Subscriber access provided by UNIV OF NEWCASTLE
Article
Compatible rhizosphere competent microbial consortium add value to nutritional quality in edible parts of chickpea Sudheer KUmar Yadav, Surendra Singh, Harikesh Bahadur Singh, and Birinchi Kumar Sarma J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.7b01326 • Publication Date (Web): 12 Jul 2017 Downloaded from http://pubs.acs.org on July 12, 2017
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a free service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are accessible to all readers and citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
Journal of Agricultural and Food Chemistry is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 32
Journal of Agricultural and Food Chemistry
1
Compatible rhizosphere competent microbial consortium add value to nutritional quality
2
in edible parts of chickpea
3 4
Sudheer K. Yadav1, Surendra Singh1, Harikesh B. Singh2, Birinchi K. Sarma2*,
5
1
Department of Botany, Institute of Science, Banaras Hindu University, Varanasi-221005
6
2
Department of Mycology and Plant Pathology, Institute of Agricultural Sciences, Banaras
7
Hindu University, Varanasi-221005
8 9
*Corresponding Author Email:
[email protected] 10 11
Abstract
12
Chickpea is used as a high energy and protein source in human and livestock’s diets. Moreover,
13
chickpea straw can be used as alternative of forage in ruminant diets. The present study evaluates
14
the effect of beneficial microbial inoculation on enhancing the nutritional values in edible parts
15
of chickpea. Two rhizosphere competent compatible microbes (Pseudomonas fluorescens OKC
16
and Trichoderma asperellum T42) were selected and applied to seeds either individually or in
17
consortium before sowing. Chickpea seeds treated with the microbes showed enhanced plant
18
growth (88.93% shoot length at 60 DAS) and biomass accumulation (21.37% at 120 DAS).
19
Notably, the uptake of mineral nutrients viz. N (90.27, 91.45, 142.64%), P (14.13, 58.73,
20
56.84%), K (20.5, 9.23, 35.98%), Na (91.98, 101.66, 36.46%), Ca (16.61, 29.46, 16%) and
21
organic carbon (28.54, 17.09, 18.54%) was found in seed, foliage and pericarp of the chickpea
22
plants, respectively. Additionally, nutritional quality viz. total phenolic (59.7, 2.8, 17.25%),
23
protein (9.78, 18.53, 7.68%), carbohydrate content (26.22, 30.21, 26.63%), total flavonoid
24
content (3.11, 9.15, 7.81%) and reducing power (112.98, 75.42, 111.75%) was also found in
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
25
seed, foliage and pericarp of the chickpea plants. Most importantly the microbial consortium
26
treated plants showed maximum increase of nutrient accumulation and enhancement in
27
nutritional quality in all edible parts of chickpea. Nutritional partitioning in different edible parts
28
of chickpea was also evident in the microbial treatments compared to their uninoculated ones.
29
The results thus clearly demonstrated microbe-mediated enhancement in dietary value of the
30
edible parts of chickpea as seeds are consumed by human whereas pericarp and foliage (straw)
31
are used as alternative of forage and roughage in ruminant diets.
32
Keywords: Biofertilizers, Nutrient content, Nutritional value, Shikimic acid, Microbial
33
consortium, Phenolics
34
Introduction
35
The present world population of about 7.2 billion is expected to cross 9.6 billion by the end of
36
year 2050.1 In order to provide food to all by that time, the annual production of legumes needs a
37
significant jump. To achieve this onerous target and to meet the food requirement of the people,
38
the current agricultural practices in many developing countries have become heavily dependent
39
on the intensive use of chemical fertilizers and pesticides which led to severe problems to human
40
health and environment. Therefore, priority should be given to the use of microorganisms as
41
biofertilizers for food security and sustainable crop production as an ecofriendly approach.2 In
42
this context, recently attempts have been made more towards ‘nutrient rich high quality food’
43
production in sustainable agriculture to secure bio-safety.3 Hence the enhancement in nutritional
44
quality of food in their natural surroundings particularly in agricultural field conditions is best
45
adopted for the sustainable agriculture.4 The use of biofertilizers has been found to enhance the
46
plant growth, yield, nutrient content, activate plant defense and improved the signaling network.5
47
Recently, organic inputs have been recommended as an alternative of soil fertilization for
ACS Paragon Plus Environment
Page 2 of 32
Page 3 of 32
Journal of Agricultural and Food Chemistry
48
improvement of nutrient supply and maintenance of field management.6 In this context organic
49
farming is helpful in ensuring the food safety along with the maintenance of soil biodiversity.7
50
Furthermore, biofertilizers are having additional advantage due to their longer shelf life without
51
imparting any harmful effects to the ecosystem.8 Biofertilizers also maintain the soil fertility
52
through various processes such as N2-fixation, phosphate solubilization, mineralization, secretion
53
of plant growth regulating compounds, production of antibiotics and biodegradation of organic
54
matters.9
55
Chickpea (Cicer arietinum L.) is an important grain legume used all over the world as a
56
good source of minerals, proteins, vitamins, and regularly included in human diets. The prospect
57
of food legumes for the livestock food mainly depends on their nutrient contribution in diet.
58
Young and fresh chickpea leaves are also used as cooked green vegetable to provide plenty of
59
dietary nutrients in malnourished populations in certain parts of the world.10 Whereas, chickpea
60
is produced mostly for human consumption, it is however, also used as an alternative to supply
61
proteins and energy feed for livestocks. Chickpea straw is also used as fodder for ruminants.11
62
Chickpea straw is a primary and major by-product after harvesting and thrashing, and also
63
contributes equal or more than grain yield. It has higher nutritional quality and palatability than
64
cereals straw.12 Thus, it is evident that no part of chickpea is a waste as all parts are consumed at
65
different stages by human and livestock.
66
Rhizosphere competent microbes are used mostly as biofertilizers or biopesticides
67
successfully13. However, what impacts they may have on the nutritional quality of edible parts of
68
the introduced crops are not well known. Keeping this in view, we used two beneficial
69
rhizosphere competent microbes, viz., Trichoderma asperellum strain T42 (GenBank accession
70
JN128894) and Pseudomonas fluorescens strain OKC (GenBank accession JN128891) either
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
71
individually or in combination, and evaluated the possible impacts they could have on the
72
nutritional quality of edible parts of chickpea in the current study. We evaluated nutritional
73
values of chickpea seeds along with foliage and pericarp and compared the values with non-
74
microbe introduced plants. The experiment was conducted under natural field condition in order
75
to get an appropriate idea how the microbes influences the nutritional values of chickpea under
76
natural environmental conditions.
77
Materials and methods
78
Organisms
79
Pseudomonas fluorescens OKC (GenBank accession JN128891) was isolated from the
80
rhizosphere of okra (Abelmoschus esculentus) plant on King’s B agar medium, whereas
81
Trichoderma asperellum T42 (GenBank accession JN128894) was obtained from a pool of
82
Trichoderma isolates maintained in the Department of Mycology and Plant Pathology, Institute
83
of Agricultural Sciences, Banaras Hindu University and grown on Potato Dextrose Agar (PDA).
84
Both the strains were selected on the basis of their plant growth promotion activities as well as
85
compatibility between them.14 The Pseudomonas strain was identified by sequencing the 16s
86
rDNA region15, and the Trichoderma isolate was identified by sequencing the ITS region.16,17
87
Inoculum preparation, seed treatment and sowing
88
Seeds of chickpea (Cicer arietinum L. var. Avrodhi) were surface sterilized by using 1% sodium
89
hypochlorite for 3 min and further rinsed 10 times with sterilized distilled water. P. fluorescens
90
strain OKC was inoculated in King’s B broth and incubated at 28°C in incubator shaker at 100
91
rpm for 48h. Bacterial culture was collected in the form of pellet by centrifugation at 4°C
92
(10,000xg for 2 min), the resulting pellets were washed with sterilized distilled water thrice and
93
absorbance of the homogenous suspension was measured spectrophotometrically at 600 nm. The
ACS Paragon Plus Environment
Page 4 of 32
Page 5 of 32
Journal of Agricultural and Food Chemistry
94
optical density for CFU 108 ml-1 P. fluorescens OKC was determined as 0.393. Similarly, the
95
Trichoderma isolate T42 was inoculated on PDA and incubated at 28°C for 4 days. Spores of
96
T42 were harvested in sterilized distilled water, absorbance of the spore suspension was
97
measured at 600 nm and optical density for CFU 107 mL-1 of T42 was determined as 1.14. OKC
98
cell suspension and T42 spore suspension were mixed in equal volume for consortium treatment.
99
Both cell and spore suspensions were mixed with 1% carboxy methyl cellulose (CMC).18 The
100
treatments applied were as follows: OKC = P. fluorescens strain OKC, T42 = T. asperellum T42,
101
OKC + T42, Control = without any microbial treatment. For sowing, the field was divided into 4
102
square meter sized experimental plots. Row to row spacing was maintained at 30 cm whereas
103
plant to plant spacing was maintained at 15 cm. The four treatments were arranged in CRBD in
104
two blocks. Each treatment was replicated thrice. Prescribed agronomical practices were adopted
105
for chickpea cultivation in Uttar Pradesh of India.
106
Plant growth promoting traits
107
For recording the growth parameters, three chickpea plants were uprooted randomly from each
108
plot after 60 and 120 days after germination (DAG). To remove soil particles adhered to the
109
roots surface, the plants were thoroughly washed by placing them on a sieve (mesh size 1 mm)
110
under running tap water. The washed plants were initially air dried followed by oven-dried at 45-
111
50°C19 by placing them on two layers of blotting papers. Shoot length (SL), shoot fresh weight
112
(SFW), shoot dry weight (SDW), root length (RL), root fresh weight (RFW), root dry weight
113
(RDW) and total biomass (TB) were quantified after 60 days of sowing and data from the
114
replicated plots were pooled. Seed, foliage and pericarp yields were also recorded from all the
115
treatments. Seed, foliage and pericarp of 100 plants from replicated plots were used for dry
116
biomass measurement from each treatment.
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
117
Preparation of plant samples for analysis
118
Seed, pericarp and foliage were separated from 50 randomly selected plants from all replications,
119
mixed thoroughly and oven dried. Dried samples were then grounded and the ground powder
120
was used for further analysis.
121
Nutrient analysis
122
Approximately 200 mg of oven-dried fine powder of plant materials was dissolved in 5 ml of
123
concentrated sulphuric acid (AR grade). The flask was shaken in swirling motion and kept at
124
room temperature for 20 min. The content was boiled gently for 30 min and to that 1 ml of 4%
125
(v/v) perchloric acid (62%) was added. The content was further heated gently till the digest
126
became clear and kept at room temperature for cooling. Phosphorus (P) was extracted by nitric–
127
perchloric acid digestion and measured using the vanadomolybdophosphoric acid colorimetric
128
method.20 Potassium (K), sodium (Na) and calcium (Ca) was assayed using flame
129
spectrophotometer (Corning 400, UK)21 whereas total nitrogen (N) and total organic matter were
130
determined by using Kjeldahl method,22 and Walkley and Black23, respectively.
131
Total phenol content
132
Total phenol content (TPC) was determined following the method of Zheng and Shetty.24 Leaf
133
sample (0.1 g) was collected from the mixture of 50 randomly selected plants from all
134
replications and placed in 95% ethanol (5 ml) and kept at 0°C for 48 h. The samples were
135
homogenized individually and centrifuged at 13000 rpm for 10 min. To 1 ml of the supernatant,
136
1 ml of 95% ethanol, 5 ml of sterilized distilled water and 0.5 ml of 50% Folin-Ciocalteau regent
137
was added and the contents were mixed thoroughly. After 5 min, 1 ml of sodium carbonate (5%)
138
was added to the reaction mixture, the reaction mixture was allowed to stand for 1h and the
139
absorbance of the colour developed was recorded at 725 nm against a reagent blank. Standard
ACS Paragon Plus Environment
Page 6 of 32
Page 7 of 32
Journal of Agricultural and Food Chemistry
140
curves were prepared for each assay using various concentrations of gallic acid (GA; Sigma,
141
USA) in 95% ethanol. Absorbance values were converted to mg GA equivalents (GAE) g-1 FW.
142
Protein content
143
Protein content was estimated following the method of Lowry et al.25 using bovine serum
144
albumin as standard and expressed in terms of mg protein g−1 FW. 0.1g sample (collected
145
similarly as TPC) was extracted in 0.1M phosphate buffer (5ml, pH=7.0). The reagent A,
146
alkaline sodium carbonate (2%) was prepared in sodium hydroxide (0.1N) and reagent B, copper
147
sulphate (0.5%) in potassium sodium tartrate (1%). Further fresh alkaline copper solution was
148
prepared by adding 50ml of reagent A and 1ml of reagent B. The aliquot of 0.2ml sample extract
149
was made up to 1 ml by adding distilled water and alkaline copper solution was added (5ml). The
150
solution was mixed thoroughly and incubated at room temperature for 10 min. 0.5ml of diluted
151
folin-ciocalteau reagent (1:1) was added in the solution, mixed thoroughly and incubated at room
152
temperature for 30 min in dark. The blue color was developed and absorbance was taken at
153
660nm. The blank was prepared directly with 1ml of distilled water (without sample extract) and
154
followed the same procedure as done with extracted samples.
155
Total carbohydrate
156
Total carbohydrate was measured using anthrone method.26 Seed, foliage and pericarp samples
157
(0.1g each) were first hydrolyzed into simple sugars using dilute HCl (2.5N) in boiling water
158
bath for 3h. The solution was neutralized with solid Na2CO3 until the effervescence ceased and
159
the final volume was made up to 100ml. One ml aliquots was mixed thoroughly with 4ml
160
anthrone reagent and incubated in boiling water bath for 8 min. Absorbance of the dark green
161
color developed was recorded at 630nm upon cooling. Absorbance values were converted to mg
162
glucose g-1 dry weight (DW) using the standard curve of glucose.
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
163
Preparation of extracts from chickpea plant parts for determination of total flavonoid
164
content and reducing power
165
The extracts were prepared by dissolving 2.0 g powders of seeds, foliage and pericarp separately
166
from the oven dried and ground powders in 10 ml of methanol (50%) and incubated overnight at
167
room temperature. The extracts were filtered through sterilized Whatman No. 1 filter paper and
168
further fractionated with equal volume of ethyl acetate in separating funnel by shaking
169
vigorously. The ethyl acetate fractions were taken out separately, and the residue was
170
refractionated using the ethyl acetate. The pooled fractions were evaporated and dried samples
171
were dissolved in 2.0 ml of HPLC grade methanol and used for analysis.27
172
i.
Total flavonoid content (TFC)
173
TFC was quantified by method of Irshad et al.28 and expressed in quercetin equivalents of
174
standard curve. To 0.5 ml extract, 4ml of distilled water and 0.3ml of 50% NaNO2 solution were
175
added. After 5 min, 0.3 ml of 10% AlCl3 solution was added mixed thoroughly. Again after
176
another 5 min, 2 ml of 1 M NaOH was added and the volume was made up to 10 ml with 95%
177
ethanol. The solution was mixed thoroughly and absorbance was recorded at 510 nm. TFC was
178
expressed as mg quercetin equivalents g−1 FW.
179
ii.
Reducing power (RP)
180
The reducing power of the plant extracts was evaluated by modified ferric reducing antioxidant
181
power assay.29 To 500 µl aliquots of the extract, 1.0 ml methanol and 2.5 ml each of phosphate
182
buffer (pH 6.6) and 1% (w/v) potassium ferricyanide were added. The reaction mixture was
183
incubated at 50°C in a water bath for 20 min. The reaction was terminated by the addition of 2.5
184
ml TCA (10% w/v). Further above reaction mixture was diluted with an equal volume of
185
deionized water and 0.5 ml FeCl3 (0.1% w/v) was added. Absorbance was measured at 700 nm
ACS Paragon Plus Environment
Page 8 of 32
Page 9 of 32
Journal of Agricultural and Food Chemistry
186
against a reagent blank after 10 min. RP was expressed as ascorbic acid equivalent (1 ASE = 1
187
mM). The ASE/ml value is inversely proportional to reducing power.
188
High performance liquid chromatography (HPLC) analyses of seed, foliage and pericarp
189
Ground powders from different parts of chickpea were used for extraction of phenolic
190
compounds. One gram of the ground samples from seed, foliage and pericarp was extracted with
191
50% methanol (10 ml) separately. The solvent was removed under reduced pressure in rota-
192
evaporator (Eyela N–Nseries, Tokyo, Japan), the resulting residue was solubilized in HPLC
193
grade methanol, and specific phenolics were analyzed using quantitative HPLC. The HPLC
194
(Shimadzu LC-10A, Japan) was furnished with dual pump LC-10A binary system, UV detector
195
SPD-10A and Phenomenex (Torrance, USA) C18 column (4µm, 250×4.6 mm). The data were
196
integrated by Shimadzu LC solution series software. Compounds were separated with
197
acetonitrile and 1% acetic acid in a linear gradient program, starting with 18% acetonitrile,
198
changing to 32% in 15 min and finally to 50% in 40 min30. Solvent flow rate was maintained to
199
1.0 mL min-1. Results (µg g-1 DW) were calculated by comparing the peak areas (max 254 nm)
200
of the samples with those of standards (LC solution series software, Shimadzu, Japan).
201
Statistical analyses
202
Data from different experiments were recorded as mean ± standard deviation (SD) of at least five
203
replications (five repeated analyses in one experiment) and were subjected to analysis of
204
variance (ANOVA). The treatment mean values were compared by Duncan’s multiple range test
205
(DMRT) at p ≤ 0.05 significance level. The software used for analysis was SPSS version 16. The
206
Principal Component Analysis (PCA) was performed using R-program.
207
Results
208
Plant growth, biomass and yield
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 10 of 32
209
Chickpea plants raised from seeds treated with the rhizosphere competent compatible microbes
210
either individually or in consortium showed increase in dry weight and yield of seed, foliage and
211
pericarp compared to the plants raised from untreated seeds (Fig. 1). Significant increase in dry
212
weight was observed in seed and pericarp (17.6 and 28.15%, respectively) in the plants raised
213
from seeds treated with the microbial consortium of P. fluorescens OKC and T. asperellum T42
214
compared to their untreated control counterparts. Dry weight of foliage was also increased over
215
the control but it was not significantly high. Although applications of the microbes OKC and T42
216
individually also resulted in increased biomass of different chickpea parts, but the increase in dry
217
weights in the consortium treated plants were higher. Similarly, there was significant increase in
218
root and shoot lengths in all microbial treatments but the consortium treated plants showed
219
maximum increase of shoot and root lengths (88.93 and 98.61%, respectively). Additionally, it
220
was also recorded that there was significant increase in, shoot fresh and dry weight, root fresh
221
and dry weight (RDW) as well as total biomass (88.62, 138.2, , 200, 71.75 and 123.63%,
222
respectively) in consortium treated plants compared to untreated control plants after 60 days of
223
sowing. Between the two microbes Trichoderma and Pseudomonas it was interesting to note that
224
the fungal strain T. asperellum T42 enhanced shoot biomass more compared to the bacterial
225
strain whereas the bacterial strain P. fluorescens OKC enhanced root biomass more compared to
226
the fungal strain.
227
Nutrient content
228
Nutrient contents (N, P, K, Na, Ca and total organic carbon) in seed, pericarp and foliage of
229
chickpea plants treated with the microbial consortium were significantly high compared to the
230
untreated control counterparts (except potassium in foliage). Interestingly, application of the
231
microbes individually also increased the nutrient contents in most of the cases but the difference
ACS Paragon Plus Environment
Page 11 of 32
Journal of Agricultural and Food Chemistry
232
was not significant in various occasion. The results thus show the significance of combining
233
compatible microbes over use of single microbes.
234
Total P content in seeds, pericarp and foliage of chickpea varied from 155.91 to 177.95,
235
43.87 to 68.81 and 91.51 to 145.26 mg g-1, respectively (Fig. 2A). Total P content in seed,
236
pericarp and foliage was 14.13, 56.84 and 58.73% higher, respectively, in the microbial
237
consortium treatment compared to the untreated control plants. However, the maximum P
238
content was found in seeds followed by foliage and pericarp. Similarly, N content also varied
239
from 2.88 to 5.48, 0.68 to 1.65 and 1.17 to 2.24% in chickpea seed, pericarp and foliage,
240
respectively, and maximum being recorded in the plants treated with the consortium of OKC and
241
T42 (Fig. 2B). N content was also recorded highest in the seeds followed by foliage and pericarp.
242
The K concentration also varied from 308.93 to 372.26, 658.7 to 895.73 and 477.16 to
243
521.2 ppm in seed, pericarp and foliage, respectively (Fig. 2C). Highest accumulation of K in
244
seeds, pericarp and foliage of the chickpea plants was also recorded in the consortium treatment
245
and the increase was 20.5, 35.98 and 9.23%, respectively, compared to the untreated control
246
plants. Unlike N and P contents, pericarp of the chickpea plants had maximum K concentration
247
followed by foliage and seed. However, the amount of K content in different parts varied
248
significantly. The K content in pericarp and seeds of chickpea plants treated with the microbial
249
consortium varied significantly but the difference in K content between pericarp and foliage did
250
not vary significantly. Similarly, richness in Na concentration was also highest in pericarp
251
followed by seed and foliage (Fig. 2D) similar to the K content. The concentration of Na ranged
252
from 9.86 to 18.93, 20.11 to 27.48 and 6.59 to 13.29 ppm in seed, pericarp and foliage,
253
respectively. However, unlike the K content, highest Na concentration was observed in OKC
254
treated plants compared to the microbial consortium treatment. Pericarp of chickpea plants
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 12 of 32
255
contained 52.31% higher Na from OKC treated plants compared to their untreated control
256
counterparts. However, chickpea plants treated with the consortium of OKC and T42 had
257
maximum Na in seeds and foliage compared to Na concentration in all three parts in untreated
258
control counterparts. Chickpea plants treated with the consortium showed 91.98, 36.64 and
259
101.67% increase in Na concentration in seed, pericarp and foliage, respectively, to that of their
260
untreated control counterparts. The Ca concentration also showed a similar trend of
261
accumulation in different chickpea parts. Similar to K and Na, the pericarp of the chickpea plants
262
had maximum Ca concentration followed by foliage and seed. The Ca concentration ranged from
263
86.23 to 100.56, 505.6 to 586.5 and 151.86 to 196.6 ppm in seed, pericarp and foliage,
264
respectively, and maximum being in the plants treated with the microbial consortium (Fig. 2E).
265
The increase in Ca concentration in seed, pericarp and foliage in the consortium treated plants
266
was 16.61, 16 and 29.46%, respectively, compared to the untreated control counterparts.
267
The organic carbon content was also enhanced significantly in chickpea seed, foliage and
268
pericarp of the plants raised from seeds treated with the microbial consortium (Fig. 2F). The
269
organic carbon content ranged from 32.13 to 41.3, 32.77 to 38.37 and 27.18 to 32.22 mg g-1 in
270
seed, pericarp and foliage, respectively. A significant increase of 28.54, 17.09 and 18.54% in
271
organic carbon content was recorded in seeds, foliage and pericarp, respectively, of the chickpea
272
plants raised from seeds treated with the consortium compared to the untreated control.
273
Interestingly, no significant difference in organic carbon content was recorded in pericarp of the
274
chickpea plants raised from the seeds treated with P. fluorescens alone compared to the untreated
275
control.
276
Biochemical contents in chickpea
ACS Paragon Plus Environment
Page 13 of 32
Journal of Agricultural and Food Chemistry
277
Influence of the microbes on biochemical contents such as total phenolics, protein, carbohydrate
278
and flavonoids was also similar to their effect on host biomass enhancement and nutritional
279
contents. The microbial consortium treated plants showed significant increase in the biochemical
280
contents in different parts of chickpea compared to the untreated control plants and in several
281
instances over the individual microbial treatments.
282
Total phenolic content (TPC)
283
TPC was highest in the foliage of chickpea plants followed by pericarp and seed in all microbial
284
treatments compared to the untreated controls (Fig. 3A). TPC in foliage were nearly ten folds
285
higher compared to seeds and nearly 2 folds higher compared to pericarp. TPC ranged from 0.67
286
to 1.07, 4.23 to 4.96 and 7.15 to 12.36 mg g-1 in seed, pericarp and foliage, respectively. TPC
287
content did not vary significantly in most of the individual microbial treatments but the
288
variations were significant in the microbial consortium treatment. Increase in TPC in seed,
289
pericarp and foliage was 59.7, 17.25 and 2.8%, respectively, compared to their untreated control
290
counterparts.
291
Protein content
292
Protein content in seed, pericarp and foliage of chickpea plants treated with the microbial
293
consortium was higher compared to their untreated control plants (Fig. 3B). Protein content of
294
seed, pericarp and foliage of the chickpea plants treated with the consortium of OKC and T42
295
was 9.78, 7.68 and 18.53% higher, respectively, than their untreated control plants. The protein
296
content ranged from 659.7 to 724.3, 434.02 to 467.36 and 424.86 to 503.61 µg g-1 of dry weight
297
in seed, pericarp and foliage, respectively. Total protein content was highest in seed followed by
298
foliage and pericarp. The protein content in seed was higher than foliage and pericarp and its
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 14 of 32
299
content was nearly equal in foliage and pericarp. However, statistically no significant difference
300
was recorded in the protein content of the pericarp of treated and untreated chickpea plants.
301
Total carbohydrate content
302
Total carbohydrate content varied from 56.67 to 71.53, 57.3 to 72.56 and 58.58 to 76.28 mg g-1
303
of dry weight in seed, pericarp and foliage, respectively (Fig. 3C). Chickpea plants treated with
304
the microbial consortium recorded maximum carbohydrate contents followed by the plants
305
treated with either Trichoderma or Pseudomonas alone. In contrast the untreated chickpea plants
306
had lowest carbohydrate content in their seed, pericarp and foliage compared to the microbial
307
treatments. Statistically significant increase in total carbohydrate content was recorded in the
308
consortium treated chickpea plant parts compared to the individual microbial treatments and
309
control plant parts.
310
Total flavonoid content (TFC)
311
Total flavonoid content in seed, pericarp and foliage of the chickpea plants varied from
312
0.998±0.001 to 1.029±0.0128, 1.139±0.003 to 1.22±0.003 and 1.257±0.016 to 1.371±0.014 mg
313
quercetin equivalents g−1 DW, respectively (Fig. 3D). Seeds, pericarp and foliage of the chickpea
314
plants treated with the microbial consortium of OKC and T42 showed 3.11, 7.81 and 9.15%
315
higher accumulation of flavonoid content compared to their untreated control counterparts. Total
316
flavonoid content was significantly high in all chickpea parts in the consortium treatment
317
compared to their untreated control counterparts. In contrast, no significant difference in
318
flavonoid content was observed in the chickpea parts of the individual microbial treatments of
319
either OKC or T42. Flavonoid content was highest in foliage followed by pericarp and least in
320
seed.
321
Reducing power (RP)
ACS Paragon Plus Environment
Page 15 of 32
Journal of Agricultural and Food Chemistry
322
Similar to total flavonoid contents the reducing power of seed, pericarp and foliage of chickpea
323
plants was high in all parts of the consortium plants compared to that of untreated control plants.
324
The percent increase in reducing power varied from 29.12 to 62.0, 27.92 to 59.11 and 33.7 to
325
59.11 in seed, pericarp and foliage, respectively (Fig. 4). Reducing power was significantly high
326
in all chickpea parts in the microbial consortium treatment compared to their individual
327
treatments and untreated control plants. Interestingly, the reducing power in all chickpea parts
328
treated with the microbial consortium was nearly equal.
329
HPLC analysis of phenolics and flavonoids
330
HPLC analyses revealed variations in the phenolic acid contents in different chickpea parts in
331
different treatments. Altogether 8 compounds viz., shikimic acid, and phenolic acids such as
332
gallic acid, t-chlorogenic acid, syringic acid, p-coumaric acid, ferulic acid, quercetin and
333
kaempferol were detected from the chickpea part extracts. Phenolic acid contents in foliage, seed
334
and pericarp were significantly high in microbial treatments particularly in the microbial
335
consortium treatment (except t-chlorogenic acid and quercetin in pericarp) compared to their
336
control counterparts (Table 1). Similarly, shikimic acid content was also significantly high in
337
both seed and foliage but the content is not-significantly high in pericarp. Individually, the
338
phenolic acids, viz., t-chlorogenic acid, syringic acid, and p-coumaric acid, and flavonoids
339
quercetin and kaempferol accumulated in higher contents in either pericarp or foliage in the
340
microbial consortium treatment whereas highest accumulation of the other two phenolics gallic
341
and ferulic acids was observed in individual treatment of OKC in pericarp. Among the three
342
different chickpea parts, phenolic acid accumulation was least in chickpea seeds. Nevertheless,
343
the phenolic acid contents in seeds were higher in all microbial treatments compared to the
344
untreated control counterparts.
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 16 of 32
345
PCA analysis showed that total phosphorus and nitrogen contents are the major
346
components that clubbed with dry weight and protein content of the chickpea seeds in various
347
treatments where plants were raised from either individual Pseudomonas and Trichoderma
348
treated seeds or plants raised from the consortium treated seeds. Similarly, the mineral contents
349
of Na, Ca and K along with organic matter content were clubbed with the carbohydrate content
350
and reducing power of the pericarp of plants in various treatments that were raised from either
351
individual Pseudomonas and Trichoderma treated seeds or plants raised from the consortium
352
treated seeds. Similarly, the total phenolic content was clubbed with the total flavonoid content
353
in all treatments in foliage (Fig. 5).
354
Discussion
355
Chickpea is an important food component in large parts of the world31 but very little is known
356
about its potential health benefits compared to the other legumes. Few earlier studies showed that
357
chickpea consumption lower the serum total cholesterol levels32,33 and coronary heart disease
358
(CHD) risk34. Efforts are being made to increase nutritional value of food through breeding
359
programs, biotechnological interventions and dietary supplements to the food products.
360
Rhizosphere microbe-induced plant defense is well demonstrated, however, unifying studies
361
linking rhizosphere microbe-induced nutritional value in edible parts in crop plants are still
362
lacking. Therefore, in the present study, we compared the effects of two rhizosphere competent
363
and compatible microbes (P. fluorescens OKC and T. asperellum T42) in enhancing the
364
nutritional value in human and livestock edible parts of chickpea.
365
N, P and K are the three main inorganic mineral nutrients which are essentially required
366
for crop growth. They are also crucial constituents of several enzymes, hormones, amino acids
367
and genetic materials in plants that take part in various life functions.35-37 Rhizosphere competent
ACS Paragon Plus Environment
Page 17 of 32
Journal of Agricultural and Food Chemistry
368
microbes play a vital role in making these nutrients available for plant uptake and their use
369
efficiency by the host plants.13 We observed a direct correlation of increased dry weight and
370
protein content of seeds in microbial treatments with increase in total phosphorus and nitrogen
371
content. Similarly, we also observed that increase in minerals and organic matter also correlated
372
with carbohydrate content in chickpea in the microbial treatments. Additionally, the total
373
phenolic content was found directly correlated with total flavonoid content in foliage collected
374
from the plants raised from seeds treated with the microbes. These correlations could directly be
375
attributed with enhanced uptake of several important nutrients (N, P, K, Na, and Ca) by chickpea
376
in microbial treatments compared to their untreated control counterparts. Interestingly, chickpea
377
plants treated with the consortium of OKC and T42 showed maximum increase in nutrient
378
contents indicating the advantage of consortium treatment of compatible microbes over their
379
individual applications. Microbial consortium potentially mimics the natural environmental
380
conditions where soil microbes lives in community. Hence, in the present study enhanced
381
nutrient content in chickpea plant parts in the microbial consortium treatment could be attributed
382
to natural lifestyle with synergistic effects of the two microbes. Similar increase in N content is
383
also reported in chickpea plants treated with indigenous Mesorhizobium sp. and P. aeruginosa.38
384
Since, human and animals acquire most of the nutrients through food products, abundance of
385
nutrients in edible plant parts is therefore desirable as they affect our daily diets.
386
Further, significant increase in total phenolics, protein, flavonoid and carbohydrate
387
contents in consortium treated chickpea plant parts compared to untreated control plants is a true
388
indication of improved nutritional qualities in consortium treated plants. Since phenols are
389
important arsenal for plant defense against any invading pathogens and are closely associated
390
with free radical scavenging property, higher accumulation of phenolics in microbe treated
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 18 of 32
391
chickpea plants is highly significant from health point of view. Similarly, polyphenols are also
392
involved in receptors and enzymes associated in the signal perception and transduction
393
pathways, and change the cellular redox conditions.39 Further, enhanced accumulation of
394
phenolics was also reported in Trigonella foenum-graecum when the plants were treated with
395
Bacillus lentimorbus.40 Individually shikimic acid is also important because it acts as a precursor
396
molecule for almost all phenolic compounds. It is interesting to note that shikimic acid
397
accumulation was more in pericarp and foliage compared to seeds in consortium treated seeds.
398
Higher shikimic acid accumulation indicates the additional advantage the host derives due to
399
enhanced phenylpropanoid activities leading to higher phenolics synthesis as these parts are
400
usually subjected to pathogen attacks. Similarly, a significant increase in quercetin and
401
kaempferol content in foliage and pericarp was also recorded in the chickpea plants raised from
402
the microbial consortium treated seeds. These flavonoids are known to act as antioxidants and
403
also enhance the antioxidant properties in foods41 by inhibiting the activity of alternative
404
oxidases.42 In diet, these flavonoids reduce lipid peroxidation and permeability of K due to
405
dysfunction of membrane in erythrocytes.43
406
The harmful effect of free radicals present in food and biological system are well known.
407
Free radicals may destroy food quality by converting them into poisonous food. Increased
408
reducing power stabilizes and stops free radical chain reactions by formation of stable products.
409
High RP may also increase with intracellular antioxidants, peptides of organism used to start
410
fermentation and their hydrogen-donating ability.27 Hence, increased RP in chickpea plant parts
411
in this study may be correlated with increased antioxidant levels such as total phenols and
412
flavonoids in chickpea plants raised from consortium treated seeds.
ACS Paragon Plus Environment
Page 19 of 32
Journal of Agricultural and Food Chemistry
413
Increasing use of cereals in livestock diet makes a competitive dispute with human feed
414
and nutrition whereas use of soybean in place of cereals is, however, a costly affair. Further,
415
livestock population in India is growing to meet the basic requirement of growing human
416
population, and at the same time demand for fodder supply has also increased. Thus, additional
417
resource such as chickpea straw has been accepted as feed for livestock. Therefore, livestock
418
feed with sustainably enhanced nutritional quality through use of rhizosphere competent
419
microbes will contribute significantly to the health of the livestock. Thus, use of proven
420
microbial consortium will not only increase the nutritional quality of the forage and roughage for
421
the livestock in countries like India but also reduce the demand and supply ratio.44 Therefore, use
422
of chickpea straw (both pericarp and foliage) is considered as one of the best alternatives to
423
overcome this problem due to their high nutritional value and harmless effect on egg production,
424
meat and milk quality.45
425
The current study thus advocates use of microbial consortia of compatible rhizosphere
426
microbes to improve nutrient content in plants, which also enhances yield. We demonstrated that
427
a useful microbial consortium can increase the nutritive value such as antioxidants of edible parts
428
of crop plants whose consumption could be a safe and effective way to battle against oxidative
429
stress in human and livestock.
430 431
Acknowledgements
432
SKY is grateful to Indian Council of Medical Research, New Delhi for financial assistance
433
[Grant No. 3/1/3/JRF-2012/HRD-66(80689)]. BKS is grateful to Indian Council of Agricultural
434
Sciences, New Delhi for financial assistance (Grant No. ICAR-NBAIM/AMAAS/2014-15/73).
435
References:
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 20 of 32
436
(1) UNDESA. World population projected to reach 9.6 billion by 2050. URL
437
(http://www.un.org/en/development/desa/news/population/un-report-world-population-
438
projected-to-reach-9-6-billion-by-2050.html) (2013).
439
(2) Bhardwaj, D., Ansari, M.W., Sahoo, R.K., Tuteja, N. Biofertilizers function as key player
440
in sustainable agriculture by improving soil fertility, plant tolerance and crop productivity.
441
Microb. Cell Fact., 2014, 13, 66.
442 443 444 445
(3) Raja, N. Biopesticides and biofertilizers: ecofriendly sources for sustainable agriculture. J. Biofertil. Biopestici., 2013, 1000e112:1000e112. (4) Patel, J.S., Singh, A., Singh, H.B., Sarma, B.K. Plant genotype, microbial recruitment and nutritional security. Front. Plant Sci., 2015, 6, 608.
446
(5) Patel, J.S., Sarma, B.K., Singh, H.B., Upadhyay, R.S., Kharwar, R.N., Ahmed M.
447
Pseudomonas fluorescens and Trichoderma asperellum enhance expression of Gα subunits
448
of the pea heterotrimeric G-protein during Erysiphe pisi infection. Front. Plant Sci., 2016,
449
6, 1206.
450
(6) Araujo, A.S.F., Santos, V.B., Monteiro, R.T.R. Responses of soil microbial biomass and
451
activity for practices of organic and conventional farming systems in Piauistate, Brazil.
452
Eur. J. Soil Biol., 2008, 44, 225–230.
453
(7) Megali, L., Glauser, G., Rasmann, S. Fertilization with beneficial microorganisms
454
decreases tomato defenses against insect pests. Agron. Sustain. Dev., 2013, 34, 649-656.
455
(8) Sahoo, R.K., Ansari, M.W., Pradhan, M., Dangar, T.K., Mohanty, S., Tuteja, N.
456
Phenotypic and molecular characterization of efficient native Azospirillum strains from rice
457
fields for crop improvement. Protoplasma, 2014, 251, 511-523.
458
(9) Sinha, R.K., Valani, D., Chauhan, K., Agarwal, S. Embarking on a second green revolution
459
for sustainable agriculture by vermiculture biotechnology using earthworms: reviving the
460
dreams of Sir Charles Darwin. Int. J. Agric. Health Saf., 2014, 1, 50–64.
461 462 463 464
(10) Ibrikci, H., Knewtson, S.J.B., Grusak, M.A. Chickpea leaves as a vegetable green for humans: evaluation of mineral composition. J. Sci. Food Agric., 2003, 83, 945–950. (11) Bampidis, V.A., Christodoulou, V. Chickpeas (Cicer arietinum L.) in animal nutrition: A review. Anim. Feed Sci. Tech., 2011, 168, 1-20.
465
(12) Maheri-Sis, N., Aghajanzadeh-Golshani, A., Cheraghi, H., Ebrahimnezhad, Y.,
466
Ghalehkandi, J.G., Asaadi-Dizaji, A. 2011. Dry matter degradation kinetics and
ACS Paragon Plus Environment
Page 21 of 32
Journal of Agricultural and Food Chemistry
467
metabolizable energy of chickpea (Cicer arietinum) straw in ruminants. Res. J. Biol. Sci.,
468
6, 635-638.
469
(13) Sarma, B.K., Yadav, S.K., Singh, S., Singh, H.B. Microbial consortium mediated plant
470
defense against phytopathogens: readdressing for enhancing efficacy. Soil. Biol. Biochem.,
471
2015, 87, 25–33.
472
(14) Jain, A., Singh, S., Sarma, B.K., Singh, H.B. Microbial consortium mediated
473
reprogramming of defense network in pea to enhance tolerance against Sclerotinia
474
sclerotiorum. J. Appl. Microbiol., 2012, 112, 537–550.
475
(15) Mishra, S., Nautiyal, C.S. Reducing the allelopathic effect of Parthenium hysterophorus
476
L. on wheat (Triticum aestivum L.) by Pseudomonas putida. Plant Growth Regul. 2012, 66,
477
155-165.
478
(16) Saxena, A., Raghuwanshi, R., Singh, H.B. Trichoderma species mediated differential
479
tolerance against biotic stress of phytopathogens in Cicer arietinum L. J. Basic Microbiol
480
2015, 55, 195-206.
481
(17) Patel, J.S., Kharwar, R.N., Singh, H.B., Upadhyay, R.S., Sarma, B.K. Trichoderma
482
asperellum (T42) and Pseudomonas fluorescens (OKC)-enhances resistance of pea against
483
Erysiphe pisi through enhanced ROS generation and lignifications. Front. Microbiol. 2017,
484
8, 306
485
(18) Yadav, S.K., Dave, A., Sarkar, A. Singh, H.B., Sarma, B.K. Co-inoculated biopriming
486
with Trichoderma, Pseudomonas and Rhizobium improves crop growth in Cicer arietinum
487
and Phaseolus vulgaris. Int. J. Agric. Environ. Biotechnol., 2013, 6, 255-259.
488 489 490 491 492 493 494 495
(19) Stuart, D.L., Wills, R.B. Effect of drying temperature on alkylamide and cichoric acid concentrations of Echinacea purpurea. J. Agric. Food Chem. 2003, 51, 1608-1610. (20) Jackson, N.E. Soil Chemical Analysis. Prentice Hall, Inc., Englewood Cliffs, NJ, 1973, p. 498. (21) Kemi Idowu, M., Adote Aduayi, E. Sodium-potassium interaction on growth, yield and quality of tomato in ultisol. J. Plant Interact. 2007, 2, 263-271. (22) Nelson, D.W., Sommers, L.E. Determination of total nitrogen in plant material. Agron. J., 1973, 65, 109–112.
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 22 of 32
496
(23) Walkley, A., Black, I.A. An examination of the Degtjareff method for determining soil
497
organic matter, and a proposed modification of the chromic acid titration method. Soil Sci.,
498
1934, 37, 29-38.
499 500 501 502 503 504
(24) Zheng, Z., Shetty, K. Solid-state bioconversion of phenolics from cranberry pomace and role of Lentinus edodes β-glucosidase. J. Agric. Food Chem., 2000, 48, 895–900. (25) Lowry, O.H., Rosebrough, N.J., Farr, A.L., Randall, R.J. Protein measurement with the folin phenol reagent. J. Biol. Chem., 1951, 193, 265-275. (26) Hedge, J.E., Hofreiter, B.T., Whistler, R.L. Carbohydrate chemistry. Academic Press, New York (1962): 17.
505
(27) Jain, A., Singh, A., Chaudhary, A., Singh, S., Singh, H.B. Modulation of nutritional and
506
antioxidant potential of seeds and pericarp of pea pericarps treated with microbial
507
consortium. Food Res. Int., 2014, 64, 275–282.
508
(28) Irshad, Md., Zafarya, Md., Singh, M., Rizvi, M.M.A. Comparative analysis of the
509
antioxidant activity of Cassia fistula extracts. Int. J. Med. Chem. 2012, 2012 ID 157125.
510
(29) Singhal, M., Paul, A., Singh, H.P., Dubey, S.K., Gaur, K. Evaluation of reducing power
511
assay of chalcone semicarbazones. J. Chem. Pharm. Res., 2011, 3, 639-645.
512
(30) Singh, B.N., Singh, B.R., Singh, R.L., Prakash, D., Singh, D.P., Sarma, B.K., Upadhyay,
513
G., Singh, H.B. Polyphenolics from various extracts/fractions of red onion (Allium cepa)
514
peel with potent antioxidant and antimutagenic activities. Food Chem. Toxicol., 2009, 47,
515
1161-1167.
516
(31) Singh, A., Jain, A., Sarma, B.K., Upadhyay, R.S., Singh, H.B. Beneficial compatible
517
microbes enhance antioxidants in chickpea edible parts through synergistic interactions.
518
LWT-Food Sci. Technol. 2014, 56, 390-397.
519
(32) Ghorai, M., Mandal, S.C., Pal, M., Pal, S.P., Saha, B.P. A comparative study on
520
hypocholesterolaemic effect of allicin, whole germinated seeds of bengal gram and
521
guggulipid of gum gugglu. Phytother. Res., 2000, 14, 200-202.
522 523 524 525
(33) Mathur, K.S., Khan, M.A., Sharma, R.D. Hypocholesterolaemic effect of Bengal gram: a long-term study in man. Brit. Med. J., 1968, 1, 30-31. (34) Murty, C.M., Pittaway, J.K., Ball, M.J. Chickpea supplementation in an Australian diet affects food choice, satiety and bowel health. Appetite, 2010, 54, 282-288.
ACS Paragon Plus Environment
Page 23 of 32
526 527 528 529
Journal of Agricultural and Food Chemistry
(35) Maathuis, F.J.M. Physiological functions of mineral macronutrients. Curr. Opin. Plant Biol., 2009, 12, 250–258. (36) Krouk, G., Crawford, N.M., Coruzzi, G.M., Tsay, Y.F. Nitrate signaling: adaptation to fluctuating environments. Curr. Opin. Plant Biol., 2010, 13, 265-272.
530
(37) Chevalier, F., Rossignol, M. Proteomic analysis of Arabidopsis thaliana ecotypes with
531
contrasted root architecture in response to phosphate deficiency. J. Plant Physiol., 2011,
532
168, 1885-1890.
533
(38) Verma, J.P., Yadav, J., Tiwari, K.N., Kumar, A. Effect of indigenous Mesorhizobium
534
spp. and plant growth promoting rhizobacteria on yields and nutrients uptake of chickpea
535
(Cicer arietinum L.) under sustainable agriculture. Ecol. Eng., 2013, 51, 282-286.
536
(39) Halliwell, B., Rafter, J., Jenner, A. Health promotion by flavonoids, tocopherols,
537
tocotrienols, and other phenols: direct or indirect effects? Antioxidant or not? Am. J. Clin.
538
Nutr., 2005, 81, 268S-276S.
539
(40) Nautiyal, C.S., Govindarajan, R., Lavania, M., Pushpangadan, P. Novel mechanism of
540
modulating natural antioxidants in functional foods: Involvement of plant growth
541
promoting rhizobacteria NRRL B-30488. J. Agric. Food Chem., 2008, 56, 4474–4481.
542 543 544 545
(41) Shahidi, F., Wanasundara, P.K. Phenolic antioxidants. Crit. Rev. Food Sci. Nutr., 1992, 32, 67. (42) Shimoji, H., Yamasaki, H. Inhibitory effects of flavonoids on alternative respiration of plant mitochondria. Biol. Plantarum, 2005, 49, 117-119.
546
(43) Maridonneau-Parini, I., Braquet, P., Garay, R.P. Heterogenous effect of flavonoids on K+
547
loss and lipid peroxidation induced by oxygen-free radicals in human red cells. Pharm. Res.
548
Commun., 1986, 18, 61-73.
549 550
(44) Datta, D. Indian fodder management towards 2030: A case of vision or myopia. Int. J. Manage. Soc. Sci. Res., 2013, 2, 33-41.
551
(45) Vasta, V., Nudda, A., Cannas, A., Lanza, M., Priolo, A. Alternative feed resources and
552
their effects on the quality of meat and milk from small ruminants. Anim. Feed Sci. Tech.,
553
2008, 147, 223-246.
554 555 556
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 24 of 32
557
Figures legends:
558
Fig. 1. Shoot fresh weight (SFW), Root fresh weight (RFW), Shoot dry weight (SDW), Root dry
559
weight (RDW) and Total biomass (TB) in g (A) and Shoot length (SL), Root length (RL) in cm
560
(B) of different treatments was recorded after 60 days. Dry weight of the seeds, foliage and
561
pericarp of chickpea raised from treatment with Pseudomonas and Trichoderma either singly or
562
in combination after 120 days (C). Data are means of three replicates. Vertical bars indicate the
563
standard deviations of the means. Different letters indicate the significant differences among
564
treatments within the results taken at the same time interval according to Duncan's multiple
565
range test at p ≤ 0.05
566
Fig. 2. Phosphorus (A), nitrogen (B), potassium (C), sodium (D), calcium (E) and organic matter
567
(F) content in the seeds, foliage and pericarp of chickpea raised from treatment with
568
Pseudomonas and Trichoderma either singly or in combination. Data are means of three
569
replicates. Vertical bars indicate the standard deviations of the means. Different letters indicate
570
the significant differences among treatments within the results taken at the same time interval
571
according to Duncan's multiple range test at p ≤ 0.05.
572
Fig. 3. Total phenolics (A), Protein (B), carbohydrate (C) and total flavonoid (D) content in the
573
seeds, foliage and pericarp of chickpea raised from treatment with Pseudomonas and
574
Trichoderma either singly or in combination. Data are means of three replicates. Vertical bars
575
indicate the standard deviations of the means. Different letters indicate the significant differences
576
among treatments within the results taken at the same time interval according to Duncan's
577
multiple range test at p ≤ 0.05.
ACS Paragon Plus Environment
Page 25 of 32
Journal of Agricultural and Food Chemistry
578
Fig. 4. Reducing power in the seeds, foliage and pericarp of chickpea raised from treatment with
579
Pseudomonas and Trichoderma either singly or in combination. Data are means of three
580
replicates. Vertical bars indicate the standard deviations of the means. Different letters indicate
581
the significant differences among treatments within the results taken at the same time interval
582
according to Duncan's multiple range test at p ≤ 0.05
583
Fig. 5. PCA ordination plot showing grouping of twelve treatments (shown by arrow) against
584
various enhanced nutrient contents (shown by triangles). Abbreviation: pericarp of control plants
585
(Cp), pericarp of Pseudomonas fluorescens OKC treated plants (Op), pericarp of Trichoderma
586
asperellum T42 treated plants (Tp), pericarp of consortium treated plants (OTp), foliage of
587
control plants (Cf), foliage of Pseudomonas fluorescens OKC treated plants (Of), foliage of
588
Trichoderma asperellum T42 treated plants (Tf), foliage of consortium treated plants (OTf),
589
seeds of control plants (Cs), seeds of Pseudomonas fluorescens OKC treated plants (Os), seeds
590
of Trichoderma asperellum T42 treated plants (Ts), seeds of consortium treated plants (OTs).
591
Total phosphate (TP), Nitrogen (N), Organic matter (OM), Sodium (Na), Potassium (K),
592
Calcium (Ca), Total dry weight (DW), Total phenolic content (TPC), Protein content (PC),
593
Carbohydrate content (C), Total flavonoid content (TFC) and Reducing power (RP).
594 595 596 597 598 599
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 26 of 32
600
Table 1. Shikimic acid, phenolics and flavonoid contents in different parts of chickpea raised
601
from treatment with Pseudomonas and Trichoderma either singly or in combination†.
602
Pericarp (µg g−1) OKC T42 OKC + T42 Control a a b Shikimic acid 1767 ± 175.8 1640 ± 80.6 1564 ± 134 1508 ± 193b Gallic acid 52.2 ± 1.97a 43.2 ± 2.6ab 58.39 ± 10a 33.3 ± 13.8b a a a t-Chlorogenic acid 36.2 ± 0.07 35.44 ± 3.3 36.55 ± 1.3 34.32 ± 2a Ferulic acid 19.5 ± 1.21b 22.25 ± 1.5a 23.16± 4.1a 18.56 ± 1.8b bc b a Syringic acid 2.31 ± 1.11 3.09 ± 0.04 9.24 ± 0.2 1.03 ± 0.3c p-Coumaric acid 35.6 ± 1.91b 36.5 ± 2.6b 42.18 ± 2.6a 29.87 ± 2.1c a a a Quercetin 1.46 ± 0.07 1.94 ± 0.8 2.05± 0.1 1.40 ± 0.3a Kaempferol 17.94 ± 0.07a 12.09 ± 0.9b 18.94 ± 0.8a 11.56 ± 1.7b −1 Seed (µg g ) Shikimic acid 1740.7 ± 127.3b 1812.9 ± 219.5b 2045.4 ± 185.7a 1731.9 ± 301.7b Gallic acid 68.71 ± 2.8c 99.9 ± 14.1b 116.27 ± 4.8a 64.12 ± 9.2c t-Chlorogenic acid 35.46 ± 2.1b 30.49 ± 0.22c 46.26 ± 1.8a 29.74 ± 1.9c b c a Ferulic acid 17.91 ± 9.1 15.44 ± 6.18 23.59 ± 4.2 14.22 ± 7c Syringic acid 7.34 ± 0.2c 9.34 ± 0.8b 11.58 ± 0.02a 2.15 ± 0.72d bc bc a p-Coumaric acid 125.7 ± 3.6 127.02 ± 6.25 166.2 ± 51.3 119.71 ± 37c b b a 2.37 ± 0.48 4.78 ± 0.5 1.96 ± 1.5b Quercetin 2.5 ± 0.2 Kaempferol 10.76 ± 1.1a 7.04 ± 0.86b 10.88 ± 1.7a 6.87 ± 0.98b Foliage (µg g−1) b Shikimic acid 1385 ± 139.9 1752.5 ± 21.6a 1914.8 ± 9.4a 1363.1 ± 86.8b Gallic acid 98.1 ± 8.2b 103.67 ± 3.0a 109.62 ± 7.0a 94.01 ± 26b a b a 13.23 ± 0.6 55.62 ± 17.1 10.17 ± 1.7b Ferulic acid 43.12 ± 2.2 b b a Syringic acid 13.42 ± 1.1 13.19 ± 2.1 24.51 ± 1.8 11.51 ± 4b p-Coumaric acid 31.52 ± 3.4a 23.65 ± 3.3b 32.40 ± 14.3a 19.24 ± 1.4b b b a Quercetin 2.11 ± 0.2 2.81 ± 0.2 7.46 ± 1.4 1.62 ± 0.1b Kaempferol 103.41 ± 15.4c 131.19 ± 4.7b 151.25 ± 14.6a 97.84 ± 11.4d †Results are expressed as means of three replicates ± SD. Different superscript letters indicate
603
significant differences among treatments within the results taken at the same time interval
604
according to Duncan's multiple range test at p ≤ 0.05.
Phenolic acid
605
ACS Paragon Plus Environment
Page 27 of 32
Journal of Agricultural and Food Chemistry
Fig. 1
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
a
Page 28 of 32
A
B
a
a
c c a
a ab bc c
cc
a
bb
b
a
C
D ab bc
c a
b
a
c c c
a
a
E
a cc cc
F F
a c
d d
a
c
a
c c
Fig. 2
ACS Paragon Plus Environment
bc b
Page 29 of 32
Journal of Agricultural and Food Chemistry
a
10
dc Control
8
OKC
ab a ab b
T42 OKC+T42
4 2
c
ab b a
500
b aa
a
a
bb c
Control OKC
400
T42
300
OKC+T42
200 100 Pericarp
Foliage
a
90
a
a
bb
b cc
c
bb
c
60
Control
50
OKC
40
T42
30
OKC+T42
20 10 0 Pericarp
Seed
Seed
1.6
C Total Flavonoid Content (mg quercetin equivalents g−1 FW)
Seed
100 Carbohydrate (mg/g DW)
B
0 Pericarp
70
c
b
600
0
80
aa
700
b
12
6
800
A Protein (µg/g DW)
Total phenolic content (mM GAE/g of DW)
14
1.4
c bb
a c b bc
a
1.2
foliage
a babab
1
Control OKC
0.8
T42
0.6
OKC+T42 0.4 0.2 0
Foliage
D
Pericarp
Fig. 3
ACS Paragon Plus Environment
Seed
Foliage
Journal of Agricultural and Food Chemistry
Page 30 of 32
Reducing Power (% increase)
80 70
a
a
a
60 ab
50
b
40 30
b
b c
b
b c
bc
Control OKC T42 OKC+T42
20 10 0 Pericarp
Seed
Foliage
Fig. 4
ACS Paragon Plus Environment
Page 31 of 32
Journal of Agricultural and Food Chemistry
Fig. 5
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Priming chickpea seeds with Pseudomonas and Trichoderma consortium enhances nutritional quality of edible parts 122x75mm (300 x 300 DPI)
ACS Paragon Plus Environment
Page 32 of 32