing bacteria restrict the growth of plant pathogens due to their strong affinity towards Fe(III). The enzyme 1-aminocyclopropane-1-carboxylate (ACC) deaminase of microbial origin facilitates plant growth and development by decreasing the ethylene level, inducing salt tolerance and reducing drought stress in plants (Zahir et al. 2008). These beneficial features of rhizobacteria have significant impact on growth and yield of plants. Among the various rhizobacteria, Pseudomonas spp. have ubiquitous distribution and have diverse plant growth promoting as well as biocontrol mechanisms. However, the global changes introduced in plants due to rhizobacterial interaction are not fully known. The wide range of antifungal compounds produced by plant growth promoting rhizobacteria includes amphisin, 2,4-diacetylphloroglucinol (DAPG), oomycin A, phenazine, pyoluteorin, pyrrolnitrin, tensin, tropolone, and cyclic lipopeptides (Loper et al. 2007). Among these, phenazine derivatives are one of the important antifungal products of Pseudomonas spp.
Due to the easiness with culture handling and large-scale production, many Pseudomonas spp. based formulations have already been introduced. Hence the Genus Pseudomonas forms an important candidate to study the global impact of plant beneficial mechanisms of rhizobacteria on plant system. Such studies are very important to explore the opportunities to design tailor made rhizobacterial formulations to specifically modulate the nutritional composition of plants. As they have been isolated from rhizosphere of numerous plants like cotton, rice, banana, rape, sugar cane, wheat and barley, they have immense promises to explore (Loaces et al. 2010; Ravindra Naik et al. 2008; Patten and Glick 2002; Rameshkumar 2012; Mavrodi et al. 2001; Parejko et al. 2012). So, in this study selected Pseudomonas spp. have been investigated in detail to identify their impact on elemental composition of the model plant Vigna unguiculata.
Materials and methods
For the study, previously isolated Pseudomonas spp. from Western Ghat rhizosphere were selected. These include P. putida (KY823010), P. monteilii (KY823008), P. rhodesiae (KY823009), P. fluorescens (KY823007) and P. taiwanensis (KY823006). For the plant growth promotion studies, seeds of V. unguiculata were collected and surface sterilized using sodium hypochlorite for 10 min (Jasim et al. 2013). The seeds were further washed several times with sterile distilled water and were allowed to germinate. The germinated seedlings were then treated with overnight grown cultures (107 CFU/mL) of P. putida, P. monteilii, P. rhodesiae, P. fluorescens and P. taiwanensis for 30 min. Treated seedlings along with control (distilled water and nutrient broth) were then observed for enhanced plant growth by planting it in double-sterilized soil. In each set of growth promotion study, ten seedlings were used per set in triplicate. Both control and treated seedlings were watered daily and observed periodically. The plants were harvested after 1 week and growth parameters such as root length, shoot length and root numbers were analysed (Jimtha John et al. 2017).
Pseudomonas spp. with enhanced plant growth enhancement effects were selected further to identify its potential to modulate the elemental composition of V. unguiculata. So, the plant samples treated with P.monteilii, P. rhodesiae and P.fluorescens were selected for ICP-MS analysis. These were oven dried for half an hour at 50 °C and powdered using mortar and pestle. From this, aliquotes of 0.1 g were digested at 85 °C with 8 mL HNO3 (Supra pure) in a microwave digestion system. The digested samples were further made up to 25 mL with ultrapure water and then stored in sterile vials. The samples for ICP-MS (THERMO FISCHER iCAP, Q) analysis were diluted with 10% acid and from that 1 mL was again diluted to 25 mL. After ICP-MS analysis, the elemental concentration in ppb was converted to µg/mg using the formula (ICP-MS result × 25 × 0.025) ÷ 0.1. Triplicates were maintained for each plant samples. The results were analysed using statistical programme Origin Pro 7. One-way analysis of variance was used for comparison among the groups. Post hoc multiple comparison tests were used to determine the significant difference among groups, P < 0.05 was considered as significant.
Results and discussion
Among the selected Pseudomonas spp., three of them enhanced the growth of V. unguiculata when compared to control. P. monteilii treatment showed the highest enhancement of mean shoot length, root length and root numbers when compared to control. The shoot length of P. monteilii-treated seedlings was 20.73 ± 0.69 cm and was high when compared to that of the distilled water and nutrient broth control (DW-14.48 ± 0.79 cm, NB-13.11 ± 0.27 cm). The root length of the same (5.49 ± 0.27 cm) was also found to get enhanced when compared to the control. The root numbers were more in the case of P. fluorescens (9.85 ± 0.99) treatment and the same for control were 6.38 ± 0.55 and 6.38 ± 0.75 for DW and NB, respectively. The shoot length (18.73 ± 0.28 cm), root length (3.92 ± 0.22 cm) and root numbers (9 ± 0.50) were also higher in P. rhodesiae-treated seedlings than that of DW and NB control. P. putida treatment showed a shoot length of 16.25 ± 0.42 cm, root length of 3.74 ± 0.06 cm and root numbers of 9.33 ± 0.60; whereas P. taiwanensis mediated shoot length to 16.14 ± 0.23 cm, root length to 2.9 ± 0.12 cm and root numbers to 9.19 ± 0.37 (Fig. 1). The bacterial isolates used in the study have been demonstrated to have efficient growth enhancement effect in various plant systems (Jimtha John et al. 2017). Hence, the result can be due to the colonization of selected bacteria on V. unguiculata. Seed bacterization with Pseudomonas spp. has previously been described to result in increased growth parameters such as root length, shoot length and dry mass of sorghum seedlings (Praveen Kumar 2012). The inoculation of Pseudomonas sp. on peanut and maize has also reported to result in increased seed germination, growth and phosphorous content (Anzuay et al. 2017).
Fig. 1.
Growth promotion analysis of Pseudomonas spp. on Vigna unguiculata seedlings by pot experiment along with untreated control. a Shoot length and root length. b Root number. DW distilled water and NB nutrient broth
By ICP-MS analysis, P. fluorescens treated plants were found to have enhancement of phosphorous and magnesium while there was decrease of potassium and calcium contents when compared to control. Micronutrients like aluminium, iron, zinc and sodium of same plants were lower than control. However, nickel, manganese, caesium, strontium, cerium, neodymium, ytterbium, europium, bismuth, beryllium and lanthanum concentrations in P. fluorescens treated plants were observed to be higher than in controls. Chromium, cobalt, praseodymium, scandium, lutetium, rhenium, thallium, indium, rubidium, arsenic, holmium, erbium, thulium, thorium, gadolinium, dysprosium, lithium, barium, lead, boron, vanadium, gallium, selenium and cadmium concentrations were lower in P. fluorescens treated plants than in control (Fig. 2).
Fig. 2.
Elemental composition variation (macronutrients) in Pseudomonas spp. (P. monteilii, P. fluorescens and P. rhodesiae treated seedlings of Vigna unguiculata when compared to control obtained from ICP-MS data. DW distilled water, NB nutrient broth control
In P. rhodesiae treated plants macro elements like phosphorous and magnesium were high, but potassium and calcium contents were lower. Aluminium, manganese, iron, chromium, gallium, vanadium, neodymium, rubidium, strontium, barium, lanthanum, cerium, lead, lithium, boron, arsenic, cadmium, praseodymium, gadolinium, samarium, beryllium, indium, caesium, europium, scandium, terbium, bismuth, thorium, uranium, holmium, erbium, thulium, ytterbium, lutetium, thallium and dysprosium concentrations in plants treated with P. rhodesiae were higher than control. However, zinc, sodium, cobalt, copper, nickel, yttrium, selenium and rhenium of P. rhodesiae treated plants showed decreased concentration than control (Fig. 2).
The macro elements like phosphorous, potassium, calcium and magnesium contents in P. monteilii treated plants were lower than controls. Manganese, sodium, nickel, copper neodymium, lanthanum, barium and thorium of treated plants were higher than control. Aluminium, iron, chromium, gallium, vanadium, neodymium, rubidium, strontium, barium, cerium, lead, lithium, arsenic, cadmium, zinc, praseodymium, gadolinium, samarium, beryllium, indium, caesium, europium, scandium, terbium, bismuth, uranium, holmium, erbium, thulium, ytterbium, lutetium, thallium and dysprosium concentrations in P. monteilii treated plants were lower than control (Fig. 2) (Table 1).
Table 1.
Elemental composition variation in Pseudomonas spp. (P. monteilii, P. fluorescens, P. rhodesiae) treated seedlings of V. unguiculata when compared to control (DW distilled water, NB nutrient broth) obtained from ICP-MS data
| Concentration of elements in µg/mg (DW) | Concentration of elements in µg/mg (NB) | Concentration of elements in µg/mg (P. fluorescens) | Concentration of elements in µg/mg (P. monteilii) | Concentration of elements in µg/mg (P. rhodesiae) | |
|---|---|---|---|---|---|
| Al | 2773.419 ± 0.579785 | 2362.462 ± 0.300888 | 2644.735 ± 0.519615 | 2279.399 ± 0.057735 | 4322.849 ± 0.57735 |
| Fe | 1548.341 ± 0.57735 | 1529.137 ± 0.015275 | 1437.867 ± 0.608276 | 1141.111 ± 0.057735 | 2362.847 ± 0.57735 |
| Zn | 1018.497 ± 0.574485 | 1093.336 ± 0.060828 | 692.4619 ± 0.635085 | 395.8311 ± 0.057735 | 556.2129 ± 0.057735 |
| Na | 798.2303 ± 0.635085 | 731.2288 ± 0.028868 | 648.3131 ± 0.057735 | 607.5434 ± 0.057735 | 539.4947 ± 0.11547 |
| Mn | 315.6843 ± 0.611991 | 569.3644 ± 0.011547 | 658.2657 ± 0.608276 | 604.6754 ± 0.057735 | 618.3861 ± 0.23094 |
| Cu | 287.652 ± 0.57735 | 371.3465 ± 0.110151 | 137.1203 ± 0.550757 | 70.57084 ± 0.288675 | 398.2044 ± 0.635085 |
| Ni | 95.74449 ± 0.57735 | 231.4784 ± 0.110151 | 274.1513 ± 0.608276 | 126.2504 ± 0.11547 | 51.16571 ± 0.608276 |
| Rb | 73.07984 ± 0.57735 | 65.63367 ± 0.060828 | 64.49175 ± 0.057735 | 65.13879 ± 0.057735 | 76.60876 ± 0.173205 |
| Ba | 48.95014 ± 0.57735 | 50.54808 ± 0.090185 | 40.48197 ± 0.57735 | 38.16625 ± 0.057735 | 55.73448 ± 0.057735 |
| Pb | 39.20162 ± 0.264575 | 40.24077 ± 0.058026 | 28.5152 ± 0.11547 | 11.7652 ± 0.11547 | 41.74654 ± 0.057735 |
| Ce | 17.31047 ± 0.763763 | 46.77984 ± 0.191594 | 47.63744 ± 0.11547 | 24.23715 ± 0.057735 | 72.37724 ± 0.057735 |
| Sr | 34.12062 ± 0.8544 | 34.06756 ± 0.066583 | 36.20203 ± 0.11547 | 25.50155 ± 0.11547 | 38.36365 ± 0.057735 |
| La | 9.635971 ± 0.52915 | 22.24709 ± 0.063509 | 25.37034 ± 0.23094 | 33.07198 ± 0.011547 | 36.2054 ± 0.057735 |
| Nd | 7.148222 ± 0.519615 | 20.55475 ± 0.005774 | 25.33701 ± 0.173205 | 21.82394 ± 0.57735 | 31.43724 ± 0.173205 |
| Cr | 12.1051 ± 0.46188 | 16.44843 ± 0.055076 | 11.19034 ± 0.173205 | 10.33974 ± 0.057735 | 23.71692 ± 0.057735 |
| B | 9.644166 ± 0.80829 | 8.268384 ± 0.057166 | 6.790562 ± 0.057735 | 12.50646 ± 0.57735 | 10.5506 ± 0.057735 |
| Co | 12.6119 ± 0.51316 | 13.24436 ± 0.057449 | 11.22673 ± 0.057735 | 11.04435 ± 0.005774 | 12.04435 ± 0.005774 |
| V | 7.825573 ± 0.503322 | 7.136994 ± 0.057166 | 5.167253 ± 0.57735 | 6.115242 ± 0.57735 | 15.33155 ± 0.057735 |
| Y | 14.56597 ± 0.503322 | 11.21149 ± 0.060828 | 10.89192 ± 0.057735 | 6.321809 ± 0.57735 | 16.93436 ± 0.011547 |
| Ga | 4.764481 ± 0.623538 | 9.072364 ± 0.011547 | 3.195728 ± 0.680686 | 5.055294 ± 1.154701 | 14.80622 ± 0.005774 |
| Pr | 6.855615 ± 0.011547 | 5.335955 ± 0.05 | 5.051339 ± 0.028868 | 3.046101 ± 0.034641 | 8.327819 ± 0.057735 |
| Se | 4.424484 ± 0.057735 | 4.375814 ± 0.05837 | 3.63396 ± 0.34641 | 2.525315 ± 0.017321 | 3.321944 ± 0.057735 |
| Gd | 5.304772 ± 0.190539 | 4.122109 ± 0.057735 | 3.855442 ± 0.57735 | 2.249681 ± 0.005774 | 6.251332 ± 0.057735 |
| Sm | 4.240168 ± 0.042564 | 3.91512 ± 0.057822 | 3.410008 ± 0.173205 | 2.031552 ± 0.005774 | 5.6794 ± 0.173205 |
| Li | 2.208819 ± 0.000902 | 2.493184 ± 0.046159 | 2.011212 ± 0.014565 | 1.668211 ± 0.57735 | 3.313335 ± 0.057735 |
| As | 4.642374 ± 0.041886 | 3.339049 ± 0.046194 | 2.744356 ± 0.34641 | 1.673618 ± 0.57735 | 4.752068 ± 0.057735 |
| Dy | 1.679462 ± 0.005774 | 1.92816 ± 0.054271 | 1.01443 ± 0.005774 | 1.032609 ± 0.017321 | 2.933963 ± 0.057735 |
| Sc | 0.847444 ± 0.005774 | 0.809872 ± 0.058014 | 0.473593 ± 0.1 | 0.656396 ± 0.057735 | 1.230956 ± 0.023094 |
| Cd | 1.58425 ± 0.112694 | 0.924124 ± 0.11576 | 0.405736 ± 0.208167 | 0.37792 ± 0.23094 | 1.663265 ± 0.04772 |
| Th | 0.432498 ± 0.017559 | 0.865954 ± 0.003464 | 0.181 ± 0.057735 | 0.933131 ± 0.011547 | 1.452252 ± 0.011547 |
| Er | 0.978176 ± 0.026458 | 0.81665 ± 0.005508 | 0.633949 ± 0.11547 | 0.424043 ± 0.011547 | 1.26346 ± 0.011547 |
| Cs | 0.455627 ± 0.028918 | 0.438053 ± 0.01 | 0.310439 ± 0.057735 | 0.408961 ± 0.005774 | 0.654966 ± 0.005774 |
| Yb | 0.171043 ± 0.017321 | 0.452301 ± 0.034641 | 0.607498 ± 0.057735 | 0.120148 ± 0.005774 | 0.767828 ± 0.005774 |
| Eu | 0.174358 ± 0.025981 | 0.455287 ± 0.021362 | 0.497044 ± 0.057735 | 0.023871 ± 0.005774 | 0.752082 ± 0.028868 |
| Tb | 0.436285 ± 0.002887 | 0.459525 ± 0.058924 | 0.328601 ± 0.057735 | 0.235315 ± 0.005774 | 0.643939 ± 0.002887 |
| Ho | 0.426438 ± 0.017321 | 0.367546 ± 0.058832 | 0.256826 ± 0.057735 | 0.235315 ± 0.028868 | 0.511165 ± 0.009033 |
| U | 0.089015 ± 0.01 | 0.288567 ± 0.055664 | 0.02649 ± 0.005774 | 0.035929 ± 0.005774 | 0.73126 ± 0.005774 |
| Tl | 0.096498 ± 0.001 | 0.119401 ± 0.027555 | 0.014297 ± 0.005774 | 0.076135 ± 0.028868 | 0.120861 ± 0.005774 |
| Tm | 0.0399 ± 0.010536 | 0.096134 ± 0.002517 | 0.035139 ± 0.005774 | 0.027294 ± 0.017321 | 0.157744 ± 0.023094 |
| Be | 0.050758 ± 0.002887 | 0.049947 ± 0.004071 | 0.051831 ± 0.000577 | 0.027745 ± 0.005774 | 0.087557 ± 0.001732 |
| In | 0.05772 ± 0.006429 | 0.076439 ± 0.005292 | 0.040781 ± 0.005774 | 0.040492 ± 0.005774 | 0.116225 ± 0.005774 |
| Lu | 0.090961 ± 0.006083 | 0.080174 ± 0.015319 | 0.062445 ± 0.005774 | 0.029883 ± 0.011547 | 0.111271 ± 0.005774 |
| Re | 0.0043 ± 0.005196 | 0.00513 ± 0.005947 | 0.002436 ± 0.00052 | 0.001627 ± 0.000173 | 0.000466 ± 0.000561 |
| Bi | 0.052993 ± 0.000643 | 0.057524 ± 0.001 | 0.074106 ± 0.005774 | 0.045035 ± 0.003464 | 0.078048 ± 0.001155 |
Data represented as mean ± standard deviation
While comparing the macronutrient enhancement by Pseudomonas spp., both P. fluorescens and P. rhodesiae treated plants showed an elevated level of phosphorous and magnesium with a decrease in potassium and calcium concentrations than P. monteilii treated plants. In the case of micronutrients, most of the elements (aluminium, manganese, iron, vanadium, boron) in P. rhodesiae treated plants were elevated than in P. fluorescens and P. monteilii treated plants. Other elements like neodymium, rubidium, strontium, barium, lanthanum, cerium, lead, lithium, arsenic, cadmium, praseodymium, gadolinium, samarium, beryllium, indium, caesium, europium, scandium, terbium, bismuth, chromium, gallium, thorium, uranium, holmium, erbium, thulium, ytterbium, lutetium, thallium and dysprosium were lower in P. monteilii treated plants than that of P. fluorescens treated plants except nickel, caesium, strontium, cerium, neodymium, ytterbium, europium, bismuth, beryllium and lanthanum. In case of P. rhodesiae treated plants, other elements except zinc, sodium, cobalt, copper, nickel, yttrium, selenium and rhenium were elevated than in P. fluorescens and P. monteilii. Even though similar studies have not been conducted previously in detail, current results confirm the role of rhizobacterial interaction in determining the elemental composition of plants. In a previous study, Pseudomonas sp. A3R3 have been reported to be effective in promoting the phytoremediation potential of both host (Alyssum serpyllifolium) and nonhost (Brassica juncea) plants by improving either the Ni accumulation or biomass production (Ma et al. 2011). At the same time, inoculation of plants with phosphate solubilizing organism has also reported to result in increased P contents and associated 10–15% increase in crop yields (Gyaneshwar et al. 2002). Another study has also suggested bacterial role in protecting plants from the inhibitory effects of nickel, lead, and zinc by providing the plants with sufficient iron (Burd et al. 2000). Inoculation of P. fluorescens at a concentration of 109 cfu/mL was also observed to cause significant increase in availability of Fe by 34.75% in plants (Pratiwi et al. 2016). Macro and micronutrient modulation and associated increase of growth have also been reported in Sorghum due to seed bacterization with Pseudomonas spp. (Kumar et al. 2012). In another study, nutrient content (P, Fe, Zn, K and Mg) and plant growth of strawberry have been suggested to be modulated by Bacillus and Pseudomonas sp. (Esitken et al. 2010). These indicate the remarkable modulatory effect of plant elemental composition by associated microorganisms.
Plant growth promoting rhizobacteria are potential tools for the sustainable agricultural trend for the future. In the study, previously isolated Pseudomonas species were found to enhance the growth of V. unguiculata seedlings when compared to that of control. From the ICP-MS analysis result, differential modulatory effect of Pseudomonas species on the elemental composition of plants could be confirmed. Hence, a detailed insight into the plant growth promoting and element modulatory functions Pseudomonas can pave the way to make use of rhizobacteria to engineer plants with desired nutritional composition.
Acknowledgements
The authors gratefully acknowledge Dr. Mahesh Mohan, School of Environmental Sciences, Mahatma Gandhi University, Kottayam for the help and support provided for ICP-MS analysis and also KSCSTE-SRS for the funded project.
Compliance with ethical standards
Conflict of interest
The authors declare that they have no conflict of interest.
References
- Anzuay MS, Ciancio MGR, Luduena LM, Angelini JG, Barros G, Pastor N, Taurian T. Growth promotion of peanut (Arachis hypogaea L.) and maize (Zea mays L.) plants by single and mixed cultures of efficient phosphate solubilizing bacteria that are tolerant to abiotic stress and pesticides. Microbiol Res. 2017;199:98–109. doi: 10.1016/j.micres.2017.03.006. [DOI] [PubMed] [Google Scholar]
- Burd GI, Dixon DG, Glick BR. Plant growth-promoting bacteria that decrease heavy metal toxicity in plants. Can J Microbiol. 2000;46:237–245. doi: 10.1139/cjm-46-3-237. [DOI] [PubMed] [Google Scholar]
- Chandra S, Kumari P. Isolation, characterization, screening, formulation and evaluation of plant growth promoting rhizobacteria. Can J Biotechol. 2017;1(Special Issue):141–141. doi: 10.24870/cjb.2017-a127. [DOI] [Google Scholar]
- Esitken A, Yildiz HE, Ercisli S, Figen Donmez M, Turan M, Gunes A. Effects of plant growth promoting bacteria (PGPB) on yield, growth and nutrient contents of organically grown strawberry. Sci Hortic. 2010;124(1):62–66. doi: 10.1016/j.scienta.2009.12.012. [DOI] [Google Scholar]
- Gupta G, Parihar SS, Ahirwar NK, Snehi SK, Singh V. Plant growth promoting rhizobacteria (PGPR): current and future prospects for development of sustainable agriculture. J Microb Biochem Technol. 2015;7:096–102. doi: 10.4172/1948-5948.1000188. [DOI] [Google Scholar]
- Gyaneshwar P, Kumar GN, Parekh LJ, Poole PS. Role of soil microorganisms in improving P nutrition of plants. Plant Soil. 2002;245:83–93. doi: 10.1023/A:1020663916259. [DOI] [Google Scholar]
- Jasim B, Jimtha J, Jyothis CM, Radhakrishnan EK. Plant growth promoting potential of endophytic bacteria isolated from Piper nigrum. Plant Growth Regul. 2013;71:1–11. doi: 10.1007/s10725-013-9802-y. [DOI] [Google Scholar]
- Jimtha John C, Jishma P, Karthika NR, Nidheesh KS, Ray JG, Mathew J, Radhakrishnan EK. Pseudomonas fluorescens R68 assisted enhancement in growth and fertilizer utilization of Amaranthus tricolor (L.) 3 Biotech. 2017;7:256. doi: 10.1007/s13205-017-0887-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Kumar GP, Kishore N, Amalraj ELD, Ahmed SMH, Rasul A, Desai S. Evaluation of fluorescent Pseudomonas spp. with single and multiple PGPR traits for plant growth promotion of sorghum in combination with AM fungi. Plant Growth Regul. 2012;67:133–140. doi: 10.1007/s10725-012-9670-x. [DOI] [Google Scholar]
- Loaces I, Ferrando L, Fernández Scavino A. Dynamics, diversity and function of endophytic siderophore-producing bacteria in rice. Microb Ecol. 2010;61(3):606–618. doi: 10.1007/s00248-010-9780-9. [DOI] [PubMed] [Google Scholar]
- Loper JE, Kobayashi DY, Paulsen IT. The Genomic Sequence of Pseudomonas fluorescens Pf-5: insights into biological control. Phytopathology. 2007;97:233–238. doi: 10.1094/phyto-97-2-0233. [DOI] [PubMed] [Google Scholar]
- Ma Y, Rajkumar M, Luo Y, Freitas H. Inoculation of endophytic bacteria on host and non-host plants—effects on plant growth and Ni uptake. J Hazard Mater. 2011;195:230–237. doi: 10.1016/j.jhazmat.2011.08.034. [DOI] [PubMed] [Google Scholar]
- Mavrodi DV, Bonsall RF, Delaney SM, Soule MJ, Phillips G, Thomashow LS. Functional analysis of genes for biosynthesis of pyocyanin and phenazine-1-carboxamide from Pseudomonas aeruginosa PAO1. Bacteriol J. 2001;183(21):6454–6465. doi: 10.1128/jb.183.21.6454-6465.2001. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Parejko JA, Mavrodi DV, Mavrodi OV, Weller DM, Thomashow LS. Population structure and diversity of phenazine-1-carboxylic acid producing fluorescent Pseudomonas spp. from Dryland Cereal Fields of Central Washington State (USA) Microb Ecol. 2012;64(1):226–241. doi: 10.1007/s00248-012-0015-0. [DOI] [PubMed] [Google Scholar]
- Patten CL, Glick BR. Role of Pseudomonas putida indoleacetic acid in development of the host plant root system. Appl Environ Microbiol. 2002;68(8):3795–3801. doi: 10.1128/aem.68.8.3795-3801.2002. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Pratiwi H, Aini N, Soelistyono R. Effects of Pseudomonas fluorescens and sulfur on nutrients uptake, growth and yield of ground nut in an alkaline soil. J Degrad Min Lands Manag. 2016;3:507–516. [Google Scholar]
- Praveen Kumar G, Desai S, Leo Daniel Amalraj E, Mir Hassan Ahmed SK, Reddy G. Plant growth promoting Pseudomonas spp. from diverse agro-ecosystems of India for Sorghum bicolor L. J Biofert Biopest. 2012;S7:001. doi: 10.4172/2155-6202.s7-001. [DOI] [Google Scholar]
- Rameshkumar N. Genotypic and phenotypic diversity of PGPR fluorescent pseudomonads isolated from the rhizosphere of sugarcane (Saccharum officinarum L.) J Microbiol Biotechnol. 2012;22(1):13–24. doi: 10.4014/jmb.1107.07025. [DOI] [PubMed] [Google Scholar]
- Ravindra Naik P, Raman G, Badri Narayanan K, Sakthivel N. Assessment of genetic and functional diversity of phosphate solubilizing fluorescent pseudomonads isolated from rhizospheric soil. BMC Microbiol. 2008;8(1):230. doi: 10.1186/1471-2180-8-230. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Vacheron J, Desbrosses G, Bouffaud M-L, Touraine B, Moënne-Loccoz Y, Muller D, Legendre L, Wisniewski-Dyé F, Prigent-Combaret C. Plant growth-promoting rhizobacteria and root system functioning. Front Plant Sci. 2013;4:356. doi: 10.3389/fpls.2013.00356. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Zahir ZA, Munir A, Asghar HN, Arshad M, Shaharoona B. Effectiveness of rhizobacteria containing ACC-deaminase for growth promotion of peas (Pisum sativum) under drought conditions. J Microbiol Biotechnol. 2008;18:958–963. [PubMed] [Google Scholar]


