10.1007@s00344-016-9663-5
10.1007@s00344-016-9663-5
10.1007@s00344-016-9663-5
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J Plant Growth Regul<br />
DOI 10.1007/s00344-<strong>016</strong>-<strong>9663</strong>-5<br />
Co-inoculation with Enterobacter and Rhizobacteria on Yield<br />
and Nutrient Uptake by Wheat (Triticum aestivum L.)<br />
in the Alluvial Soil Under Indo-Gangetic Plain of India<br />
Ashok Kumar 1,2 · B. R. Maurya 1 · R. Raghuwanshi 2 · Vijay Singh Meena 1,3 ·<br />
M. Tofazzal Islam 4<br />
Received: 2 August 2<strong>016</strong> / Accepted: 9 November 2<strong>016</strong><br />
© Springer Science+Business Media New York 2017<br />
Abstract The aim of this work was to evaluate the effects<br />
of co-inoculation with phosphate-solubilizing and nitrogenfixing<br />
rhizobacteria on growth promotion, yield, and nutrient<br />
uptake by wheat. Out of twenty-five bacteria isolated<br />
from the rhizosphere soils of cereal, vegetable, and agroforestry<br />
plants in eastern Uttar Pradesh, three superior most<br />
plant growth-promoting (PGP) isolates were characterized<br />
as Serratia marcescens, Microbacterium arborescens, and<br />
Enterobacter sp. based on their biochemical and 16S rDNA<br />
gene sequencing data and selected them for evaluating their<br />
PGP effects on growth and yield of wheat. Among them,<br />
Enterobacter sp. and M. arborescens fixed significantly<br />
higher amounts (9.32 ± 0.57 and 8.89 ± 0.58 mg Ng −1 carbon<br />
oxidized, respectively) of atmospheric nitrogen and<br />
produced higher amounts (27.06 ± 1.70 and 26.82 ± 1.63<br />
TP 100 µg mL −1 , respectively) of IAA in vitro compared<br />
to S. marcescens (8.32 ± 0.39 mg Ng −1 carbon oxidized and<br />
21.29 ± 0.99 TP 100 µg mL −1 ). Although both M. arborescens<br />
and S. marcescens solubilized remarkable amounts<br />
of phosphate from tricalcium phosphate likely through<br />
* Ashok Kumar<br />
ashokbhu2010@gmail.com; ashokabt@gmail.com<br />
* Vijay Singh Meena<br />
vijay.meena@icar.gov.in; vijayssac.bhu@gmail.com<br />
1<br />
2<br />
3<br />
4<br />
Department of Soil Science and Agricultural Chemistry,<br />
Institute of Agricultural Sciences, Banaras Hindu University,<br />
Varanasi, Uttar Pradesh 221005, India<br />
Department of Botany, MMV, Banaras Hindu University,<br />
Varanasi, Uttar Pradesh 221005, India<br />
ICAR-Vivekananda Parvatiya Krishi Anusandhan Sansthan,<br />
Almora, Uttarakhand 263601, India<br />
Department of Biotechnology, Bangabandhu Sheikh Mujibur<br />
Rahman Agricultural University, Gazipur 1706, Bangladesh<br />
production of organic acids, however, Enterobacter sp. was<br />
inactive. The effects of these three rhizobacteria were evaluated<br />
on wheat in alluvial soils of the Indo-Gangetic Plain<br />
by inoculation of plants with bacterial isolates either alone<br />
or in combinations in both pot and field conditions for two<br />
successive years. Rhizobacterial inoculation either alone<br />
or in consortium of varying combinations significantly<br />
(P ≤ 0.05) increased growth and yield of wheat compared<br />
to mock inoculated controls. A consortium of two or three<br />
rhizobacterial isolates also significantly increased plant<br />
height, straw yield, grain yield, and test weight of wheat in<br />
both pot and field trials compared to single application of<br />
any of these isolates. Among the rhizobacterial treatment,<br />
co-inoculation of three rhizobacteria (Enterobacter, M.<br />
arborescens and S. marcescens) performed best in promotion<br />
of growth, yield, and nutrient (N, P, Cu, Zn, Mn, and<br />
Fe) uptake by wheat. Taken together, our results suggest<br />
that co-inoculation of Enterobacter with S. marcescens and<br />
M. arborescens could be used for preparation of an effective<br />
formulation of PGP consortium for eco-friendly and<br />
sustainable production of wheat.<br />
Keywords Plant health · PGPR · P-solubilization · PGP<br />
activities · Crop productivity<br />
Introduction<br />
During the green revolution, high-yielding varieties with<br />
application of synthetic fertilizers and pesticides were<br />
introduced for increasing yields of crops. Indiscriminate<br />
use of hazardous synthetic fertilizers and pesticides<br />
caused environmental pollution and deteriorated soil health<br />
(Elkoca and others 2010). Moreover, production of crops<br />
largely depending on synthetic chemicals also decreased<br />
Vol.:(0123456789) 1 3
J Plant Growth Regul<br />
the nutritional quality of the produce that ultimately affects<br />
human health. Therefore, it is a great challenge to search<br />
for an alternative to hazardous synthetic chemicals for ecofriendly<br />
and sustainable crop production with improvement<br />
of soil health for ensuring food and nutritional security<br />
of the growing population of the world. Application of<br />
organic fertilizers and pesticides such as composts, green<br />
manures, biofertilizers, and biopesticides has been suggested<br />
for ensuring sustainable crop production in agriculture<br />
(Ahmad and others 2<strong>016</strong>; Bahadur and others 2<strong>016</strong>;<br />
Verma and others 2015b; Yadav and Sidhu 2<strong>016</strong>; Yasin<br />
and others 2<strong>016</strong>; Zahedi 2<strong>016</strong>). The plant rhizosphere is<br />
considered as a hot spot as well as a battle field of diverse<br />
microorganisms, and most of them play a crucial role in<br />
plant nutrition through fixation of nitrogen and/or solubilization<br />
of soil minerals and production of plant growth-promoting<br />
substances. Discovery of the elite strains of plant<br />
growth-promoting bacteria from the plant rhizosphere and<br />
applying them as biofertilizers is a new trend of research<br />
in eco-friendly and sustainable crop production systems<br />
worldwide (Hayat and others 2010; Kaymak 2011). The<br />
plant growth-promoting rhizobacteria (PGPR) exert a<br />
positive effect on plant growth either by direct mechanisms<br />
such as solubilization of soil nutrients, fixation of<br />
nitrogen, and production of growth regulators (Kumar and<br />
others 2014) and/or indirect mechanisms such as stimulation<br />
of mycorrhizal development, competitive exclusion<br />
of pathogens, induction of systemic resistance in plants,<br />
or remediation of phytotoxic substances (Bashan and de-<br />
Bashan 2010). Biofertilizer refers to the product, carrierbased<br />
solid or liquid containing agriculturally useful living<br />
microorganisms when applied in soil or seeds to increase<br />
the fertility of the soil and consequently improve crop productivity.<br />
The PGPR genera such as Arthrobacter, Azotobacter,<br />
Azospirillum, Bacillus, Enterobacter, Caulobacter,<br />
Erwinia, Chromobacterium, Flavobacterium, Microbacterium,<br />
Pseudomonas, and Serratia have been used for<br />
formulation of biofertilizers to enhance plant growth and<br />
yield (Bahadur and others 2014; Das and Pradhan 2<strong>016</strong>;<br />
Dominguez-Nunez and others 2<strong>016</strong>; Dotaniya and others<br />
2<strong>016</strong>; Velazquez and others 2<strong>016</strong>; Verma and others<br />
2015a). Serratia marcescens is one of the PGPR which<br />
promotes plant growth by enhanced P-solubilization in the<br />
rhizosphere and production of phytohormones (Tripura<br />
and others 2007). Nitrogen (N) is one of the major essential<br />
plant nutrients involved in improving plant growth and<br />
yield (Jaiswal and others 2<strong>016</strong>; Kumar and others 2015,<br />
2<strong>016</strong>a; Sindhu and others 2<strong>016</strong>; Teotia and others 2<strong>016</strong>).<br />
The rhizobacteria that can fix atmospheric nitrogen are<br />
also known as diazotrophic bacteria. They are capable of<br />
transforming atmospheric nitrogen into fixed nitrogen, that<br />
is, inorganic compounds usable by plants. Many efficient<br />
strains of diazotrophic bacteria have been formulated as<br />
biofertilizers. The effective biofertilizers developed from<br />
elite strains of diazotrophic bacteria play crucial roles in<br />
reducing dependency of synthetic fertilizers in eco-friendly<br />
sustainable agriculture (Ashrafuzzaman and others 2009;<br />
Meena and others 2<strong>016</strong>c). A large body of literature is<br />
available on plant growth promotion by PGPR and their<br />
mode of actions (Mukerji and others 2006; Kumar and others<br />
2<strong>016</strong>b). However, discovery of novel and elite strains of<br />
bacteria having nitrogen-fixing and phosphate-solubilizing<br />
abilities and/or with other plant growth-promoting traits<br />
from the native crop plants is important for development of<br />
effective biofertilizers for a particular crop.<br />
Plant microbe associations that improve soil fertility and<br />
contribute to increased overall plant growth and health are<br />
receiving increased attention for use as microbial inoculants<br />
in agriculture (Lugtenberg and Kamilova 2009; Islam<br />
and Hossain 2013). Most of the micronutrients such as Fe,<br />
Zn, Cu, and Mn are essential for plants, humans, and animals<br />
and play important roles in improving human nutrition<br />
on a global scale (Masood and Bano 2<strong>016</strong>; Saha and<br />
others 2<strong>016</strong>b; Sharma and others 2<strong>016</strong>; Shrivastava and<br />
others 2<strong>016</strong>). Several lines of evidence suggest that application<br />
of PGPR significantly enhance growth promotion<br />
and yield of crop plants, such as wheat and maize (Shankar<br />
and others 2013), chickpea (Akhtar and Siddiqui 2009),<br />
chilli (Turan and others 2012), soybean (Fernandez and<br />
others 2007), and decrease the use of synthetic chemicals<br />
in crop production (Meena and others 2<strong>016</strong>c). However, the<br />
application of PGPR as a consortium of compatible strains<br />
has been more effective than their single application in the<br />
practical field (Meena and others 2<strong>016</strong>c). This study aimed<br />
to isolate some indigenous nitrogen-fixing and P-solubilizing<br />
rhizobacteria and evaluate their effects either singly<br />
and/or combined application to seeds on growth, yield, and<br />
nutrient uptake by wheat in alluvium soils of IGP of eastern<br />
Uttar Pradesh, India.<br />
Materials and Methods<br />
Isolation and Purification of Diazotrophic<br />
Rhizobacteria<br />
A total of 90 composite rhizosphere soil samples were collected<br />
from rice, wheat, vegetables, and agro-forestry fields<br />
from seven districts of the IGP of eastern Uttar Pradesh,<br />
India (82°59′ East, 25°15′ North and 82°33′ East, 25°8′<br />
North) in 2010. The nitrogen-fixing rhizobacteria (NFR)<br />
were isolated on nitrogen-free Ashby medium (with agar)<br />
by a serial dilution technique followed by purification on<br />
the same solid medium with a repeated plating method<br />
(Schmidt and Belser 1982). Twenty-five pure isolates were<br />
obtained and tested for their N-fixing (Bremner 1965) and<br />
1 3
J Plant Growth Regul<br />
P-solubilizing abilities (Gaur 1990) using standard protocols.<br />
Among them, the three most efficient NFR strains<br />
were selected based on their higher N-fixing capacities.<br />
These superior nitrogen-fixing bacteria were identified<br />
through 16S rDNA gene sequencing.<br />
Amplification of 16S rDNA Genes by Polymerase Chain<br />
Reaction (PCR)<br />
The universal primer was used for the amplification of 16S<br />
rDNA genes for all three rhizobacterial isolates. Primer<br />
was custom synthesized by Bangalore Genei, Bangalore,<br />
India. The 50 μL of reaction mixture consisted of 50 ng<br />
of genomic DNA, 2.5 U of Taq polymerase, 5 μL of 10×<br />
buffer (100 mMTris-HCl, 500 mM KCl pH 8.3), 200 μMd<br />
NTP, 1.5mM MgCl 2 , and 10 pmoles of each primer. The<br />
forward primer 27F (5′-AGA GTT TGA TCC TGG CTC<br />
AG-3′) and reverse primer 1492R (5′-TAC GGT TAC CTT<br />
GTT ACG ACT T-3′) were used (Narde and others 2004).<br />
The amplification was performed by PCR (PCR System<br />
2720, Applied Biosystems, Singapore) conditions-initial<br />
denaturation at 94 °C for 5 min, followed by 34 cycles<br />
of denaturation at 94 °C for 1 min, annealing at 52 °C for<br />
1.5 min, extension at 72 °C for 2 min, and a final extension<br />
at 72 °C for 7 min.<br />
Amplified PCR products (5 µL) were resolved on a 1.5%<br />
(w/v) agarose gel at 100 V for 45 min in 1× TAE buffer<br />
containing ethidium bromide (EtBr) along with about<br />
500 bp DNA ladder (Bangalore Genei Pvt., Ltd. Bangalore,<br />
India). The PCR product size was approximately 1500 bp.<br />
The PCR product was purified using a PCR purification kit<br />
(Bangalore Genei, Bangalore, India) for the sequencing of<br />
16S rDNA genes.<br />
Sequencing<br />
Sequencing of 16S rDNA was carried out at Bangalore<br />
Genei Pvt. Ltd., Bangalore, India. The 16S rDNA<br />
sequences were analyzed with the nucleotide database<br />
available at the GenBank using the BLASTN tool of NCBI<br />
(http://www.ncbi.nlm.nih.gov) for homology search, and<br />
then the 16S rDNA sequences of the selected strains were<br />
submitted to the NCBI GenBank for obtaining accession<br />
numbers (Table 1).<br />
Seed Treatment<br />
Seeds of the wheat variety HUW 234 were collected from<br />
Banaras Hindu University, Agriculture Farm, Varanasi,<br />
Uttar Pradesh, India. The seeds were surface sterilized<br />
using 0.1% HgCl 2 for 2 min followed by rinsing five times<br />
with sterilized double distilled water. Enterobacter, M.<br />
arborescens, and S. marcescens were grown in nutrient<br />
broth at 120 rpm in a shaking incubator at 30 °C for 48 h.<br />
The healthy wheat seeds were treated with 5-day-old broth<br />
cultures of each of the rhizobacterial strains singly and/or<br />
in combinations along with 1 mL of sticker solution (2.5 g<br />
gum acacia + 5 g sugar in 100 mL) at a rhizobacterial population<br />
at a range of about 10 7 to 10 8 CFU seed −1 . Untreated<br />
healthy wheat seeds were used as controls.<br />
Pot and Field Experiments<br />
To study the individual and combined effects of rhizobacterial<br />
strains, pot and field experiments were conducted<br />
with the wheat variety HUW 234 during Rabi season of<br />
2011–12 and 2012–13. Three rhizobacterial strains namely<br />
Enterobacter, M. arborescens, and S. marcescens were<br />
inoculated in seven treatment combinations including controls<br />
with four replications of each treatment. For the pot<br />
experiment, alluvial soil collected from the agricultural<br />
research farm, and BHU was sieved through a 10-mesh<br />
sieve and filled in approximately 5 kg of earthen pots lined<br />
with polythene. The recommended doses of fertilizers for<br />
N-P-K (120-60-60) were thoroughly mixed in required<br />
quantity of soil. The chemical properties of pot and field<br />
soil were pH (7.84 and 7.80), EC 0.164 and 0.161 dS m −1 ,<br />
organic carbon 0.50 and 0.502% (Walkley and Black 1934),<br />
available N (0.095 g kg − 1 and 202.45 kg ha − 1 ) (Subbiah<br />
and Asija 1956), P (0.01 g kg − 1 and 19.28 kg ha − 1 ) (Olsen<br />
Table 1 Plant growth-promoting (PGP) activity of diazotrophic isolates under in vitro conditions<br />
Diazotrophic strains<br />
Nitrogen fixation mg<br />
Ng −1 carbon oxidized<br />
IAA at TP 100 µg mL − 1 pH of broth cultures P-solubilization<br />
of broth μg mL − 1<br />
Accession number<br />
2 day 2 day<br />
Control ND ND 7.00 ± 0.09 c ND NA<br />
Serratia marcescens 8.32 ± 0.39 a 21.29 ± 0.99 b 5.88 ± 0.11 b 101.04 ± 1.12 b KC453982<br />
Enterobacter 9.32 ± 0.57 b 27.06 ± 1.70 c 7.00 ± 0.10 c ND KC453983<br />
Microbacterium arborescens 8.89 ± 0.58 b 26.82 ± 1.63 c 5.67 ± 0.09 a 112.27 ± 1.44 c KC453984<br />
IAA indole acetic acid, TP tryptophan, ND not dedicated, NA not applicable, SD standard deviation. Data are average of four replicates ±SD.<br />
Mean with different letters in the same column differ significantly at P ≤ 0.05 (Fisher’s protected LSD)<br />
1 3
J Plant Growth Regul<br />
and others 1954), and K 0.118 g kg − 1 and 250.16 kg ha − 1<br />
(Jackson 1973), respectively. Ten rhizobacteria-treated<br />
seeds were sown in each pot. The uninoculated seeds were<br />
also sown in the pots as a control. Three plants were maintained<br />
after full emergence of the first leaf in each pot.<br />
The pots were arranged in a complete randomized design<br />
(CRD). During the whole experimental period, recommended<br />
agronomic practices were followed. A field experiment<br />
was conducted following a randomized block design<br />
(RBD) in four replications with alluvial soil at a farmer’s<br />
field of Bhadohi district, Uttar Pradesh, India, with plots<br />
size 5 m × 2 m (10 m 2 ). Each plot was fertilized with N-P-K<br />
(120-60-60) ha − 1 .<br />
The rhizobacteria-treated seed @ 150 kg ha − 1 was sown<br />
to each plot in line with 20 × 20 cm distance between lines.<br />
Seeds were sown at a depth of about 3 cm using a seed<br />
drill. Untreated wheat seeds were sown in control plots.<br />
The plots were irrigated timely, and recommended agronomical<br />
intercultural practices were followed. At the time<br />
of maturity, pot and field crops were harvested and threshed<br />
after optimum (~12% moisture in grain) drying. The grain<br />
yield in terms of g pot − 1 and q ha −1 was recorded for pot<br />
and field experiments, respectively. The acquisition of N<br />
and P by grain and straw and contents of Cu, Zn, Mn, and<br />
Fe in grain were determined by following the procedure as<br />
described by Iswaran and Marwah (1980).<br />
Statistical Analysis<br />
The data were analyzed by one-way analysis of variance<br />
(ANOVA). The significant differences between means were<br />
compared using Fisher’s protected LSD test at P ≤ 0.05.<br />
Statistical analysis was performed using SPSS software<br />
version 16.0.<br />
Results and Discussion<br />
In Vitro Plant Growth Promotion (PGP)<br />
by Diazotrophic Rhizobacteria<br />
Twenty-five diazotrophic bacteria were isolated from the<br />
rhizospheric soils from IGP of eastern Uttar Pradesh, India.<br />
Among them, the three best nitrogen-fixing isolates were<br />
selected for further studies and identified as Enterobacter<br />
sp., Microbacterium arborescens, and Serratia marcescens<br />
by 16 S rDNA gene sequencing (Table 1). The accession<br />
numbers of these rhizobacterial strains (S. marcescens,<br />
KC453982; Enterobacter sp., KC453983; and M. arborescens,<br />
KC453984) were deposited in NCBI GenBank. In vitro<br />
PGP activities of these three rhizobacteria were quantitatively<br />
assessed and presented in Table 1. Among these bacteria,<br />
Enterobacter sp. produced the maximum (~27 µg mL − 1 )<br />
IAA followed by M. arborescens (~26 µg mL −1 ) and S.<br />
marcescens (22 µg mL −1 ) at 100 µg mL −1 of tryptophan.<br />
IAA increases surface area and root branching in plants and<br />
facilitates nutrient uptake by plants. Jia and others (2013)<br />
demonstrated that diazotrophic rhizobacteria, S. marcescens<br />
(~17 µg mL − 1 ), and M. trichotecenolyticum (~19 µg mL −1 )<br />
produce appreciable amounts of IAA at 0.1% tryptophan.<br />
Besides IAA production, all three rhizobacteria fixed higher<br />
amounts of atmospheric nitrogen in vitro. Both Enterobacter<br />
sp. (9.32 ± 0.57 mg Ng −1 carbon utilized) and M. arborescens<br />
(8.89 ± 0.58 mg Ng −1 carbon utilized) fixed significantly<br />
higher amounts of nitrogen than S. marcescens<br />
(8.32 ± 0.39 mg Ng − 1 carbon utilized) (P ≤ 0.05). Fixation of<br />
higher amounts of atmospheric nitrogen (2–15 mg Ng − 1 carbon<br />
oxidized) by Bacillus, Klebsiella, Pseudomonas, and two<br />
rhizobacterial strains of Enterobacter has also been reported<br />
by Fayez (1990). Both nitrogen fixation and IAA production<br />
by B. megaterium, A. chlorophenolicus, and Enterobacter<br />
have been reported by many investigators (Kumar and others<br />
2014; Maurya and others 2014; Saha and others 2<strong>016</strong>a).<br />
To see whether selected diazotrophic rhizobacteria can<br />
solubilize insoluble phosphorus, we evaluated their ability<br />
in broth culture using TCP as a source of insoluble P.<br />
Although S. marcescens (101.04 ± 1.12 μg mL −1 ) and M.<br />
arborescens (112.27 ± 1.44 μg mL −1 ) solubilized appreciable<br />
amounts of P from TCP 2 days after inoculation, Enterobacter<br />
sp. was practically inactive (Table 1). The solubilization<br />
of P by both rhizobacteria was linked to a significant<br />
decrease in pH of the culture broth indicating the production<br />
of low molecular weight organic acids by the bacteria. Solubilization<br />
of P from TCP in broth culture by the production<br />
of various organic acids (citric acid, oxalic acid, succinic<br />
acid, and glycolic acid) by PGPR has been reported (Chen<br />
and others 2006; Islam and Hossain 2013; Meena and others<br />
2013, 2<strong>016</strong>a). P-solubilization by PGPR genera Bacillus,<br />
Pseudomonas, and Serratia has widely been reported<br />
(Hameeda and others 2008; Islam and Hossain 2013).<br />
Effect of Diazotrophic Strains on Growth, Yield,<br />
and Test Weight Under Pot Experiment<br />
Application of rhizobacteria alone or in various combinations<br />
significantly (P ≤ 0.05) increased growth and yield of<br />
wheat compared to untreated controls (Table 2). Co-inoculation<br />
of Enterobacter with S. marcescens and M. arborescens<br />
significantly increased (up to 14% over control) plant<br />
height of wheat followed by dual inoculation (up to 11%<br />
over control) compared to control. Single inoculation of S.<br />
marcescens showed somewhat more plant height as compared<br />
to M. arborescens and Enterobacter. Enhancement of<br />
plant height of wheat by the application of S. marcescens<br />
and Enterobacter has been reported (Zinniel and others<br />
2002; Kumar and others 2014).<br />
1 3
J Plant Growth Regul<br />
Table 2 Effect of diazotrophic strains on growth, yield, and test weight under pot and field experiments<br />
Treatments Pot experiment Field experiment<br />
Plant height at<br />
60 DAS<br />
Grain yield (g<br />
pot −1 )<br />
Straw yield (g<br />
pot −1 )<br />
Test weight<br />
(g)<br />
Plant height at<br />
60 DAS<br />
Grain yield (q<br />
ha −1 )<br />
Straw yield (q<br />
ha −1 )<br />
Test weight (g)<br />
Control 57.50 ± 0.29 a 4.71 ± 0.31 a 6.77 ± 0.03 a 34.60 ± 0.98 a 33.50 ± 0.03 a 31.80 ± 0.35 a 47.35 ± 1.80 a 33.85 ± 0.66 a<br />
Enterobacter 60.50 ± 0.29 b 6.43 ± 0.17 bc 9.27 ± 0.27 c 39.50 ± 1.50 bc 41.00 ± 0.22 cd 36.50 ± 0.87 b 55.42 ± 1.46 cd 35.99 ± 0.13 ab<br />
S. marcescens 62.50 ± 0.29 bc 5.34 ± 0.08 b 7.53 ± 0.23 ab 38.17 ± 0.89 b 40.00 ± 0.19 c 36.33 ± 0.21 b 53.78 ± 1.76 bc 34.63 ± 0.56 a<br />
M. arborescens<br />
Enterobacter<br />
+ S.<br />
marcescens<br />
Enterobacter<br />
+ M.<br />
arborescens<br />
Enterobacter<br />
+ S.<br />
marcescens+<br />
M.<br />
arborescens<br />
60.00 ± 1.45 b 5.88 ± 0.81 bc 8.73 ± 0.06 bc 39.19 ± 2.27 b 37.00 ± 0.22 b 33.65 ± 0.49 a 49.69 ± 1.03 ab 34.10 ± 1.10 a<br />
64.00 ± 0.88 cd 7.35 ± 0.60 cd 11.02 ± 0.58 d 40.84 ± 0.65 c 44.00 ± 0.58 de 38.36 ± 0.74 cd 58.48 ± 2.28 cd 38.65 ± 0.55 c<br />
64.00 ± 0.58 cd 7.67 ± 0.58 cd 11.26 ± 0.90 d 41.65 ± 0.49 cd 43.00 ± 1.49 d 37.67 ± 0.45 bc 57.71 ± 1.12 cd 37.77 ± 1.21 bc<br />
65.50 ± 0.87 d 8.47 ± 0.78 d 12.09 ± 0.52 d 44.60 ± 2.14 d 45.00 ± 0.06 e 39.45 ± 0.61 d 59.77 ± 1.93 d 39.94 ± 0.61 c<br />
‘M.’, Microbacterium; ‘S.’, Serratia; ‘g’, grams; ‘DAS’, Days after sowing; Data are average of four replicates ± SD. Mean with different letters<br />
in the same column differ significantly at P ≤ 0.05 (Fisher’s protected LSD)<br />
Co-inoculation of Enterobacter with S. marcescens<br />
and M. arborescens significantly increased grain (up to<br />
80%) and straw yield (up to 79%) of wheat compared to<br />
untreated control (Table 2). Both single and dual inoculations<br />
of wheat with the rhizobacteria also significantly<br />
increased both straw and grain yield of wheat compared<br />
with untreated controls. Although either single or dual<br />
inoculation of rhizobacteria produced statistically similar<br />
higher grain yields of wheat over controls, dual inoculation<br />
of Enterobacter with S. marcescens or M. arborescens<br />
produced significantly higher straw yield than single inoculation<br />
of any bacteria. These significant enhancements of<br />
growth and yield of wheat by the PGPR might be linked<br />
with their PGP traits recorded under the in vitro experiments<br />
(Table 1) as well as synergistic effects due to coinoculation.<br />
Inoculation of winter wheat with Enterobacter<br />
cloacae has been shown to significantly enhance yield<br />
under a growth chamber (Renato de Freitas 2000). Zahir<br />
and others (2009) demonstrated that S. proteamaculans<br />
significantly increased plant height, grain yield, 100-grain<br />
weight, and straw yield of wheat under less than 15 dS m −1<br />
salinity. A significant increase in wheat grain yield by inoculation<br />
with various PGPR strains has also been demonstrated<br />
(Kumar and others 2014). In the current study, all<br />
treatments of PGPR either alone or in combination showed<br />
significant positive influences in test weights of wheat.<br />
Co-inoculation of Enterobacter with S. marcescens and<br />
M. arborescens gave significantly higher (up to 29%) test<br />
weight compared to the control plot. Increased test weight<br />
by the effects of PGPR has been reported (Khalid and others<br />
2004; Askary and others 2009).<br />
Effects of Diazotrophic Rhizobacterial Strains<br />
on Growth and Yield Attributes of Wheat in Field<br />
Conditions<br />
The effect of diazotrophic rhizobacterial strains either<br />
applied singly or in various combinations significantly<br />
increased plant height (10–34%) compared to control<br />
(Table 2). Similarly, co-inoculation of wheat with dual or<br />
triple combinations of Enterobacter, S. marcescens, and<br />
M. arborescens significantly promoted straw yield, grain<br />
yield, and test weight of wheat compared with untreated<br />
control (Table 2). Among the treatments, a combination of<br />
Enterobacter, S. marcescens, and M. arborescens showed<br />
the highest enhancement in growth (45 ± 0.06 cm), grain<br />
(39.45 ± 0.61 q/ha) and straw (59.77 ± 1.93 q/ha) yields<br />
of wheat which were more or less statistically similar to<br />
the application of dual inoculations of these diazotrophic<br />
rhizobacteria (Table 2). However, co-inoculation of Enterobacter<br />
with S. marcescens resulted in increased grain<br />
yield, straw yield, and test weight of wheat by 21, 24, and<br />
14% over untreated controls followed by a combination of<br />
Enterobacter with M. arborescens (up to 18, 22, and 11%).<br />
Single inoculation of Enterobacter showed slightly higher<br />
yield and test weight compared to S. marcescens and M.<br />
arborescens possibly due to its higher PGP activities as<br />
shown in the in vitro assays (Table 1). The plant growthpromoting<br />
effects of PGPR shown in this study might be<br />
1 3
J Plant Growth Regul<br />
due to stimulated plant growth, absorption of nutrients,<br />
and their efficiency by the inoculated PGPR. Enhancement<br />
of growth, yield, and nutrient uptake by pearl millet and<br />
wheat by the co-inoculation of rhizobacterial inoculants, S.<br />
marcescens, Pseudomonas, and Enterobacter sp. has been<br />
reported (Hameeda and others 2006; Meena and others<br />
2015a).<br />
Effect of Diazotrophic Strains on N and P Uptake<br />
in the Pot Experiment<br />
To see whether uptake of essential plant nutrients is<br />
enhanced by the inoculation of PGPR alone or in combination,<br />
we analyzed contents of N and P in grain and straw<br />
of wheat. It revealed that total uptake of N and P was significantly<br />
increased by the rhizobacterial inoculation of<br />
wheat compared to untreated control (Table 3). The coinoculation<br />
of Enterobacter with S. marcescens and M.<br />
arborescens significantly increased N uptake by grain (up<br />
to 127%) and straw (up to 156%) of wheat over untreated<br />
controls. Similarly, P uptake was also increased by grain<br />
(up to 118%) and straw (up to 83%) of wheat over untreated<br />
controls due to inoculation with PGPR. However, co-inoculation<br />
of Enterobacter with S. marcescens caused higher<br />
amounts of N and P uptake than Enterobacter with M.<br />
arborescens which might be due to the better PGP activity<br />
of strains and their yield. The single inoculation of Enterobacter<br />
sp. gave somewhat higher N and P uptake by grain<br />
and straw than either S. marcescens or M. arborescens that<br />
can be explained on the basis of their content, yield, and<br />
PGP activity. The increased N content might be linked with<br />
the enhancement of different fractions of mineral N in soils<br />
and the PGP mechanisms through N 2 -fixation, which positively<br />
influenced plant growth and crop yields (Asghar and<br />
others 2004). The enhancement in available P content in<br />
soil shown in this study might be due to the higher solubilization<br />
of soil insoluble P from soils by S. marcescens<br />
and M. arborescens. Selvakumar and others (2008) demonstrated<br />
earlier that inoculation of S. marcescens and E.<br />
asburiae significantly enhanced N and P uptake by plants.<br />
Co-inoculation of plants with PGPR and enhancement of<br />
nutrient uptake by plants have been described in many<br />
reports (Abbasi and others 2011; Meena and others 2015a).<br />
Effect of Diazotrophic Strains on N and P Uptake<br />
in the Field Experiment<br />
Co-inoculation of Enterobacter with S. marcescens and M.<br />
arborescens consistently enhanced N and P uptake by grain<br />
and straw of wheat in the field experiment. As shown in the<br />
pot experiment, co-inoculation of these three bacteria gave<br />
the highest N and P uptake by the grain and straw of wheat<br />
which were significantly higher than untreated controls.<br />
Similarly, a combination of any two bacteria in seed inoculation<br />
also significantly increased N and P uptake by wheat<br />
compared to untreated control (Table 3). Among single<br />
inoculations, Enterobacter significantly increased N and P<br />
uptake by grain and straw of wheat over untreated control.<br />
Our results showed that nitrogen-fixing and P-solubilizing<br />
activities of the tested strains significantly influenced better<br />
N and P uptake by wheat which ultimately impacted on better<br />
growth and yield of wheat by the application of PGPR.<br />
Enhancement of growth, yield, and nutrient uptake in<br />
wheat by the application of nitrogen-fixing, P-solubilizing<br />
and IAA-producing bacteria has been reported (Khalid and<br />
others 2004). Enhancement of nutrient uptake in wheat by<br />
the application of S. marcescens and Enterobacter has also<br />
been demonstrated (Selvakumar and others 2008) (Fig. 1).<br />
Table 3 Effect of diazotrophic strains on N and P uptake by grain and straw under pot and field experiments<br />
Treatments Pot experiment Field experiment<br />
N uptake (g pot − 1 ) P uptake (g pot − 1 ) N uptake (kg ha − 1 ) P uptake (kg ha − 1 )<br />
Grain Straw Grain Straw Grain Straw Grain Straw<br />
Control 6.91 ± 0.50 a 5.15 ± 0.31 a 1.31 ± 0.20 a 0.83 ± 0.01 a 45.93 ± 0.79 a 40.59 ± 1.95 a 8.32 ± 0.90 a 5.74 ± 0.22 a<br />
Enterobacter 11.57 ± 0.14 bc 10.51 ± 0.74 c 2.10 ± 0.05 bc 1.13 ± 0.06 bc 64.32 ± 1.86 d 51.56 ± 2.33 bc 11.26 ± 1.39 bc 6.83 ± 0.21 b<br />
S. marcescens 10.59 ± 1.29 b 7.80 ± 0.55 b 1.91 ± 0.27 bc 1.11 ± 0.01 bc 60.50 ± 1.20 c 49.72 ± 0.75 b 11.00 ± 0.26 b 6.52 ± 0.24 ab<br />
M. arborescens 8.75 ± 0.22 ab 7.23 ± 0.50 b 1.68 ± ± 0.02 ab 0.93 ± 0.03 ab 53.51 ± 1.20 b 47.67 ± 0.96 b 10.40 ± 0.08 b 6.27 ± 0.20 ab<br />
Enterobacter + S.<br />
marcescens<br />
Enterobacter + M.<br />
arborescens<br />
Enterobacter + S.<br />
marcescens + M.<br />
arborescens<br />
14.76 ± 1.45 d 11.77 ± 0.61 cd 2.30 ± 0.27 c 1.28 ± 0.16 cd 67.72 ± 0.74 de 56.28 ± 1.12 cd 12.69 ± 1.10 d 7.93 ± 0.60 cd<br />
13.81 ± 0.51 cd 11.25 ± 0.46 cd 2.19 ± 0.07 bc 1.20 ± 0.11 c 66.88 ± 0.61 de 55.33 ± 1.31 cd 12.41 ± 0.21 c 7.49 ± 0.28 c<br />
15.67 ± 1.61 d 13.20 ± 0.97 d 2.86 ± 0.13 d 1.52 ± 0.06 d 69.19 ± 1.03 e 58.08 ± 2.01 d 13.02 ± 0.75 d 8.52 ± 0.27 d<br />
‘M.’, Microbacterium; ‘S.’, Serratia; ‘g’, grams; Data are average of four replicates ± SD. Mean with different letters in the same column differ<br />
significantly at P ≤ 0.05 (Fisher’s protected LSD)<br />
1 3
J Plant Growth Regul<br />
Effect of Diazotrophic Strains on Micronutrient<br />
Content in Grain in the Pot and Field Experiments<br />
Co-inoculation of Enterobacter, S. marcescens, and<br />
M. arborescens significantly increased the contents of<br />
micronutrients, for example, Cu, Zn, Mn, and Fe, in wheat<br />
grain under both pot and field experiments compared to<br />
control (Fig. 2). Significantly increased micronutrient<br />
(Zn, Fe, and Cu) contents in grain of wheat due to inoculation<br />
with siderophore-producing PGPR strains has been<br />
Fig. 1 Effect of rhizobacterial strains on micronutrient contents<br />
in grain under pot conditions, ‘S.m.’, Serratia marcescens; ‘M.a.’,<br />
Microbacterium arborescens; Data are average of four replicates<br />
±SD. Mean with different letters in the same column differ significantly<br />
at P ≤ 0.05 (Fisher’s protected LSD)<br />
Fig. 2 Effect of rhizobacterial strains on micronutrient contents in<br />
grain under field conditions, ‘S. m.’, Serratia marcescens; ‘M. a.’,<br />
Microbacterium arborescens; Data are average of four replicates<br />
±SD. Mean with different letters in the same column differ significantly<br />
at P ≤ 0.05 (Fisher’s protected LSD)<br />
1 3
J Plant Growth Regul<br />
reported (Kumar and others 2014). The co-inoculation of<br />
Enterobacter with S. marcescens significantly enhanced<br />
Cu, Zn, Mn, and Fe contents in wheat grain by 56, 32, 52,<br />
and 18% in the pot and 43, 23, 48, and 16% in the field<br />
experiment. Co-inoculation of wheat with Enterobacter<br />
with M. arborescens also showed similar performances in<br />
micronutrient uptake by the wheat. However, single inoculation<br />
of rhizobacterial strains, Enterobacter and M. arborescens,<br />
displayed a significant effect over controls regarding<br />
micronutrient content in grain. The synergistic effects<br />
of PGPR inoculation leads to increased micronutrient content<br />
of wheat plants which might be due to a positive effect<br />
for improving the translocation of micronutrients from soils<br />
to plants. Micronutrient uptake from the rhizosphere soil is<br />
the first step in the process of accumulation in plants, prior<br />
to translocation to seed. These PGPR strains may be elucidated<br />
by their ability to enhance the nutrient availability in<br />
the soil system, which enhanced nutrient uptake by the crop<br />
(Abdel-Wahab and others 2008; Verma and others 2010).<br />
The micronutrient concentrations in grain for all treatments<br />
were slightly higher under the pot as compared to the field<br />
experiment, which could be due to reduced chelation, limited<br />
ion exchange, no leaching, and lack of weeds in the pot<br />
culture compared to the field conditions (Kumar and others<br />
2014; Meena and others 2015b).<br />
Conclusions<br />
Isolation of elite strains of PGPR and integration of a possible<br />
combination of synergistic bacteria in the consortium<br />
application to plants is crucial for the highest promotion<br />
of plant growth and yield. In the current study, we isolated<br />
and identified three potential diazotrophic bacteria<br />
(Enterobacter sp., S. marcescens, and M. arborescens) and<br />
applied them alone or in varying combinations to assess<br />
their effects on growth, yield, and nutrient uptake by wheat.<br />
Co-inoculation of these three PGPR consistently increased<br />
nutrient uptake, growth, and yield of wheat under both the<br />
pot and field experiments. Our results suggest that application<br />
of PGPR in a consortium with synergistic bacteria having<br />
multiple plant growth-promoting traits such as nitrogen<br />
fixation; P-solubilization and IAA production could be used<br />
for boosting wheat production in a sustainable manner. The<br />
findings of this research could be used for development of<br />
an eco-friendly and cost-effective technology for biofertilization<br />
of wheat which might reduce the application of<br />
chemical fertilizers and save fossil fuel consumption.<br />
Acknowledgements The authors are thankful to Uttar Pradesh<br />
Council of Agricultural Research for funding the research work.<br />
Thanks are also due to the Head, Department of Soil Science and<br />
Agricultural Chemistry, Institute of Agricultural Sciences, Banaras<br />
Hindu University, Varanasi, India, for providing the necessary facilities<br />
required for conducting the research work.<br />
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