International Journal of Chemical Studies 2017; 5(2): 310-316
P-ISSN: 2349–8528
E-ISSN: 2321–4902
IJCS 2017; 5(2): 310-316
© 2017 JEZS
Received: 17-01-2017
Accepted: 18-02-2017
SS Tomar
Department of Agronomy, Sardar
Vallabhbhai Patel University of
Agriculture and Technology, Meerut,
Uttar Pradesh, India
Adesh Singh
Department of Agronomy, Sardar
Vallabhbhai Patel University of
Agriculture and Technology, Meerut,
Uttar Pradesh, India
Ashish Dwivedi
Department of Agronomy, Sardar
Vallabhbhai Patel University of
Agriculture and Technology, Meerut,
Uttar Pradesh, India
Rahul Sharma
Department of Agronomy, Sardar
Vallabhbhai Patel University of
Agriculture and Technology, Meerut,
Uttar Pradesh, India
RK Naresh
Department of Agronomy, Sardar
Vallabhbhai Patel University of
Agriculture and Technology, Meerut,
Uttar Pradesh, India
Effect of integrated nutrient management for
sustainable production system of maize (Zea mays
L.) in indo-gangetic plain zone of India
SS Tomar, Adesh Singh, Ashish Dwivedi, Rahul Sharma, RK Naresh,
Vineet Kumar, Saurabh Tyagi, Ankit Singh Yadav Siddhart N Rahul and
Brajendra Pratap Singh
Abstract
To get more yield farmers tend to use excessive chemical fertilizers, while current energy crisis
prevailing higher prices and lack of proper supply system of fertilizers and deterioration of soil health
calls for more efficient nutrient management using conjunctive use of organic manure, inorganic
fertilizers and biofertilizer to sustain yield levels and agro-eco-system. Therefore, a thrice replicated 2
year field trial was conducted during 2010 and 2011 by using F test. The results revealed that
combination of 100% NPK + 5 t FYM+ Azotobactor + PSB recoded higher mean growth attributes
viz.,plant height (201.25 cm), dry weight/plant (267.25 g), LAI at 60 DAS (4.2), yield attributing
component and yield viz., cob/plants (1.1), number of grain/cob (541.2) and test weight (245.05 g), grain
yield (53.15 q/ha), quality parameters viz., protein content (8.38%) and protein yield (445.4kg/ha), total
nutrients uptake and economics viz.,net return/ha (Rs 36073.5), B:C ratio (2.86), production efficiency
(59.1 kg/day/ha) and economic efficiency (400.8 Rs/day/ha), besides achieved maximum nitrogen used
efficiency as compared to rest of its counterparts Thus, study suggests that maize can be successfully
grown under Indo-Gangetic plain zone on 100% NPK + 5 t FYM+ Azotobactor + PSB and harvest
maximum productivity and profitability besides, improving used efficiency of nitrogen.
Keywords: INM, Indo-Gangetic Plain Zone, Maize, NiUE and Sustainable Production System
Vineet Kumar
Department of Agronomy, Sardar
Vallabhbhai Patel University of
Agriculture and Technology, Meerut,
Uttar Pradesh, India
Saurabh Tyagi
Department of Agronomy, Sardar
Vallabhbhai Patel University of
Agriculture and Technology, Meerut,
Uttar Pradesh, India
Ankit Singh Yadav
Department of Agriculture Extension
and Communication, Sardar Vallabhbhai
Patel University of Agriculture and
Technology, Meerut (U.P.) India
Brajendra Pratap Singh
Department of Agriculture Extension
and Communication, Sardar Vallabhbhai
Patel University of Agriculture and
Technology, Meerut (U.P.) India
Siddhart N Rahul
Department of Plant Pathology, Sardar
Vallabhbhai Patel University of
Agriculture and Technology, Meerut,
Uttar Pradesh, India
Correspondence
Ashish Dwivedi
Department of Agronomy, Sardar
Vallabhbhai Patel University of
Agriculture and Technology, Meerut,
Uttar Pradesh, India
1. Introduction
Utilization of indigenous sources of organics act as alternatives and/or supplements to
chemical fertilizers and even help in increasing the productivity of the maize (Seshaiah, 2000)
[17]
. Worldwide maize is the top ranking cereal crop in potential grain productivity. By 2020
AD, the requirement of maize will be around 100 mt for various sector, of which the poultry
sector alone demand 31 mt. It is a very difficult work for our researchers to increase the
production of maize from the present level of 34 to 100 Mt (Seshaiah, 2000) [17].
Since inception of Green Revolution there has been a race for increasing cereal production by
using synthetic chemical fertilizers in India. Over the years, India was able to increase food
grain production by 5 times at the cost of Remarkable 322 times increase in fertilizer
consumption staggering ‘net negative nutrient balance’ of 10 million tonnes has been reported
in India which is anticipated to reach 15 million tonnes upto 2025. Considering high cost of
fertilizers and their adverse implications on environmental due to their imbalanced use,
fertilizer recommendations based on soil test values, residual effect and yield targets become
highly important in India (Prasad, 2009) [15].
To get more yield farmers tend to use excessive chemical fertilizers, but decision on fertilizer
use requires knowledge of the expected crop yield response to nutrient application, which is a
function of crop nutrients need, supply of nutrients from soil as an indigenous source its
inherent capacity to supply nutrients and the short and long term fate of fertilizer applied
(Dobermann et al., 2003) [3].
The current energy crisis prevailing lack of proper supply system and higher prices of
fertilizers, distortion of soil fertility and deterioration of soil health calls for more efficient
nutrient management by using conjunctive use of organic manure and inorganic fertilizers to
sustain yield levels. An effective nutrient management is the one which involves site specific
nutrient recommendations to crops. This includes timely application of fertilizers using
appropriate methods and developing and practicing integrated plant nutrient supply system
~ 310 ~
International Journal of Chemical Studies
using chemical fertilizers, organic manures, crop residues and
biofertilizers and balanced fertilizer nutrient application
(Satish et al., 2011) [16]. The treatments receiving both
inorganic and organic fertilizers in Kharif season, followed by
only inorganic fertilizers during summer season has improved
the soil fertility, rice-maize grain and straw yield. The uptake
pattern also followed the yield of both the crops.
(Chandravanshi et al., 2014) [1]. Though, RDF alone can be
reduced up to 85% by supplying nutrients through organics.
(Manasa et al., 2015) [10]. Moreover, the values of all nitrogen
use efficiency (NiUE) in Western Uttar Pradesh were much
lower as compared to the global level. (Naresh et al., 2014)
[11]
. Therefore, the present study was planned to evaluate
performance, productivity and used efficiency of nitrogen as
influenced by integrated nutrient management in maize.
2. Matarials and method
Experimental details and site description
A field trial was carried out for two consecutive years during
kharif 2010 and 2011 at crop research centre of Sardar
Vallabhbhai Patel University of Agriculture and Technology,
Meerut (UP) satuated at a latitude of 29 o 40’ North and
longitude of 77o 42’ East with an elevation of 237 meters
above sea level. The mean maximum as well as minimum
temperature of 410 to 450 was recorded in the month of June
and minimum touches as low as 16.60 in October. The mean
annual rainfall during crop growing period was 807 mm (7583% of which is received during July to September) and
average relative humility varied between 67 to 85%
throughout the both the years. The experimental trial was well
drained, sandy loam in texture (46.2 % sand, 18.5 % silt and
17.3 % clay, hydrometer method) and slightly alkaline in
reaction (pH 7.87, Glass electrode pH meter). It was medium
in organic carbon available nitrogen and available
phosphorus, whereas high in available potassium (0.576 and
0.578 %, 0.98 and 1.01 %, 224.8 and 226.2 kg/ha, 16.9 and
17.3 kg/ha and 250.4 and 249.0 kg/ha first and second years,
respectively) with an electrical conductivity (1:2, soil: water
suspension, Solbridge conductivity meter method) and Bulk
density, Core sampler method of 1.61 dS/m and 1.41 Mg/m 3,
respectively. All the soil properties were analyzed as per the
standard procedures adopted by Jackson (1973) [6]. The
experiment was laid out in randomized block design with
three replication. The maize crop was grown as per agronomic
package of practice with a varieties of Kanchan with the
spacing (rows) of 50 cm. The seeds of crop were placed
manually in the furrows at a plant to plant distance of 20 cm
with a seed rate of 20 kg/ha and sown on 25 July during 2010
and 2011, while harvested on 23 October 2010 and 24
October 2011, respectively. The 100 per cent NPK is
characterized by 120 kg N, 60 kg P 2O5 and 40 kg K2O/ ha and
FYM is applied @ 5 t/ha as per the treatments whereas, PSB
is used as seed treatment @ 20 g/kg of seed. Two hand
weedings were performed manually with the help of Khurpi
for controlling weeds, first at 25 DAS and second at 45 DAS.
The maize is highly sensitive to water excess and stress,
therefore surface drains were opened just after sowing to
ensure proper drainage. Moreover, Only 1 irrigation was
applied at 60 DAS due to rains commensurate well with crop
water requirement at critical stages.
Data collection
Various growth parameters viz., plant height (cm) and dry
matter accumulation (g/plant) was recorded at maturity, leaf
area index was calculated at 60 DAS and yield attributes were
also measured at maturity stage. Grain yield was estimated by
the obtained produce from net plot area, treatment wise and
finally expressed at 14 % moisture from 15 m2, whereas
production and economic efficiency was calculated as per the
standard procedure used by Kumawat et al., (2012) [9].
Plant sampling and analysis
The total uptake of N, P and K was determined by plants
which were used for analyze the N, P and K content in plant.
The plant samples were dried at 70 °C in a hot air oven. The
dried samples were ground in a stainless steel Thomas Model
4 Wiley ® Mill. Further, the N content in plant was
determined by digesting the plant samples in H2SO4, followed
by analysis of total N by the Kjeldahl method (Page, 1982) [12]
using a Kjeltec™ 8000 auto analyzer (FOSS Company,
Denmark). Whereas, the P content in plant was resolute by the
vanadomolybdo-phosphoric yellow colour method and the K
content was determined in di-acid (HNO3 and HClO4) digests
by the flame photometeric method (Page, 1982) [12]. The
uptake of the nutrients (NPK) were calculated by multiplying
the nutrient content (%) by their respective yield (kg/ha -1) and
then divided by 100 to get the uptake in kg/ha-1. Finally the
sum of grain and stover calculate total uptake.
Nitrogen use efficiency
The effectiveness of applied nitrogen is to be establish by this
factor. The most important advantage of these index is that, it
quantifies total economic output from any particular nutrient/,
factor related to its utilization from all resources, including
nutrients from applied inputs and native soil nutrients
(Dobermann et al., 2002) [2]. The following expressions are
used for determining nitrogen used efficiency:
1 Agronomic efficiency of applied nitrogen (AEN)
AEN = kg grain yield increase per kg N applied (often used
synonym: N use efficiency:
AEN =Δ GY+N / FN
Where,
GY+N is the grain yield in a treatment with nitrogen
application in kg ha-1.
GY0N is the grain yield in a treatment without nitrogen
application, and FN is the amount of fertilizer nitrogen
applied, all in kg ha-1.
2 Recovery efficiency of applied nitrogen (REN)
REN = kg nitrogen taken up per kg nitrogen applied:
REN = UN+N – UN0N
Where,
UN+N is the total nitrogen uptake measured in above ground
biomass at physiological maturity (kg ha-1) in a plots that
received applied N at the rate of FN (kg ha-1).
UN0N is the total N uptake without N addition.
3 Partial factor productivity (PFPN)
PFPN = kg grain per kg nitrogen applied:
PFPN = GY+N / FN
Where,
GY+N is the grain yield in kg ha-1 and
FN is the amount of fertilizer nitrogen applied in kg ha-1.
~ 311 ~
International Journal of Chemical Studies
4 Physiological efficiency of applied nitrogen (PEN)
PEN = kg grain yield increase per kg fertilizer nitrogen taken
up:
PEN = (GY+N – GY0N) / (UN+N – UN0N)
Where,
GY+N is the grain yield in a treatment with
application in kg ha-1.
GY0N is the grain yield in a treatment without
application in kg ha-1.
UN+N are the total N uptake in a treatment with
application in kg ha-1.
UN0N is the total N uptake in a treatment without
application in kg ha-1.
nitrogen
nitrogen
nitrogen
nitrogen
Economic study
Benefit: cost ratio in terms of net return per rupee investment
was calculated by using the following formula:
B∶C=
Net return(Rs/ha)
Cost of cultivation(Rs/ha)
Statistical analysis
The data obtained were subjected to analyze statistically as
outlined by Gomez and Gomez (1984). The treatment
differences were tested by using “F” test and critical
differences (at 5 per cent probability).
3. Results and discussion
Growth attributes
Application of 100% NPK along with 5 t FYM+ Azotobactor
+ PSB produced significantly higher growth attributes viz.,
plant height (203.6 and 198.9 cm) and dry matter
accumulation (265.1 and 269.4 g) during 2010 and 2011,
respectively (Table 1). Although plant height remained
statistically on par with T2 to T6 and T9 during both the year,
while dry matter accumulation also clashes with all
treatments, except control during both the year. However, the
magnitude was higher in second year for dry matter
accumulation and first year for plant height. Moreover, lowest
growth attributes were measured in control plot during 2010
and 2011, respectively.The results so obtained in
performances probably due to nutrients were responsible for
increased cell division, cell enlargement, growth,
photosynthesis, and protein synthesis which are responsible
for quantitative increase in plant growth. The results of
present study are in agreement with the findings of several
other investigators (Panwar, 2008 and Manasa et al., 2015) [13,
10]
.
Kumari et al. (2012) [8, 9] also reported more leaf area due to
higher fertility and PSB inoculation.
Yield attributes
Treatments T3 to T6 and T10 recorded significantly similar and
maximum cob/plant (1.1), while remaining other treatment
also shown a similar values (1.0) including unfertilized plot
(Table 1). Furthermore, number of grain per cob and test
weight was seen higher under the treatments where FYM and
both biofertilizer had to be used, however number of grain per
cob remained on par to T 3 only, whereas test weight to T 3, T4
and T6 and significantly superior to rest of the level. Though,
lowest yield attributes were measured in control plot during
both the year.It might be due to better effect of inorganic and
organic sources on the adequate nutrients supply for longer
period, which will affects crop growth and photosynthetic
activity. Similar results were found by Sharma et al. (2013)
[18]
and Kokani et al. (2014) [7].
Yields
Yields were also varied significantly due to increment of
fertility level and reached to maximum in T10 (100% NPK + 5
t FYM+ Azotobactor + PSB) (Table 2). Maximum grain,
stover and biological yield were recorded under 100% NPK +
5 t FYM+ Azotobactor + PSB which were 52.7 and 53.6 q/ha
for grain, 75.6 and 73.6 q/ha for stover and 128.3 and 127.2
q/ha for biological yield, while stover yield were superior
over rest of its counterparts. Moreover, application of 100%
NPK + 5 t FYM were statistically on par to T 10 for grain and
biological yield during both the year, whereas, grain yield
were also remained statistically on par to T 6 and T9 and
superior over rest of the treatments, as above unfertilized plot
were also recorded lowest yield as compared to other
treatments. Similar results were obtained by Kokani et al.,
(2014) [7] and Kumar et al. (2015) observed that incorporation
of organic residues along with inorganic fertilizer
significantly increased uptake of N, P and K by plants which
facilitated the allocation and transfer of nutrient elements to
the grains and straw.
Harvest index
Data depicted in Figure 1 revealed that application of 100%
NPK + 5 t FYM+ Azotobactor + PSB recorded maximum
harvest index as compared to other treatments, while 75%
NPK recorded lowest harvest index but it was much higher
from unfertilized plot. More control recorded lowest harvest
index during both the year of experimentation. Similar results
were found by Sharma et al. (2013) [18].
Leaf area index
Significantly maximum leaf area index (4.2) average pool of
two year was noticed under 100% NPK + 5 t FYM+
Azotobactor + PSB which was superior to control during both
year and 75% NPK alone during previous year while
remained on par to all other treatments (Table 1). Application
of FYM and biofertilizer were not brought any changes in leaf
area index. Moreover, lowest leaf area index was measured in
control plot during both the year. The higher values of LAI
might be associated with increased availability of nitrogen
and phosphorus due to using Azotobactor and PSB and
having balanced nutrition which played an important role in
rapid cell division and elongation in meristmatic plant tissues.
~ 312 ~
Fig 1: Effect of different treatments on harvest index
International Journal of Chemical Studies
Nutrient Uptake
Significantly higher removal of NPK were noticed under
100% NPK + 5 t FYM+ Azotobactor + PSB which was
superior to rest of its counterparts, except P uptake in 100%
NPK + 5 t FYM. Although, the magnitudes of nutrient
removal were higher in 2011 as against 2010 (Table 2).
Moreover unfertilized plot removed least amount of Nitrogen
(46.8 and 47.1 kg/ha), phosphorus (13.1 and 13.6 kg/ha) and
potassium (71.1 and 71.6 kg/ha). Application of 75% NPK
along with other parts were also shown lowest removal of
NPK as against 100% NPK with either FYM or biofertilizer.
Higher uptake of N P and K was may be due to favorable
effect of incorporation of organic sources together with
inorganic nutrients which was earlier reported by Sharma et
al. (2013) [18]. Moreover, Decomposition of organic source is
accompanied by the release of appreciable amount of Co2
which dissolve in water to form carbonic acid being capable
of decomposition of certain primary minerals and release of
nutrients, besides favors higher biomass production and
nutrient uptake (Chandravanshi, 2014) [1]. Similar opinion was
also put forward by Kumar et al. (2015).
fertilizer (Naresh et al., 2014) [11]. For that, a computation of
values present in Figure 1 revealed that the combination of
organic, inorganic and biofertilizer (100% NPK + 5 t FYM+
Azotobactor + PSB) had got maximum average of two year
nitrogen use efficiency viz., agronomic efficiency (32.7
kg/ha), partial factor productivity (44.29), recovery efficiency
(72.5%) and physiological efficiency (37.6%). Moreover
lower efficiency were recorded under control plot. This
finding corroborates with the report by Naresh et al. (2014)
[11]
and Dwivedi et al. (2015) [4].
Quality attributes
Significantly maximum protein content (8.35 and 8.41%) and
protein yield (440.0 and 450.8 kg/ha) during 2010 and 2011,
respectively were recorded under the treatments of 100%
NPK + 5 t FYM+ Azotobactor + PSB (Table 3) which was
superior to rest of its counterparts for protein yields, while it
remained on par to protein content from T 3 to T6. Moreover
lowest protein content and protein yield were observed under
the plot where no fertilizer was used. This may be ascribed to
intense protein synthesis in plant and its efficient storage in
the presence of abundant supply of available nutrients through
biofertilizer and organics. The easy availability of nutrients
leads to balanced C:N ratio which enhanced the vegetative
growth of plant resulting in high photosynthetic activity.
Which finally out yielded better protein content in plant and
higher grain yield which in turn improved the protein yield.
The results of present investigation corroborate with the
findings of few previous studies (Pathak et al., 2002 and
Sharma et al., 2013) [14, 18].
Production economics
Computation of valued revealed that maximum net return
(35508 and 36639 Rs/ha), B:C ratio (2.83 and 2.89) during
2010 and 2011, respectively as against other of its treatments
were fetched under the treatments where 100% NPK + 5 t
FYM+ Azotobactor + PSB had applied (Table 3). This mainly
due to maximum yield produced under this level which
overcome the cost of FYM and biofertilizer and benefited
more. Furthermore, production efficiency (58.6 and 59.6
kg/day/ha) and economic efficiency (394.5 and 407.1
Rs/day/ha) was also observed maximum under 100% NPK +
5 t FYM+ Azotobactor + PSB. Although lower production
economics were recorded under control plots. These findings
lend support to the report of Shete et al. (2011) [19] and
Dwivedi et al. (2015) [4].
Nitrogen use efficiency (NIUE)
The values of all nitrogen use efficiency (NiUE) in India were
lower as against global (Figure 2 and 3). Moreover, values of
NIUE in the field experiment in western U. P. showed that, N
is much more efficiently utilized in world as compared with
western U. P. in India. Consequently, in western U. P., there
is a considerable scope for increase efficiency of nitrogenous
~ 313 ~
Fig 2: Effect of different treatments on agronomic efficiency and
physiological efficiency
Fig 3: Effect of different treatments on partial factor productivity
and recovery efficiency
International Journal of Chemical Studies
Table 1: Effect of different treatments on growth, LAI and yield attributes
Plant height (cm)
Treatments
T1
T2
T3
T4
T5
T6
T7
T8
T9
T10
Control
100% NPK
100% NPK + 5 t FYM
100% NPK + Azotobactor
100% NPK + PSB
100% NPK + Azotobactor + PSB
75% NPK
75% NPK + 5 t FYM
75% NPK + 5 t FYM+ Azo + PSB
100% NPK + 5 t FYM+ Azo + PSB
S.Em.±
C.D. (P=0.05)
2010
151.6
187.5
202.3
200.7
200.2
201.0
171.9
174.2
191.4
203.6
5.75
17.20
2011
146.3
182.7
196.8
193.1
195.7
194.5
174.6
178.3
186.4
198.9
5.25
15.65
Dry matter production
(g/plant)
2010
2011
234.8
238.8
248.0
254.6
256.9
261.8
253.6
259.5
252.0
258.3
255.4
259.4
242.5
248.8
245.3
251.2
249.9
254.9
265.1
269.4
8.5
9.3
25.7
28.1
Leaf area index at 60 DAS
2010
2.0
3.5
3.9
3.7
3.6
3.9
3.2
3.5
3.6
4.0
0.21
0.62
2011
2.3
3.8
4.3
3.9
3.9
4.2
3.6
3.9
4.2
4.4
0.29
0.88
Cob/plant
Number of grain/cob
2010 2011
1.0
1.0
1.0
1.0
1.1
1.1
1.1
1.1
1.1
1.1
1.1
1.1
1.0
1.0
1.0
1.0
1.0
1.0
1.1
1.1
0.009 0.008
0.027 0.024
2010
362.3
428.0
516.0
488.3
481.3
497.3
402.7
414.3
474.0
537.3
9.49
28.43
2011
368.8
435.9
521.4
495.2
487.6
504.6
410.6
421.5
483.9
545.1
10.2
30.7
Test weight
(g)
2010 2011
217.2 219.3
229.4 233.5
237.4 241.2
236.5 239.3
232.3 236.8
236.5 240.6
226.5 231.8
228.7 233.5
231.5 236.7
243.9 246.2
0.67 0.61
1.96 1.85
Table 2: Effect of different treatments on yields and uptake of nutrients
Treatments
T1
T2
T3
T4
T5
T6
T7
T8
T9
T10
Control
100% NPK
100% NPK + 5 t FYM
100% NPK + Azotobactor
100% NPK + PSB
100% NPK + Azotobactor + PSB
75% NPK
75% NPK + 5 t FYM
75% NPK + 5 t FYM+ Azo + PSB
100% NPK + 5 t FYM+ Azo + PSB
S.Em.±
C.D. (P=0.05)
Grain yield (q/ha)
Stover yield (q/ha)
Biological yield (q/ha)
2010
13.6
44.7
49.7
47.9
47.3
48.8
40.7
42.9
45.1
52.7
1.50
4.50
2010
44.5
67.3
71.7
70.1
69.1
70.8
65.2
66.7
67.4
75.6
0.97
2.91
2010
58.1
112.0
121.4
118.0
116.4
119.6
105.9
109.6
112.5
128.3
2.47
7.41
2011
14.2
45.8
50.6
49.1
48.3
49.7
42.1
44.6
45.9
53.6
1.30
4.10
2011
43.7
66.5
70.2
69.1
67.5
58.4
63.8
65.3
64.7
73.6
1.30
4.10
2011
57.9
112.3
120.8
118.2
115.8
108.1
105.9
109.9
110.6
127.2
2.6
8.2
N
2010
46.8
106.5
121.2
115.9
114.9
117.6
95.2
99.9
106.9
133.7
2.76
8.27
Nutrient uptake (kg/ha)
P
K
2011 2010 2011 2010 2011
47.1 13.1 13.6 71.1
71.6
107.3 25.1 25.5 109.8 110.4
121.6 28.8 29.3 117.1 117.9
116.7 26.9 27.3 114.3 114.8
115.5 26.9 27.4 112.0 113.6
118.4 27.9 28.2 115.7 116.2
96.0 22.0 22.1 95.6
96.1
101.2 23.3 23.4 101.7 102.3
107.4 25.5 25.6 111.2 111.6
134.3 32.2 32.4 128.7 129.4
2.81 1.26 1.25 3.51
3.57
8.44 3.76 3.75 10.53 10.71
Table 3: Effect of different treatments on quality and production economics
Treatments
T1
T2
T3
T4
T5
T6
Control
100% NPK
100% NPK + 5 t FYM
100% NPK + Azotobactor
100% NPK + PSB
100% NPK + Azotobactor + PSB
Quality attributes
Protein content (%) Protein yield (kg/ha) Net return (Rs/ha)
2010
2011
2010
2011
2010
2011
7.92
7.98
107.7
113.3
5549
6354
8.10
8.13
362.1
372.4
29543
30785
8.31
8.36
413.0
423.0
32913
34025
8.23
8.27
394.2
406.1
29311
30501
8.20
8.24
387.9
398.0
28757
29870
8.25
8.30
402.6
412.5
29790
31145
~ 314 ~
Production economics
B:C Ratio Production efficiency (kg/day/ha) Economic efficiency (Rs/day/ha)
2010 2011
2010
2011
2010
2011
0.68 0.72
15.1
15.8
61.7
70.6
2.60 0.65
49.7
50.9
328.3
342.1
2.65 2.72
55.2
56.2
365.7
378.1
2.56 2.61
53.2
54.6
325.7
338.9
2.51 2.57
52.6
53.7
319.5
331.9
2.59 2.66
54.2
55.2
331.0
346.1
International Journal of Chemical Studies
T7
75% NPK
T8
75% NPK + 5 t FYM
T9 75% NPK + 5 t FYM+ Azo + PSB
T10 100% NPK + 5 t FYM+ Azo + PSB
S.Em.±
C.D. (P=0.05)
8.05
8.08
8.16
8.35
0.05
0.15
8.08
8.10
8.20
8.41
0.06
0.18
327.6
346.6
368.0
440.0
0.8
2.3
340.2
361.3
376.4
450.8
0.8
2.5
26257
28098
29861
35508
-
27789
29634
30712
36639
-
~ 315 ~
2.56
2.49
2.62
2.83
-
2.62
2.57
2.66
2.89
-
45.2
47.7
50.1
58.6
1.7
5.0
46.8
49.6
51.0
59.6
1.4
4.6
291.7
312.2
331.8
394.5
-
308.8
329.3
341.2
407.1
-
International Journal of Chemical Studies
4. Conclusion
Based on two year field experimentation and with support of
the previous works, it could be inferred that performance,
productivity, profitability and used efficiency of nitrogen in
maize was improved by combination of organic, inorganic
and bioferilizer. Application of 100% NPK + 5 t FYM+
Azotobactor + PSB was found to be more effective for
improving performance, productivity, profitability and used
efficiency of nitrogen in maize than all over rest of the
treatments. Thus, study suggests that maize can be
successfully grown under semi-arid conditions of Western
Uttar Pradesh on 100% NPK + 5 t FYM+ Azotobactor + PSB
and harvest maximum productivity and profitability besides,
improving used efficiency of nitrogen.
5. References
1. Chandravanshi P, Chandrappa H, Hugar AY, Danaraddi
Vijay S, Kumar NBT, Pasha A. Effect of integrated
nutrient management on soil fertility and productivity for
sustainable production in rice-maize cropping system
under Bhadra command area of Karnataka Proceedings of
National Conference on Harmony with Nature in Context
of Environmental Issues and Challenges of the 21st
Century, Special issue, The Ecoscan, 2014; 6:385-390.
2. Doberman A, Witt C, Dawe D, Abdulrachman S, Gines
HC, Nagarajan R et al. Site- specific nutrient
management for intensive rice cropping systems in Asia.
Field Crops Researhc. 2002; 74:37-66.
3. Dobermann A, Witt C, Abdulrachman S, Gines HC,
Nagrajan R, Son TT et al. Soil fertility and indigenous
nutrient supply in irrigated rice domains of Asia. Agron.
J. 2003; 95:913-923.
4. Dwivedi Ashish, Singh A, Tomar SS, Kumar S, Dev I,
Kishore R, Singh P et al. Performance, Uptake and Use
Efficiency of Nutrients in Maize (Zea mays L.) and
Mashbean (Vigna mungo L.) alongwith Microbiological
Properties under Intercropping System in Alluvial Soil of
India J. Pure Appl. Microbio. 2015; 9(2):1233-1242.
5. Gomez KA, Gomez AA. Statistical procedure for
Agricultural Research An international Rice Research
Institute Book. John Willey and sons, 2nd edition. 1984,
329.
6. Jackson ML. Soil Chemical Analysis. Prentice Hall of
India Pvt. Ltd. New Delhi, 1973.
7. Kokani JM, Shah KA, Tandel BM, Nayaka P. Growth,
yield attributes and yield of summer blackgram (Vigna
mungo l.) as influenced by FYM, phosphorus and
sulphur. Proceedings of National Conference on
Harmony with Nature in Context of Environmental Issues
and Challenges of the 21st Century, Special issue, The
Ecoscan, 2014; VI:429-433.
8. Kumari A, Singh ON, Kumar R. Effect of integrated
nutrient management on growth, seed yield and
economics of garden pea (Pisum sativum L.) and soil
fertility changes. J. Food Legumes. 2012; 25(2):121-124.
9. Kumawat N, Singh RP, Kumar R, Kumari A, Kumar P.
Response of intercropping and integrated nutrition on
production potential and profitability on rainfed
pigeonpea. J. Agril. Sci. 2012; 4(7):154-162.
10. Manasa V, Hebsur NS, Malligawad LH, Shiva Kumar L,
Ramakrishna B. Effect of water soluble fertilizers on
uptake of major and micro nutrients by groundnut and
post-harvest nutrient status in a vertisol of northern
transition zone of Karnataka. The Ecoscan. 2015; 9(12):01-05.
11. Naresh RK, Tomar SS, Kumar D, Samsher Purushottam,
Singh SP, Dwivedi Ashish et al. Experiences with Rice
Grown on Permanent Raised Beds: Effect of Crop
Establishment Techniques on Water Use, Productivity,
Profitability and Soil Physical Properties. Rice Sci. 2014;
21(3):170-180.
12. Page AL. Methods of Soil Analysis: Part 2. Chemical and
Microbiological Properties. American Society of
Agronomy, Soil Science Society of America, Madison,
WI, USA, 1982.
13. Panwar AS. Effect of integrated nutrient management in
maize (Zea mays) - mustard (Brassica campestris var.
toria) cropping system in mid hills altitude. Indian J.
Agricultural Sciences. 2008; 78(1):27-31.
14. Pathak SK, Singh SB, Singh SN. Effect of integrated
nutrient management on growth, yield and economic in
maize (Zeamays)-wheat (Triticum aestivum) cropping
system. Ind. J. Agron. 2002; 47:325-332.
15. Prasad R. Efficient fertilizer use: the key to food security
and better environment. J. Trop Agric, 2009; 47:(1)7-26.
16. Satish A, Govind Gowda V, Chandrappa H, Nagaraja K.
Long term effect of integrated use of organic and
inorganic fertilizers on productivity, soil fertility and
uptake of nutrients in rice and maize cropping system.
Int. J. Sci. Nat. 2011; 2:84-88.
17. Seshaiah MP. Sorghum grain in poultry feed. In: Proc.
Intl.
Consultation,
Chandrasekaran,
A.
R.
Bundyopadhyay and H.I. Hall (Eds.). ICRISAT, Andhra
Pradesh, India, 2000; 18-19:240-241.
18. Sharma GD, Thakur R, Som R, Kauraw DL, Kulhare PS.
Impact of intergated nutrient management on yield,
nutrient uptake, protein conttent of wheat (Triticum
astivum) and soil fertility in a typic Haplustert. The
Bioscan. 2013; 8(4):1159-1164.
19. Shete PG, Thanki JD, Baviskar VS, Bhoye KP. Yield,
nutrient uptake and economics of greengram as
influenced by land configuration, inorganic fertilizers and
FYM levels. Green Farming. 2011; 2(4):425-427.
~ 316 ~