Journal of Agricultural Science and Food Research

Journal of Agricultural Science and Food Research
Open Access

ISSN: 2593-9173

+44 1223 790975

Special Issue Article - (2012) Volume 3, Issue 3

Plant Growth Promoting Pseudomonas spp. from Diverse Agro-Ecosystems of India for Sorghum bicolor L.

Praveen Kumar G1*, Suseelendra Desai1, Leo Daniel Amalraj E1, Mir Hassan Ahmed SK1 and Gopal Reddy2
1Central Research Institute for Dry land Agriculture (ICAR), Santoshnagar, Hyderabad-500 059, India
2Department of Microbiology, Osmania University, Hyderabad- 500 007, India
*Corresponding Author: Praveen Kumar G, Central Research Institute for Dry land Agriculture (ICAR), Santoshnagar, Hyderabad-500 059, India, Tel: +91-9849598248 Email:

Abstract

 Fluorescent Pseudomonas spp. comprise an important group of rhizosphere bacterial community affecting plant growth. Sorghum is an important fifth largest cereal crop in world. 75 fluorescent Pseudomonas spp. were isolated from diverse agro-ecosystems of India and evaluated for their plant growth promoting ability initially by paper cup method. Fourteen selected isolates were further evaluated under glass house conditions. Plants inoculated with bacteria showed higher growth and nutrient uptake than controls. Seedlings treated with selected isolate P17 showed highest root volume (0.3 cm3 ), shoot length (36.2 cm), dry mass (152 mg), leaf area (31 cm2 ), chlorophyll (23 spad units), carbohydrates (30%), phosphorus (1.3%), nitrogen (2.2%) and other nutrients. Among the evaluated isolates Pseudomonas sp. P17 strain was identified as a potential PGPR for nutrient uptake and plant growth in sorghum. This finding has potential for integrated plant nutrient management in rainfed agroecosystems where farmers tend to rely on cost effective technologies for enhanced profitability

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Keywords: Pseudomonas spp; Plant growth; Rhizobacteria; Soil nutrition; Agro-ecosystems; Sorghum

Introduction

Sorghum (Sorghum bicolor L.), is an important rainfed crop grown world over on 42 million ha in 98 countries and Nigeria, India, USA, Mexico, Sudan, China and Argentina are the major producers [1]. In India, sorghum was planted in 7.7 million ha with production of 7.24 million tonnes and productivity of 940 kg. ha-1 [2].

Soil microorganisms play important role in determining plant productivity. For successful functioning of introduced microbial bioinoculants, exhaustive efforts have been made to explore soil microbial diversity of indigenous community, their distribution and behaviour in soil habitats [3]. Soil microorganisms are directly responsible for recycling of nutrients [4].

Considering the ill-effects of inorganic fertilizers on soil health, adoption of integrated nutrient management (INM) has been advocated for sustainable agriculture. Efforts to supplement nutrients through biofertilizers as part of INM helped the rainfed farmers significantly [5]. Microorganisms that facilitate nutrients availability and use could form sustainable solutions for present and future agricultural practices [6]. Microbes that indirectly or directly promote plant growth are referred to as plant growth promoting rhizobacteria (PGPR) [7]. Species of Pseudomonas comprise a large portion of the total culturable bacterial population in the rhizosphere. Due to the ubiquity and versatility of pseudomonads, there is a considerable interest in exploiting these bacteria for diverse agricultural applications such as plant growth promotion and pest management etc., [8].

Information on fluorescent Pseudomonas spp. from diverse agroecosystems and their plant growth promoting potential particularly in sorghum is scanty. In this paper, we report isolation and variations among 75 isolates of Pseudomonas spp. from 23 different agroecological regions of India with respect to their ability to promote nutrient uptake and growth in sorghum.

Materials and Methods

Bacterial cultures and seed bacterization

Seventy-five soil samples of different crops representing 31 locations from 13 states of India were used for isolation of fluorescent Pseudomonas spp. [9]. Sorghum seeds of cv. CSV-15 procured from Directorate of Sorghum Research, Hyderabad, India were bacterized with Pseudomonas isolates as described by Dileep Kumar and Dube [10].

Physico-chemical characterization of soil samples

Physical characters like pH, electrical conductivity (EC), particle size and chemical characters like macronutrients (N, P, K) and organic carbon content were characterized for all the collected soil samples and similar characterization was also done for the soil used for plant experiments (Table 3) [11].

Screening for plant growth promoting Pseudomonas isolates

Preliminary screening of Pseudomonas spp. isolates for their plant growth promotion (PGP) by seed bacterization was done as explained by Ali et al. [12]. Three bacterized seeds were sown in each paper cup containing sterile soil and six replicates were maintained with untreated control. 15 days after sowing (DAS) root length, shoot length and dry mass of seedlings (by drying to constant weight at 65oC) were recorded and relative increase was calculated as against un-inoculated control

Pot experiments and nutrient analysis

Fourteen Pseudomonas spp. isolates viz, P1, P2, P4, P5, P13, P14, P17, P20, P21, P22, P23, P28, P29 and P35 shortlisted from previous experiment with >50% enhancement in dry mass of seedlings (Table 1) were selected for pot culture experiments. Pot experiments with bacterized seeds were conducted as described by Sindhu et al. [13]. After 30 DAS root volume, shoot length, leaf area (measured by LI 3100 Lincoln Nebraska USA leaf area meter), total chlorophyll (measured by Minolta Spad chlorophyll meter-502) and dry mass of root and shoot were recorded.

Analysis of the macro- (NPK) secondary- (Na, Ca) and micro- (Fe, Cu, Mn, Zn) nutrients in the experimental plants was carried out following the protocols of Tandon [11]. Total carbohydrate content was estimated by anthrone method [14].

Statistical Analysis

Data obtained from all experiments were subjected to analysis of variance (ANOVA). Mean values between treatments were compared using Fisher’s least significant difference (L.S.D) test (P<0.05). All plant growth parameters were given equal importance to follow Z-score ranking and to identify the promising Pseudomonas isolate showing best plant growth promotion.

Results

Isolation of fluorescent Pseudomonas spp.

Pseudomonas spp. isolated from different soil samples showing fluorescein production on King’s B medium were selected and purified. 75 fluorescent Pseudomonas spp. were isolated from soil samples obtained from 31 different locations representing 13 states of India (Figure 1). Isolates were designated as P1 to P75 and added to the culture collection of Central Research Institute for Dryland Agriculture, Hyderabad. All the isolates were stored as 30% glycerol stocks at -20°C and revived periodically for further studies.

biofertilizers-biopesticides-agro-ecosystems

Figure 1: India map showing soils samples from different agro-ecosystems. Figures in parentheses in legends represent number of samples collected.

Characterization of soil samples

Of the 31 soil samples characterized, five were from western plains, one from western Himalayas, six from northern plains, two from central highlands, 11 from Deccan plateau, four from eastern ghats, and one each from eastern plateau and Chattisgarh-Mahanadi basin agro-ecological regions of India. The annual mean rainfall of these regions ranged from 150-1450 mm (lowest in western plains and highest in Chattisgarh-Mahanadi basin). The annual mean maximum soil temperatures ranged between 28-47°C with lowest being in western Himalayas and highest in western plains (Table 1).

Location State Agro-ecological Sub Region Climate Soil Type Mean Annual Rainfall (mm) Max. Soil Temperature (°C)
Bari Brahmana Jammu & Kashmir Western Himalayas Subhumid Alluvial deep Inceptisols 1180 28
Jodhpur Rajasthan Western Plain Arid Black-medium Inceptisols/ Vertisols 150 47
Arjia Rajasthan Northern Plain Semiarid      Black-medium vertic inceptisols/
vertisols
656 44
Junagadh Gujarat Western Plain Semiarid Medium-deep Vertisols 650 42
Sardar Krishinagar Gujarat Western Plain Arid Desert-very deep Aridisols 550 41
Rewa Madhya Pradesh Central Highlands Subhumid Black-mediumdeep Vertisols 1087 39
Rajkot Gujarat Western Plain Arid Black-medium deep-deep Vertisols 615 42
Akola Maharashtra Deccan Plateau Semi arid Black-medium deep-deep vertic inceptisols/ Vertisols 825 41
Gunegal Andhra Pradesh Deccan Plateau Semi arid Deep Alfisols 850 35
Kadiri Andhra Pradesh Deccan Plateau Arid Black-medium deep Vertisols 450 42
Bijapur Karnataka Deccan Plateau Semi arid Black-medium deep-deep Vertisols 680 42
Ongole Andhra Pradesh Eastern Ghats Semi arid Medium-deep Vertisols/ Alfisols 900 43
Guntakal Andhra Pradesh Eastern Ghats Semi arid Medium-deep Vertisols/ Alfisols 900 42
Maruteru Andhra Pradesh Eastern Ghats Semi arid Deep Vertisols 800 43
Warangal Andhra Pradesh Deccan Plateau Semi arid Medium-deep Vertisols 850 38
Hayathnagar Andhra Pradesh Deccan Plateau Semi arid Deep Alfisols 850 36
Karimnagar Andhra Pradesh Deccan Plateau Semi arid Medium-deep Vertisols 850 44
Solapur Maharashtra Deccan Plateau, Eastern Ghats Semi arid Black-medium deep-deep Vertic/ Vertisols 723 43
Phulbani Orissa Eastern Plateau (Chhotanagpur) and Eastern Ghats Subhumid Red/yellow deep Alfisols 1299 43
Parbhani Maharashtra Deccan Plateau Semi arid Deep Vertisols 850 40
Bhopal Madhya Pradesh Central (Malwa & Bundelkhand) Highlands Semi arid Deep Vertisols 800 42
Jagdalpur Chattisgarh Chattisgarh/Mahanadi Basin Subhumid Red/yellow deep Alfisols 1450 43
Faizabad Uttar Pradesh Northern Plain Subhumid Alluvial deep Inceptisols 1057 40
Udaipur Rajasthan Northern Plain Semi arid Black-medium deep-deep vertic inceptisols/ Vertisols 656 44
Jhansi Uttar Pradesh Northern Plain Semi arid Inceptisols 550 42
Hisar Haryana Western Plain Arid Alluvial-very deep Aridisols 412 41
Varanasi Uttar Pradesh Northern Plain Subhumid Alluvial deep Inceptisols 850 39
Ballowal Saunkhri Punjab Northern Plain Subhumid Red loamy soils 750 40
Kovilpatti Tamilnadu Eastern Ghats Semi arid Black deep Vertisols 743 40
Rajendranagar Andhra Pradesh Deccan Plateau Semi arid Deep Alfisols 850 39
Suryapet Andhra Pradesh Deccan Plateau Semi arid Deep Alfisols 850 44

Table 1: Agro-ecological regions, climatic conditions and their soil types of India used for isolation of fluorescent Pseudomonas spp.

Eight samples showed acidic pH from 6.0-6.9 with Phulbani sample recording lowest pH. Four soil samples were neutral with pH 7.0-7.2 and 19 were alkaline (pH 7.3-8.6) with Bijapur sample showing highest pH 8.6. Electrical conductivity (EC) of the samples ranged between 0.02 (Phulbani, Orissa) and 1.79 dS.m-1 (Hisar, Haryana). Organic carbon (OC) content ranged between 0.12 (Phulbani) and 0.5% (Rajendranagar, Andhra Pradesh). Total available nitrogen content ranged from 62 (Hayatnagar, Andhra Pradesh) to 183 kg.ha-1 (Arjia, Rajasthan). Similarly phosphorus (Pi) content ranged from 6.3 (Akola, Maharashtra) to 20.1 kg.ha-1 (Parbhani, Maharashtra). Potassium content varied widely across samples with the highest being in 500.4 kg.ha-1 Solapur (Maharashtra) and lowest of 55.6 kg.ha-1 in Baribrahmana (Table 2).

S. No. Location pH EC (dS.m-1) OC (%) Particle Size (%) Macronutrients (kg/ha)
Sand Silt Clay N P K
01 Bari Brahmana 7.2 0.04 0.38 79.5 7.14 13.36 114.9 12.4 55.6
02 Jodhpur 8.1 0.12 0.41 26.2 12.6 61.2 92.90 7.90 190.1
03 Arjia 8.3 0.14 0.24 63.7 13.1 23.2 182.6 8.50 109.4
04 Junagadh 6.9 0.10 0.16 60.7 9.20 30.1 102.9 19.9 129.5
05 Sardar Krishinagar 8.0 0.04 0.43 84.1 4.10 11.8 98.40 11.6 85.10
06 Rewa 7.4 0.10 0.17 28.0 23.3 48.7 113.9 9.00 407.5
07 Rajkot 8.1 0.10 0.38 26.6 12.1 61.3 93.50 8.00 188.8
08 Akola 8.3 0.13 0.18 18.8 19.1 62.1 116.2 6.30 76.70
09 Gunegal 6.5 0.49 0.37 74.3 7.70 18.0 63.30 9.10 71.00
10 Kadiri 6.8 0.09 0.17 60.5 9.20 30.3 103.6 19.6 129.2
11 Bijapur 8.6 1.40 0.27 20.4 17.7 61.9 58.20 9.40 378.2
12 Ongole 7.6 0.05 0.44 83.2 4.20 12.6 97.20 12.1 86.30
13 Guntakal 7.3 0.12 0.26 84.2 4.80 11.0 98.10 2.50 61.00
14 Maruteru 7.0 0.11 0.17 60.4 9.80 29.8 101.4 19.7 124.2
15 Warangal 7.8 0.27 0.41 82.3 4.80 12.9 99.70 16.0 118.0
16 Hayatnagar 6.3 0.48 0.34 73.0 7.00 20.0 62.00 8.90 70.00
17 Karimnagar 7.4 0.13 0.27 83.9 4.60 11.5 99.20 2.70 61.70
18 Solapur 8.1 0.12 0.30 11.4 13.8 74.8 73.70 8.00 500.4
19 Phulbani 6.0 0.02 0.12 55.4 11.1 33.5 104.8 14.5 195.1
20 Parbhani 7.1 0.13 0.18 61.4 9.80 28.8 99.80 20.1 122.1
21 Bhopal 7.1 0.12 0.16 63.1 9.90 27.0 101.2 19.6 119.5
22 Jagdalpur 6.1 0.04 0.13 56.2 12.1 31.7 102.2 16.4 188.4
23 Faizabad 8.1 0.29 0.18 28.5 32.2 39.3 125.7 8.40 160.3
24 Udaipur 8.4 0.14 0.19 19.1 20.4 60.5 112.4 7.40 78.30
25 Jhansi 8.1 0.12 0.42 27.5 13.2 59.3 93.10 8.10 191.2
26 Hisar 7.4 1.79 0.15 55.9 17.5 26.6 150.3 10.9 163.1
27 Varanasi 8.2 0.31 0.19 29.5 31.5 39.0 119.4 8.90 159.3
28 Ballowal Saunkhri 8.1 0.32 0.21 29.9 32.2 37.9 115.1 9.10 149.6
29 Kovilpatti 8.0 0.80 0.36 29.8 5.85 64.35 86.30 6.70 272.3
30 Rajendranagar 6.7 0.12 0.50 69.4 7.80 22.8 65.00 9.20 69.50
31 Suryapet 6.9 0.15 0.46 71.4 8.20 20.4 68.20 9.40 89.00

EC=Electrical conductivity and OC= Organic carbon; N= Nitrogen, P=Phosphorus and K=Potash

Table 2: Physico-chemical properties and macronutrient status of soil types used for the isolation of Pseudomonas spp.

Physical characters  
pH 7.4
EC 0.075 dS.m-1
Chemical characters  
Total ‘N’ 201.9 kg. ha-1
Total ‘P’ 21.0 kg. ha-1
Total ‘K’ 197.84 kg. ha-1
Organic carbon 0.32%

Table 3: Physico-chemical characters of soil used for plant growth studies

Screening for plant growth promotion

Most of the Pseudomonas spp. isolates promoted growth of sorghum seedlings. While 69 isolates showed increase in root length, 70 isolates showed increase in shoot length and dry mass as compared to un-inoculated control (Table 4). All the isolates were grouped into three categories based on increase in dry mass viz, <25%, 25-50% and >50%. Of the 75 isolates, 45% of them showed <25% enhancement of dry mass, whereas 29% of them enhanced dry mass in the range of 25- 50% and 17% of them showed >50% increment in dry mass (Figure 2). Remaining 7% isolates showed dry mass of less than control and were considered as deleterious rhizobacteria (Figure 2). 14 isolates viz, P1, P2, P4, P5, P13, P14, P17, P20, P21, P22, P23, P28, P29 and P35 that showed more than 50% enhancement in dry mass of seedlings were considered as potential strains for further pot-culture studies.

 Isolate Increase in root length Increase in shoot length Increase in dry mass  Isolate Increase in root length Increase in shoot length Increase in dry mass
*P1 44 100 134 P39 38 29 29
*P2 39 86 127 P40 30 29 25
P3 26 10 50 P41 -13 -01 -05
*P4 24 76 62 P42 26 22 02
*P5 82 31 100 P43 13 25 34
P6 06 10 14 P44 31 32 17
P7 07 29 45 P45 35 45 19
P8 77 13 35 P46 45 18 05
P9 46 39 50 P47 37 32 18
P10 -25 -01 -04 P48 13 27 12
P11 -28 -02 -14 P49 14 37 07
P12 05 24 10 P50 32 37 16
*P13 27 76 65 P51 23 47 24
*P14 30 78 69 P52 36 63 17
P15 12 34 34 P53 52 57 06
P16 07 38 21 P54 32 57 22
*P17 44 53 96 P55 29 56 12
P18 05 11 03 P56 -12 -03 -01
P19 12 39 34 P57 29 46 14
*P20 77 28 95 P58 40 50 47
*P21 72 25 75 P59 23 35 14
*P22 70 23 70 P60 19 32 20
*P23 98 37 105 P61 10 13 10
P24 14 38 48 P62 17 36 06
P25 15 39 45 P63 33 46 21
P26 11 51 27 P64 21 41 27
P27 10 43 31 P65 16 34 17
*P28 22 68 59 P66 28 41 20
*P29 32 78 76 P67 16 47 08
P30 12 43 41 P68 32 39 28
P31 28 35 14 P69 40 38 07
P32 15 32 17 P70 21 28 28
P33 21 35 28 P71 17 36 14
P34 -04 19 39 P72 40 28 13
*P35 43 24 63 P73 40 25 14
P36 24 36 16 P74 31 32 14
P37 -16 -04 -03 P75 17 16 01
P38 20 29 07        

*isolates that were further selected for evaluation by pot culture studies

Table 4: Control P17 Figure 3: Plant growth promotion of sorghum by Pseudomonas sp. P17 in pots (30 days after sowing). Relative percentage increase in root, shoot length and dry mass of sorghum seedlings on seed bacterization with Pseudomonas spp. (15 DAS).

biofertilizers-biopesticides-fluorescent-Pseudo-monas

Figure 2: Grouping pattern of plant growth promoting fluorescent Pseudo monas spp. on sorghum.

Pot experiments and nutrient analysis

Seed bacterization of sorghum with fluorescent Pseudomonas spp. enhanced sorghum plant growth significantly (Figure 3, Table 5). Root volume in control was 0.17 cm3 whereas, in treatments it ranged between 0.18 and 0.30 cm3. Inoculation of sorghum with P1 and P17 showed maximum root volume of 0.30 cm3 compared to other treatments. Significant increase in shoot length was observed with P17 (36.2 cm) inoculation followed by P1 (33.5 cm) and P22 (32.2 cm). Highest root dry mass was recorded in P2 (78.4 mg) followed by P17 (69.1 mg) and P35 (66.9 mg). Maximum shoot dry mass was recorded in plants treated with P17 (83.1 mg) followed by P1 (69 mg) and P22 (68 mg). Inoculated plants also showed higher leaf area compared to control. Leaf area of plants inoculated with P17 was 31.6 cm2 followed by P22 (27 cm2) and P20 (22 cm2) than un-inoculated control plants (9.8 cm2). Similar results were also recorded in case of chlorophyll content. P17 treated plants recorded highest chlorophyll content of 23 spad units followed by P22 and P23 treatments which were 22 and 21 spad units respectively compared to control (8 spad units). Overall increase in plant dry mass was highest in P17 treated plants (152 mg) followed by P22 (132 mg) and P23 (128 mg) (Table 5).

Treatment RV (cc) SL (cm) RDW (mg) SDW (mg) TDM (mg) LA (cm2) Total chlorophyll (Spad reading)
P1 0.30a (±0.014) 33.5a (±1.54) 46.4d (±2.14) 69a (±3.16) 115 17.5 (±0.81) 20a (±0.92)
P2 0.25 (±0.012) 26.0b-e (±1.19) 78.4 (±3.61) 45b (±2.06) 123 14.8 (±0.68) 19b (±0.88)
P4 0.28 (±0.013) 23.7e (±1.09) 58c (±2.66) 44b (±2.03) 102 10.0ef (±0.46) 13 (±0.6)
P5 0.20d (±0.009) 23.7e (±1.09) 57c (±2.62) 37cd (±1.71) 94 11.3b-f (±0.52) 1d (±0.78)
P13 0.22c (±0.010) 24.2de (±1.11) 43e (±1.98) 39c (±1.81) 82 10.8c-f (±0.5) 15 (±0.69)
P14 0.20d (±0.009) 25.1c-e (±1.15) 44de(±2.03) 38cd (±1.73) 82 10.4d-f (±0.48) 14 (±0.65)
P17 0.30a (±0.014) 36.2 (±1.66) 69.1a (±3.18) 83.1 (±3.83) 152 31.6 (±1.46) 23 (±1.06)
P20 0.20d (±0.009) 31.1a (±1.43) 44de (±2.04) 62.1 (±2.86) 106 22 (±1.01) 20a (±0.92)
P21 0.20d (±0.009) 25.3c-e (±1.16) 56c (±2.58) 45b (±2.07) 101 12.4ab (±0.57) 17d (±0.78)
P22 0.23b (±0.011) 32.2a (±1.48) 63.6b (±2.93) 68a (±3.15) 132 27 (±1.24) 22 (±1.01)
P23 0.23b (±0.011) 28.2b (±1.3) 61b (±2.81) 67a (±3.08) 128 24 (±1.11) 21 (±0.97)
P28 0.18 (±0.008) 24.5c-e (±1.29) 61b (±2.81) 38cd (±1.76) 99 12.8a (±0.59) 19b (±0.88)
P29 0.22c (±0.010) 25.2c-e (±1.16) 56c (±2.58) 35d (±1.63) 91 12.2a-c (±0.56) 18c (±0.83)
P35 0.20d (±0.009) 26.8bc (±1.23) 66.9a (±3.08) 44b (±2.04) 111 12.4ab (±0.57) 18c (±0.83)
Control 0.17 (±0.008) 20.2 (±0.93) 30 (±1.38) 31.1 (±1.43) 61 9.8f(±0.45) 8 (±0.37)
LSD 0.08 2.4 2.6 3.3   1.4 0.82
CV% 19.10 17.7 23 32   43.3 22.2

values superscribed by same letter are not significantly different according to fisher’s lsd test (P<0.05). values in the parentheses are standard errors of means.
RV=Root volume; RL=Root length; SL=Shoot length; RDW/ SDW= Root, shoot dry weight TDM=Total Dry Mass; R-S ratio=Root-shoot ratio; LA= Leaf area *means of two independent experiments with six replicates each time. values in the parentheses are standard errors of means.

Table 5: Plant growth of sorghum as influenced by seed bacterization with fluorescent Pseudomonas spp. (30 days after sowing).

biofertilizers-biopesticides-promotion-sorghum

Figure 3: Plant growth promotion of sorghum by Pseudomonas sp. P17 in pots (30 days after sowing).

Inoculation of sorghum with Pseudomonas spp. not only enhanced plant growth but also increased nutrient uptake significantly (Table 6,7). Total carbohydrates content of treated plants was in the range of 17.3 to 30.6% with highest by P17 where as untreated plants had 15.4%. Phosphorus uptake was also significantly higher in treated plants with Pseudomonas isolates in general and P1 and P17 (1.35%) in particular compared to control (0.38%). Nitrogen uptake was also significantly higher in P17 treatment (2.254%) followed by P22 and P23 (2.24% in both). Similarly, sodium uptake in plants increased on treatment with P22 (0.54%) followed by P17 (0.52%) and P23 (0.51%). However, potassium uptake was more in P17 treated plants (2.9%) followed by P22 (2.85%) and P1 (2.54%). P5, P13 and P35 treated plants showed significantly higher Ca uptake of 0.88%, 1.02% and 1.15% respectively (Table 6).

  Macronutrients (mg) / 100 mg of dry plant material
Treatment  Total ‘CH’ Total ‘P’ Total ‘N’ Na K Ca
P1 25.0* (±1.15) 1.35 (±0.062) 2.212 (±0.102) 0.45 (±0.021) 2.54 (±0.117) 0.63 (±0.029)
P2 21.0 (±0.97) 0.77 (±0.035) 1.652 (±0.076) 0.48 (±0.022) 1.27 (±0.059) 0.48 (±0.022)
P4 19.5 (±0.90) 0.57 (±0.026) 1.512 (±0.070) 0.49 (±0.023) 1.71 (±0.079) 0.46 (±0.021)
P5 19.4 (±0.89) 0.80 (±0.037) 1.736 (±0.080) 0.51 (±0.024) 1.84 (±0.085) 0.88 (±0.041)
P13 18.6 (±0.86) 0.71 (±0.033) 1.876 (±0.086) 0.43 (±0.020) 1.80 (±0.083) 1.02 (±0.047)
P14 17.3 (±0.80) 0.62 (±0.029) 1.708 (±0.079) 0.48 (±0.022) 1.99 (±0.092) 0.44 (±0.020)
P17 30.6 (±1.41) 1.35 (±0.062) 2.254 (±0.104) 0.52 (±0.024) 2.90 (±0.134) 0.84 (±0.039)
P20 24.4 (±1.12) 0.85 (±0.039) 1.722 (±0.079) 0.47 (±0.022) 2.38 (±0.110) 0.49 (±0.023)
P21 23.5 (±1.08) 0.95 (±0.044) 1.806 (±0.083) 0.50 (±0.023) 2.14 (±0.099) 0.69 (±0.032)
P22 29.5 (±1.36) 1.18 (±0.054) 2.240 (±0.103) 0.54 (±0.025) 2.85 (±0.131) 0.42 (±0.019)
P23 29.2 (±1.35) 1.31 (±0.060) 2.240 (±0.103) 0.51 (±0.024) 2.44 (±0.112) 0.45 (±0.021)
P28 20.9 (±0.96) 0.91 (±0.042) 2.114 (±0.097) 0.50 (±0.023) 1.85 (±0.085) 0.52 (±0.024)
P29 23.0 (±1.06) 0.82 (±0.038) 1.946 (±0.090) 0.41 (±0.019) 2.03 (±0.094) 0.85 (±0.039)
P35 23.5 (±1.08) 0.84 (±0.039) 2.184 (±0.101) 0.49 (±0.023) 1.87 (±0.086) 1.15 (±0.053)
Control 15.4 (±0.71) 0.38 (±0.018) 1.148 (±0.053) 0.40 (±0.018) 2.10 (±0.097) 0.38 (±0.018)
CV% 21.1 33.1 18.7 11.4 22 38

*means of two independent experiments with six replicates each time.

Table 6: Macro-nutrient uptake in sorghum as influenced by seed coating with fluorescent Pseudomonas spp. (30 days after sowing).

Seed bacterization of sorghum with Pseudomonas isolates significantly increased the uptake of micronutrients (Table 7). Inoculation with P17 and P35 enhanced the Cu content (14 ppm) followed by P1 and P5 (12 ppm) compared to control (7 ppm). Higher quantity of Fe was accumulated in plants inoculated with P17 (3500 ppm) followed by P35 (2901 ppm) and P22 treatments (2527 ppm). Mn uptake was maximum in P17 treatment (237 ppm) followed by P28 (227 ppm) P4 (183 ppm) compared to control (74 ppm). Zn uptake was more on inoculation with P22 (936 ppm) followed by P17 (433 ppm) and P13 (429 ppm) than control (159 ppm) (Table 7). Overall impact of P17 treatment on nutrient uptake and plant growth was 70-220% and 30-290% respectively (Figure 4,5).

  Micronutrients (ppm) / 100 mg of  dry plant material
Treatment Cu Fe Mn Zn
P1 12b (±0.55) 2125b (±98) 179ab (±8.2) 411a (±18.9)
P2 10d (±0.46) 1229cd (±57) 110f (±5.1) 312cd (±14.4)
P4  11c (±0.5) 1293a (±60) 183a (±8.4) 341bc (±15.7)
P5 12b (±0.55) 1075d (±50) 141d (±6.5) 252e (±11.6)
P13 11c (±0.5) 1980b (±91) 175a-c (±8.1) 429a (±19.8)
P14 10d (±0.46) 1538 (±71) 135d (±6.2) 201 (±9.3)
P17 14a (±0.64) 3500 (±161) 237 (±10.9) 433a (±20)
P20 10d (±0.46) 2001b (±92) 173bc (±8) 285de (±13.1)
P21 11c (±0.5) 1764 (±81) 179ab (±8.2) 420a (±19.4)
P22 10d (±0.46) 2527a (±116) 123e (±5.7) 936 (±43.1)
P23 11c (±0.5) 2470a (±114) 169c (±7.8) 248e (±11.4)
P28 10d (±0.46) 1135cd (±52) 227 (±10.5) 243e (±11.2)
P29 9 (±0.41) 2373a (±109) 118ef (±5.4) 266e (±12.3)
P35 14a (±0.64) 2901 (±134) 125e (±5.8) 357b (±16.5)
Control  7 (±0.32) 881 (±41) 74 (±3.4) 159 (±7.3)
LSD 0.37 160.7 9.4 39.2
CV% 18.1 39.1 28.8 51.5

values superscribed by same letter are not significantly different according to Fisher’s LSD test (P<0.05) and values in the parentheses are standard errors of means.

Table 7: Micro-nutrient uptake in sorghum as influenced by seed bacterization with fluorescent Pseudomonas spp. (30 days after sowing).

Discussion

The microbial biodiversity of a region is mainly determined by agro-ecological systems and constituents of plant root exudates that decide the type and density of microbial population in a given crop production system [15]. Efficient colonization and/or physiological adaptation to adverse soil conditions are the options for soil bacteria to survive [16]. In the present study, with an aim of obtaining isolates of Pseudomonas spp., different crop production systems of diverse agro-ecological regions were surveyed (Figure 1) and 75 isolates were obtained. Fourteen isolates were found to enhance >50% dry mass of sorghum seedlings (Table 4). Of these, 9 isolates were from semi-arid deep alfisols belonging to agro-ecological region, 1 isolate each from semi-arid medium deep inceptisols/vertisols (deccan plateau), semiarid medium deep vertisol (deccan plateau), semi-arid black medium deep vertic inceptisol (northern plain), sub-humid alluvial deep inceptisol (western himalayas) and semi-arid medium deep vertisol (western plain) (Table 1). This indicates the congenial conditions of the soil perhaps facilitated the plant growth promotion (PGP) activity of these isolates as soil nutritional conditions are reported to be influencing the performance of PGPRs [17].

Present experiments on sorghum clearly indicated that Pseudomonas spp. can be used to enhance the plant growth as reported earlier [18,19]. Bacterial inoculated seedlings of different crops showed enhanced plant growth as reported by Kloepper et al. [20], Glick [21] and Dey et al. [22]. In the present study, a significant increase (P<0.05) in root and shoot length and dry mass of sorghum seedlings was observed due to seed bacterization (Table 5). The plant growth promotion could be attributed to the exertion of direct and/or indirect action of PGP traits [23].

Seed bacterization of sorghum with Pseudomonas spp. also enhanced the uptake of essential macro and micro-nutrients resulting in overall increase of plant growth (Table 6,7). It is in concurrence with the observations of Paul, et al. [24] and Kourosh et al. [25] who reported enhanced uptake of nutrients in black pepper and sweet basil due to seed bacterization with Pseudomonas spp. Increased nutrient uptake by plants inoculated with plant growth promoting bacteria has been attributed to the production of plant growth regulators at the root interface, which stimulate root development and better absorption of water and nutrients from soil [26,27]. In the present study, we observed significant impact (P<0.05) of Pseudomonas spp. on plant growth promotion in various parameters like root volume, shoot length, dry mass, chlorophyll content, leaf area etc. and enhanced macro and micro-nutrients uptake. Besides plant growth, inoculated plants clearly showed increased accumulation of nitrogen which is in agreement with observations of Puente et al. [28]. Esitken et al. [29] demonstrated that root inoculation of Bacillus and Pseudomonas sp. increased nutrient content (P, Fe, Zn, K and Mg) and plant growth of strawberry. Rhizobacteria efficacy on sorghum growth promotion in green house conditions was shown by Idris et al. [30]. Present findings are co-inciding with earlier studies. The importance and role of PGPR traits of Pseudomonas spp. in growth promotion of sorghum was shown by Praveen Kumar, et al. [31].

Defreitas and Germide [32] demonstrated that seed treatment with Pseudomonas spp. significantly enhanced early growth of winter wheat in low fertility asquith soil. Observations in the present study with Pseudomonas sp. P17 strain showed good plant growth enhancement (Figure 3,4) and higher nutrient uptake (Figure 5). Z-score ranking also revealed that P17 ranked as the best isolate among the other Pseudomonas isolates studied.

biofertilizers-biopesticides-growth-parameters

Figure 4: Influence of seed bacterization with Pseudomonas sp. P17 on plant growth parameters of sorghum.

biofertilizers-biopesticides-macro-micro-nutrients

Figure 5: Uptake of macro- and micro-nutrients as influenced by inoculation with Pseudomonas sp. P17 in sorghum.

Conclusion

Present studies were carried out with the objective of assessing the plant growth promoting potential of Pseudomonas spp. towards S. bicolor from diverse rainfed agro-ecosystems. Sorghum is generally cultivated under rainfed conditions and after sowing, generally the crop suffers due to a dry spell. During this period, if the plant is protected with a better vigour, it can tide over the dry spell and grow normally with the resuming of monsoon. A low cost technology like seed bacterization has been found to promote plant growth during early phenophase of the crop that is most vulnerable to dryspells. Isolates obtained from semi-arid deep alfisols are efficient PGPRs than the other isolates which depicts that the origin of the PGPR also plays an important role in determining the behaviour and efficacy of PGPRs in increasing the plant growth. In conclusion, improvement in nutrient uptake and growth of sorghum plants were observed on inoculation with fluorescent Pseudomonas sp. P17. Further investigations on this PGPR for its efficiency under field conditions are in progress to promote it as ‘low cost’ input for improved productivity of rainfed agro-production systems.

Acknowledgements

Authors thank Indian Council of Agricultural Research (ICAR), Ministry of Agriculture, Government of India, New Delhi for financial support under the network project “Application of Microorganisms in Agriculture and Allied Sectors (AMAAS)- Nutrient Management & PGPR”.

References

  1. Winch T (2006) Growing Food-A guide to food production. Springer Publications, Netherlands, pp. 135-140.
  2. Hill GT, Mitkowski NA, Aldrich-Wolfe L, Emele LR, Jurkonie DD, et al. (2000) Methods for assessing the composition and diversity of soil microbial communities. App Soil Ecol 15: 25-36.
  3. Wardle DA, Giller KE (1996) The quest for a contemporary ecological dimension to soil biology. Soil Biol Biochem 28: 1549-1554.
  4. Venkateswarlu B, Wani SP, (1999) Biofertlizers: An important component of Integrated Plant Nutrient Supply (IPNS) in drylands. Fifty years of Dryland Agricultural Research in India, CRIDA, Hyderabad, pp 379-394.
  5. Kloepper JW, Lifshitz R, Zablotowicz RM (1989) Free-living bacterial inocula for enhancing crop productivity. Trend Biotech 7: 39-43.
  6. Walsh UF, Morrissey JP, O'Gara F (2001) Pseudomonas for biocontrol of phytopathogens: from functional genomics to commercial exploitation. Curr Opin Biotech 12: 289-295.
  7. Nandakumar R, Babu1 S, Raguchander T, Samiyappan R (2007) Chitinolytic activity of native Pseudomonas fluorescens strains. J Agric Sci Tech 9: 61-68.
  8. Dileep Kumar BS, Dube HC (1992) Seed bacterization with a fluorescent Pseudomonas for enhanced plant growth, yield and disease control. Soil Biol Biochem 24:539-542.
  9. Tandon HLS (2001) Methods of analysis of soils, plants, water and fertilisers. Fertiliser Develoment and Consultation Organisation, New Delhi, India, pp. 144.
  10. Ali SkZ, SandhyaV, Grover M, Kishore N, Rao LV, et al. (2009) Pseudomonas sp. strain AKM-P6 enhances tolerance of sorghum seedlings to elevated temperatures. Biol Fert Soils 46: 45-55.
  11. Sindhu SS, Sunita S, Goel AK, Parmar N, Dadarwal KR (2002) Plant growth promoting effects of Pseudomonas sp. on co-inoculation with Mesorhizobium sp. cicer strain under sterile and ‘wilt sick’ soil conditions. App Soil Ecol 19: 57-64.
  12. Hedge JE, Hofreiter BT (1962) Whistler RL, Be Miller JN (eds) Carbohydrate Chemistry. Academic Press, New York
  13. Van Overbeek LS, Van Veen JA, Van Elsas JD (1997) Induced reporter gene activity, enhanced stress resistance, and competitive ability of a genetically modified Pseudomonas fluorescens strain released into a field plot planted with wheat. App Environ Microbiol 63: 1965–1973.
  14. Egamberdiyeva D (2007) The effect of plant growth promoting bacteria on growth and nutrient uptake of maize in two different soils. App Soil Ecol 36: 184-189.
  15. Luigi C, Annamaria B, Silvia T, Claudia D (1998) Inoculation of Burkholderia cepacia, Pseudomonas fluorescens and Enterobacter sp. on Sorghum bicolor: Root colonization and plant growth promotion of dual strain inocula. Soil Biol Biochem 30: 81-87.
  16. Hameeda B, Srijana M, Rupela OP, Reddy G (2007) Effect of bacteria isolated from composts and macroflora on sorghum growth and mycorrhizal colonization. W J Microbiol Biotech 23: 883-887.
  17. Kloepper JW, Hume DJ, Scher FM, Singleton C, Tipping B, et al. (1988) Plant growth promoting bacteria on canola (rape seed). Plant Dis 72: 42-46.
  18. Glick BR (1995) The enhancement of plant growth promotion by free living bacteria. Can J Microbiol 41: 109-117.
  19. Dey R, Pal KK, Bhatt DM, Chauhan SM (2004) Growth promotion and yield enhancement of peanut (Arachis hypogea L.) by application of plant growth promoting rhizobacteria. Microbiol Res 159: 371-394.
  20. Brown GD, Rovira AD (1999) The rhizosphere and its management to improve plant growth. Adv Agron 66: 1-102.
  21. Paul D, Sarma YR, Srinivasan V, Anandaraj M (2005) Pseudomonas fluorescens mediated vigour in black pepper (Piper nigrum L.) under green house cultivation. Ann Microbiol 55: 171-174.
  22. Kourosh O, Shahram S, Mahdi Z (2011) Influence of PGPR on growth, essential oil and nutrients uptake of sweet basil. Adv Environ Biol 5: 672-677.
  23. Kloepper JW, Zablokovicz RM, Tipping EM, Lifshitz R (1991) Plant growth promotion mediated by bacterial rhizosphere colonizers. The rhizosphere and plant growth. Kluwer Academic Publishers, Netherlands 315-326.
  24. Zimmer W, Kloos K, Hundeshagen B, Neideran E, Bothe H (1995) Auxin biosynthesis and denitrification in plant growth promoting bacteria. In: Fendrik J, De Gallo Vandeleyden J, De Zamoroczy D (eds) Azospirillum VI and related microorganisms. Series G: Ecological. 37:120-141.
  25. Puente ME, Li CY, Bashan Y (2004) Microbial populations and activities in the rhizoplane of rock-weathering desert plants. II Growth promotion of cactus seedlings. Plant Biol 6: 643-650.
  26. Esitken A, Hilal E, Yildiz, Sezai Ercisli M, Figen Donmez, et al. (2010) Effects of plant growth promoting bacteria (PGPB) on yield, growth and nutrient contents of organically grown strawberry. Scientia Horti 124: 62-66.
  27. Idris A, Labuschagne N, Korsten L (2009) Efficacy of rhizobacteria for growth promotion in Sorghum under greenhouse conditions and selected modes of action studies. J Agric Sci 147: 17-30.
  28. Praveen Kumar G, Kishore N, Leo Daniel Amalraj E, Mir Hassan Ahmed SK, Abdul Rasul, et al. (2012) Evaluation of fluorescent Pseudomonas spp. with single and multiple PGPR traits for plant growth promotion of sorghum in combination with AM fungi. Plant Grow Regul
  29. DeFreitas JR, Germide JJ (1992) Growth promotion of winter wheat by fluorescent Pseudomonas under growth chamber conditions. Soil Biol Biochem 24:1137-1146.
Citation: Praveen Kumar G, Desai S, Leo Daniel Amalraj E, Mir Hassan Ahmed SK, Reddy G (2012) Plant Growth Promoting Pseudomonas spp. from Diverse Agro-Ecosystems of India for Sorghum bicolor L. J Biofert Biopest S7:001.

Copyright: © 2012 Praveen Kumar G. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
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