Agricultural
Communication
Biosci. Biotech. Res. Comm. 9(3): 382-390 (2016)
Vermicompost and
Azotobacter
as an ecological
pathway to decrease chemical fertilizers in the
maize,
Zea mays
Ali Shirkhani
1
and Safar Nasrolahzadeh
2
1
Agricultural And Natural Resources Research And Education Centre, Kermanshah, Iran
2
Department of Eco-physiology, Faculty of Agriculture, University of Tabriz, Tabriz, Iran
ABSTRACT
Iran is a major importer of maize in the world. Maize is one of the most important crops in the western Iran. Maize
production in this region has two major problems: water shortage and low percentage of organic matter in soil. In
this research, effects of vermicompost and Azotobacter as a boifertilizers and chemical fertilizers levels on yield and
Some traits of leaves of Maize under normal and de cit irrigation was investigated in two years (2014 and 2015).
Results showed that grain yield, Leaf Area Index, leaf chlorophyll contents, the normalized difference vegetation
index (NDVI) and Leaf relative water content (RWC) were decreased by de cient irrigation. Use of Azotobacter and
vermicompost signi cantly increased these traits in normal and de cit irrigation. Results also showed that using 6
ton/ha of vermicompost and Azotobacter in soil, 50% of the corn fertilizer supplied. The results showed that combined
use of biofertilizers with chemical fertilizers increased the yield and other traits. Therefore the uses of biological fer-
tilizers signi cantly reduce the consumption of chemical fertilizers and reduce the adverse environmental effects. So
biofertilizers could be considered as a suitable substitute for chemical fertilizer in organic agricultural systems. On
the other hand from this experiment, application of vermicompost in combination with chemical fertilizers showed
better performance than only chemical fertilizers, even in 100% recommendation based on soil test treatments. As a
general conclusion these results suggest that integrating organic sources with 50% of recommended NPK fertilizers
are appropriate for sustainable crop production in normal and de cient irrigation.
KEY WORDS: MAIZE, VERMICOMPOST, AZOTOBACTER, CHEMICAL FERTILIZER, YIELD, LAI, NDVI, RWC
382
ARTICLE INFORMATION:
*Corresponding Author: Ali.shirkhani@gmail.com
Received 6
th
July, 2016
Accepted after revision 26
th
Aug, 2016
BBRC Print ISSN: 0974-6455
Online ISSN: 2321-4007
Thomson Reuters ISI ESC and Crossref Indexed Journal
NAAS Journal Score 2015: 3.48 Cosmos IF : 4.006
© A Society of Science and Nature Publication, 2016. All rights
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Online Contents Available at: http//www.bbrc.in/
Ali Shirkhani and Safar Nasrolahzadeh
INTRODUCTION
Maize (Zea mays L.) is a major food, feed and industrial
crop around the world. The crop provides food secu-
rity and income to several million small holder farm-
ers in Sub-Saharan Africa, Latin America and Asia.
The area, production and productivity of maize have
increased several-fold over the last  ve decades. In
2014, over 180 thousand hectares and 1.223 million tons
of maize produced in Iran. However Iran was imported
6000 (1000 MT) maize grain. Maize is one of the most
important crops in the western Iran and we have short-
age in producing animal feeds, so, maize production is
very important in Iran. The dearth of water is one of
the important factors for maize production. The water
shortage because of decreasing annual precipitation and
the dry climate, and the other hand low fertility and low
percentage of organic matter in soil are major problems
in maize production in Iran. For this reason, overuse of
chemical fertilizers in Iran is rising, leading to environ-
mental pollution and soil degradation.
Soil water de cit reduces yield of maize (Zea mays
L.) and other grain crops by three main mechanisms.
First, whole canopy absorption of incident PAR may be
reduced, either by drought induced limitation of leaf
area expansion, by temporary leaf wilting or rolling dur-
ing periods of severe stress, or by early leaf senescence.
Second, drought stress reduces the ef ciency with which
absorbed PAR is used by the crop to produce new dry
matter. Third, drought stress may limit grain yield of
maize by reducing the harvest index (Earl and Davis,
2003 and Paroda and et al., 2014).
As heavy feeder of nutrients, maize productivity is
largely dependent on nutrient management. Therefore, it
needs fertile soil to express its yield potential. Farmers use
chemical fertilizers to increase production to meet their
needs, but the excessive use of fertilizers leads to contami-
nation of soil and groundwater and reduce soil fertility.
Moreover, Heavy agricultural reliance on synthetic-chem-
ical fertilizers and pesticides is having serious impacts on
public health and the environment. It killed the bene cial
soil organisms & destroyed their natural fertility, impaired
the power of ‘biological resistance’ in crops making them
more susceptible to pests & diseases Runoff of soil and
nitrogen fertilizer from corn-belt corn production has con-
tributed to the anaerobic “dead zone” in the Gulf of Mexico.
The U.S. National Academy of Sciences (2003) reports
that excessive fertilizer use costs $2.5 billion from wasted
fertilizer inputs. Hence, there is a need to search for alter-
native strategies to improve soil health without causing
damage to environment as well as soil. Therefore, biofer-
tilizers are gaining importance as they are ecofriendly,
non hazardous and nontoxic products (Sharma et al.,
2007, Adhikary, 2012).
The new approaches to the use of organic amend-
ments in farming have proven to be effective means of
improving soil structure, enhancing soil fertility and
increasing crop yields. Vermicompost is an important
type of non chemical fertilizers. Bio-fertilize is a densely
populated preservative of one or more types of useful
terricolous microorganism, their metabolic phenomenon
are used to provide the nutrients needed by plants, con-
trol soil-borne diseases and maintain the stability of
soil structure. Vermicomposts are  nely divided, peat-
like materials with high porosity, aeration, drainage,
water-holding capacity, and microbial activity. Natural
humic acids (HA) of vermicompost can be an ecological
alternative to increase tolerance of plants to drought,
precisely because they have been shown to stimulate
protein synthesis in various plant organs and enzyme
synthesis and/or activity (Muscolo et al., 2007).
In addition application of biocompost to consumable
crop minimizes the use of chemical fertilizers improve
the quality of soil (Tripathi et al., 2007). The addition
of organic matter to the soil usually increases the water
holding capacity of the soil. This is because the addition
of organic matter increases the number of micropores
and macropores in the soil either by “gluing” soil par-
ticles together or by creating favourable living condi-
tions for soil organisms. Certain types of soil organic
matter can hold up to 20 times their weight in water.
The consequence of increased water in ltration com-
bined with a higher organic matter content is increased
soil storage of water (Reicosky, 2005 and Pandya et al.
2014).
Lately, a number of studies were carried out inves-
tigating the association of nitrogen- xing microor-
ganisms on the roots of non-leguminous plants, such
as maize (Cvijanovic et al. 2007). Associative nitrogen
xing bacteria are present in all soils in unequal num-
bers. Their numbers depend on physical and chemical
properties of the soil, the presence of oxygen, the pres-
ence and absence of Ca and P, trace elements content,
organic matter content, the presence of the antagonists
and toxic chemicals, and can also be affected by differ-
ent plant species. Associative nitrogen  xing bacteria
are most abundant in plant rhizosphere and within root
hairs zone (Malik et al. 2005).
The use of associative nitrogen- xing bacteria (Azo-
tobacter, Azospirillum, Derxia etc.) in the production of
wheat, corn, sugar beet, sun ower and some vegeta-
ble crops, show that depending on the strain there is
a possibility of replacing up to 60 kg N ha-1, and pos-
sibly even up to 150 kg N ha-1 of mineral fertilizer. As
heavy feeder of nutrients, maize productivity is largely
dependent on nutrient management. Therefore, it needs
fertile soil to express its yield potential. Ideal soils are
rarely found in nature.
BIOSCIENCE BIOTECHNOLOGY RESEARCH COMMUNICATIONS VERMICOMPOST AND AZOTOBACTER AS AN ECOLOGICAL PATHWAY 383
Nasrolahzadeh and Shirkhani
Organic manures not only supply the plant nutrients
(Duhan and Singh, 2002). To alleviate the problem, INM
is an option as it utilizes available organic and inorganic
nutrients to build ecologically sound and economically
viable farming system. Research has suggested that
integrated nutrient management strategies involving
chemical fertilizers and bio-fertilizers enhance the sus-
tainability of crop production. Integrated plant nutrient
managet (INM) is the combined use of mineral fertilizers
with organic resources such as cattle manures, crop resi-
dues, urban/rural wastes, composts, green manures and
biofertilizers (Kemal and Abera, 2015).
Integrated nutrient management (INM) is a judi-
cious application of fertilizers or manures from different
sources to a  eld in order to maintain the environmental
sustainability. Saini et al., (2004), reported that using of
50 percent of chemical fertilizers and farm yard manure
with inoculation of seeds by Rhizobium bacteria and
phosphor solubilizing bacteria, increased grain yield and
biomass of sorghum and chick pea. According to Akbari
et al., (2009), combination of bio and chemical fertilizers
increased grain yield, plant height, biological yield and
harvest index of sun ower.
Also it has ben shown that application of 50% N through
chemical fertilizer + 25% through biocompost + 25% N
through vermicompost signi cantly improved growth in
terms of plant height, dry matter accumulation per plant
and LAI over the treatment 100% N through chemical fer-
tilizer. Moreover, the use of bio stimulators in condition
of environmental stress can decrease effects of stress and
enhance soil water holding capacity, root growth and yield
(Li and Ni, 1996 and Santosh and et al. 2013).
Furthermore, the concept of leaf area index was  rst
introduced by Watson (1947) and de ned as the ratio
of leaf area to a given unit of land area (Jonckheere
et al., 2004). Leaf area index is the component of crop
growth analysis that accounts for the ability of the crop
to capture light energy and is critical to understand-
ing the function of many crop management practices.
Leaf area index can have importance in many areas of
agronomy and crop production through its in uence
on: light interception, crop growth weed control, crop-
weed competition, crop water use, and soil erosion.To
measure LAI, scientists generally have cut a number of
plants at the soil surface, separated leaves from the other
plant parts, and measured the area of individual leaves
to obtain the average leaf area per plant. The product of
leaf area per plant and the plant population gives the
LAI. Alternatively, LAI could be measured non-destruc-
tively with this procedure if area of individual leaves
was determined by some combination of leaf length and
width measurements.
The SunScan canopy analysis system (Delta-T Devices,
Cambridge, UK) was designed to measure the light levels
of photosynthetically active radiation (PAR), the inter-
ception of solar radiation and make estimates of LAI in
plant canopies. SunScan probe estimates LAI indirectly
from measurements of radiation above and below the
canopy, based on a theoretical relationship between leaf
area and canopy transmittance. Its optical sensor is the
light sensitive “wand” of one meter long, containing 64
photodiodes equally spaced along its length (Potter et
al., 1996). The SunScan canopy analysis system (Delta-T
Devices, Cambridge, UK), rely on the strong dependency
between canopy structure and gap fraction or size distri-
bution of the canopy (Jonckheere et al., 2004).
The chlorophyll meter (or SPAD meter) is a simple,
portable diagnostic tool that measures the greenness or
the relative chlorophyll concentration of leaves. Com-
pared with the traditional destructive methods, this
equipment might provide a substantial saving in time,
space and resources. The Minolta Soil Plant Analysis
Development (SPAD-502) chlorophyll meter is one tool
that enables researchers to determine chlorophyll con-
tent by measuring leaf greenness (Peterson et al., 1993).
The SPAD uses a silicon photodiode to derive the ratio
of transmittance through the leaf tissue at 650 nm com-
pared with transmittance at 940 nm, and a value is given
based on that ratio. SPAD measures relative chlorophyll
content in plant leaves. Because chlorophyll content is
closely related to N supply (Pandey et al., 2000), SPAD
is also used to diagnose corn N status and predict corn
grain yield potential (Vetsch and Randall, 2004).
Janos (2010) reported a close correlation between N
fertilization and SPAD readings. Increasing N applica-
tion increased N content and chlorophyll content in
corn (Rambo et al., 2010). Factors affecting SPAD values
include radiation differences between seasons, variety
and species differences, plant and soil nutrient status
(including N and other nutrients), and biotic and abiotic
stresses (Peterson et al., 1993).
The normalized difference vegetation index (NDVI) is
widely used at ground level and from low, high and sat-
ellite altitudes to measure vegetative greenness and can-
opy photosynthetic size. Optical sensors that measure
the re ectance from the corn canopy and then attempt
to use that information to manage the crop have been
available for more than a decade now. GreenSeeker (TM
Trimble) is one of the better known sensors.The Normal-
ized Difference Vegetative Index (NDVI) is a commonly
used measurement of crop health in agricultural applica-
tions. NDVI is calculated as:
NDVI= (NIR re ected – Red re ected) / (NIR re ected
+Red re ected), where Red and NIR stand for the spec-
tral re ectance measurements acquired in the red and
near-infrared regions, respectively. Healthier crop can-
opy will absorb more red and re ect more near infra-
red light, and consequently has a higher NDVI value.
384 IFIS IN CRITICAL CARE SETTING VERMICOMPOST AND AZOTOBACTER AS AN ECOLOGICAL PATHWAY
BIOSCIENCE BIOTECHNOLOGY RESEARCH COMMUNICATIONS VERMICOMPOST AND AZOTOBACTER AS AN ECOLOGICAL PATHWAY 385
Nasrolahzadeh and Shirkhani
Jones and Wechler (2007) has used a GreenSeeker sensor
(NTech Industries, Inc.) to measure NDVI and there was
strong correlation between NDVI and chlorophyll con-
tent per plant of spinach (R²=0.91). The NDVI has been
correlated to many variables such as crop nutrient de -
ciency,  nal yield in small grains, and long-term water
stress (Govaerts and Verhulst, 2010). NDVI was found to
be closely correlated with the Leaf Area Index (Leon et
al., 2003).This present research work was therefore con-
ducted to assess the potential of the recommended dose
of inorganic fertilizers and its 50% amount alone and in
combination with different doses of vermicompost and
Azotoabcter inoculum as biofertilizer in order to explore
the possibility of reducing the use of chemical fertiliz-
ersin maize under drought stress and normal condition.
MATERIAL AND METHODS
Field experiments were conducted for two years (2014 –
2015) at the agricultural research farm, Agricultural and
Natural Resources Research Centre in Kermanshah, Iran.
This farm is located at 34.08 N, 46.26 E, 1345 m altitude,
silty clay soil, pH=7.5-8, 450 mm precipitation Mediter-
ranean climate. In this research, effects of vermicompost
and Azotobacter as a boi- fertilizers and chemical fertiliz-
ers on yield and yield components of Maize under normal
and de cit irrigation was investigated in two sites. Sites
included normal irrigation and de cient irrigation (65%
optimum water requirement) and each site was conducted
as the factorial split plot in a randomized complete block
design with three replications and three factors. Treat-
ments included Azotobacter in the main plots (non-inoc-
ulation and inoculation), vermicompost (consuming 0, 2,
4 and 6 ton/ha) and chemical fertilizers included N,P,K in
tree levels (100% recommendation based on soil test, 50%
recommendation and no fertilizer) in the sub plots. The
Maize cultivar used was “KSC 704” (a grain Maize cultivar
that is commonly planted in the region).
Before planting 7g inoculation with 1g had 107 active
and live bacteria, were used inoculating seeds. Seeds
which must mix with Azotobacter soaked with sugar
water with concentration 2% and with ratio 2kg inocula-
tion 100kg seeds. Plot dimensions using in this study will
be 7m long by 3m wide, each plot will be consisted four
rows spacing at 0.75m. Vermicompost used in this study
has been produced by the activity of Eisenia foetida worm
produced from cattle manure. Phosphorus and potassium
fertilizers were mixed by soil before cultivation. A quarter
of urea fertilizer at planting, one-fourth of 6 to 8 leaf
stage, and the remaining fertilizer was applied prior to
owering, before planting all quantities of vermicompost
was mixed with soil to a depth of 30 cm. Maize is an
irrigated crop in Iran; therefore, it is not dependent on
the seasonal rainfall. Irrigations were carried out at 7 day
intervals. Water treatments (de cit and adequate irriga-
tion) were initiated during middle vegetative growth stage
(around V6). Beginning on these dates, water was applied
at weekly intervals based on the amount of evapotranspi-
ration for the previous week as determined by the on-site
weather station using a modi ed version of the Penman
FAO equation (O’Neill et al., 2004).
The adequate irrigation treatment received the
amount of water required to fully replace the previ-
ous week evapotranspiration while the de cit treat-
ment received 65 % this amount. This was continued
throughout the remainder of the growing season. Rela-
tive chlorophyll (SPAD) content was measured in corn
leaves with Minolta SPAD-520 meter (Konica Minolta
Sensing, Inc., Japan) at the V8 and R1 stages. At least
ten SPAD meter readings were collected either in the
upper most fully expanded corn leaves (V8 stage) or ear
leaves (R1 stage) from each plot and the average value
was recorded. Leaf Relative water content (RWC) was
calculated by using the following equation:
RWC (%) = [fresh weight- dry weight/ turgid weight – dry weight] × 100
Where FW, TW and DW are fresh weight (g), turgid weight
(g) and dry weight (g) respectively. For this purpose, a
fully expanded young leaf (ear leaf) was selected from
each treatment and replication at the mid-canopy posi-
tion before irrigation in  owering stage (four plants). Ten
leaf pieces (2 cm diameter) were cut from these leaves
and weighed immediately to record fresh weight (FW).
Turgid weight (TW) was determined by weighing the leaf
segments after 24 h of immersion in distilled water in a
sealed  ask at room temperature. Dry weight (DW) was
determined by weighing the leaf segments after 48 h at
70°C in oven (Efeoglu et al., 2009).
For measuring the Leaf area index, SunScan canopy
analysis system (Delta-T Devices Ltd., UK) was used. The
instrument is indirectly measuring leaf area index by
measuring the ratio of transmitted radiation through
canopy to incident radiation. Normalized difference
vegetation index (NDVI) is an estimate of biomass and
nitrogen content in many crops. The NDVI sensor used
in this research was a GreenSeeker Hand Held Data col-
lection and Mapping Unit (NTech Industries, Inc., Ukiah,
Cal.), according to the methodology of Verhulst and
Govaerts (2010). Each plot was harvested at maturity for
yield. The Maize ears located 6 m2 from each plot were
harvested by hand, then allowed drying at 80°C to a
constant weight and then seed yield was obtained.
RESULTS AND DISCUSSION
The LAI was signi cantly in uenced by de cient irriga-
tion; Results showed that LAI was decreased from 3.7 to
386 VERMICOMPOST AND AZOTOBACTER AS AN ECOLOGICAL PATHWAY BIOSCIENCE BIOTECHNOLOGY RESEARCH COMMUNICATIONS
Nasrolahzadeh and Shirkhani
2.1 by de cient irrigation. Corn yield is strongly depended
on LAI, LAD and leaves ef ciency for absorption of solar
radiation for photosynthesis process. For most plant spe-
cies, the shortage of nitrogen or water causes a reduction
in leaf area development, changes in leaf tissue compo-
sition, leaf cell structure and plant water content (Casa,
2003) and also in maize, drought reduces leaf area, leaf
chlorophyll contents, photosynthesis and ultimately low-
ers the grain yield (Athar & Ashraf, 2005).
Stone et al. (2001) reported that water de cit reduces
crop growth and morphological characteristics of maize
plant. In corn, reproductive growth after the silking and
owering stages is the critical period for yield, and chlo-
rophyll content and intact chloroplast structure are key
factors for accumulation of dry matter and high yields
(Yu et al., 2010).
Analysis of variance showed that Azotobacter
increased LAI about 0.1 in all treatments. But this
increase was not statistically signi cant. Moreove leaf
area index increased with increasing levels of chemi-
cal fertilizers and vermicompost. The maximum LAI 4.5
was recorded in the plots where 6 ton/ha vermicompost
and 100% chemical fertilizer were applied. But with no
vermicompost and 100% chemical fertilizer LAI was 4
and with use of 6 ton/ha vermicompost and Azotobacter
and 50% chemical fertilizer LAI also was 4, this result
showed that use of vermicompost and azotobacter that
means a 50% reduction in the consumption of chemical
fertilizers. Whereas without chemical fertilizer and with
use of 6 ton/ha vermicompost and Azotobacter, LAI was
3.6 and 1.9 in normal and De cient Irrigation condition
respectively (Table 1).
Using of different Levels of fertilizers had signi cant
effect on leaf area index of corn (Rasheeed et al., 2003).
Yadav et al (2002) revealed that application of incorpo-
ration chemical and biofertilizers increased the biologi-
cal yield, grain yield and LAI of blond plantago (Plan-
tago ovate). In other study, application of incorporation
chemical and bio-fertilizers on corn crop increased plant
height, LAI, dry matter production, leaf area duration
(LAD) and leaf area ratio compared with sole chemical
fertilizers (Eidi Zadeh et al., 2010).
Verma (2011) reported Organic source of nitrogen
application also in uenced the plant height, leaf area
index, dry matter production/plan recorded signi cantly
more with the addition of FYM followed by Azospiril-
lum and control, respectively. Manyuchi et al., (2013)
showed that applying of vermicompost enhance maize
leaves production more than 3 leaves per plant.
The results of this study showed that de cient irri-
gation decreased leaf chlorophyll contents from 40.6
to 37.7.On the other hand bio and chemical fertilizers
had a signi cant effect on leaf chlorophyll contents
(Table 2). Vermicompost and Azotobacter increased leaf
chlorophyll contents and also chemical fertilizers. The
maximum chlorophyll contents (46.6) were observed
from 6 ton/ha vermicompost + inoculation with Azo-
tobacter + 100% chemical fertilizer in normal irrigation
but with use of 6 ton/ha vermicompost and Azotobacter
and 50% chemical fertilizer chlorophyll contents was
45.2 and no signi cant different was observed. Also
without chemical fertilizer and with use of 6 ton/ha ver-
micompost and Azotobacter, This trait was 35.2 and 32.3
in normal and de cient irrigation condition respectively.
Table 1: Effects of chemical fertilizer and vermicompost on LAI
De cient Irrigation Normal Irrigation
Vermicompost (ton/ha)
Chemical Fertilizers
024 60246
No Fertilizer 1.7 1.8 1.9 1.9 2.5 3.2 3.5 3.6
50% Recommendation 1.9 1.9 2 2.3 3.4 3.6 3.6 4
100% Recommendation 2.4 2.5 2.6 2.6 4 4.2 4.4 4.5
Table 2: Effects of Chemical and bio fertilizer on leaf chlorophyll contents
De cient Irrigation Normal Irrigation
Vermicompost (ton/ha)
Chemical Fertilizers
02460246
No Fertilizer 26.9 27.1 28.9 32.4 34.8 35.3 35.4 36.3
50% Recommendation 35 37.1 38.2 44 37.6 38.3 40.3 44.7
100% Recommendation 45.6 45.6 45.7 45.7 46.5 47 47 47
BIOSCIENCE BIOTECHNOLOGY RESEARCH COMMUNICATIONS VERMICOMPOST AND AZOTOBACTER AS AN ECOLOGICAL PATHWAY 387
Nasrolahzadeh and Shirkhani
Ciganda et al (2008) had similar results and reported
that chlorophyll content is among the most important
crop biophysical characteristics. Chlorophyll can be
related to photosynthetic capacity, thus, productivity,
developmental stage, and canopy stresses, also Munne-
Bosch and Alegre (2000) reported the chlorophyll con-
tent was decreased with decreasing the irrigation water
and this decrease was correlated with relative water
content in leaves. Chlorophyll loss is a negative conse-
quence of water stress. In addition, the negative effect of
de cit irrigation was re ected in decreasing the chloro-
phyll content of rosemary leaves.
On the other hand, some authors found an opposite
trend since chlorophyll increased by de cit irrigation.
Khayatnezhad, (2011) reported that drought stress con-
dition increased the leaf chlorophyll content in wheat
genotypes. This is because the exact effect of de cit irri-
gation may vary according to the intensity of the water
stress imposed (Cameron, 1999). These results are similar
with the previous  ndings of Chamle et al. (2006).
Pandurang (2014) reported vermicompost increased
Chlorophyll contents in maize. Casa (2003) reported
that differences in leaf spectral re ectance, in particu-
lar those related to variations in the chlorophyll content
of the leaves, have been used as an indirect means to
assess nitrogen stress and Nitrogen availability typically
affects leaf pigment concentration (e.g. chlorophyll) with
a clear effect on leaf spectral re ectance. Studies show
that when maize plants were subjected to PEG induced
drought stress their chlorophyll a, b and total chloro-
phyll contents were signi cantly decreased due to leaf
senescence acceleration (Efeoglu et al., 2009).
Inoculation with Azotobacter and use of vermicom-
post signi cantly in uenced the NDVI. Two years mean
revealed that maximum NDVI (0.78) was recorded with
the application of recommended dose of chemical ferti-
lizer plus 6 ton/ha vermicompost and Azotobacter inocu-
lation and in normal irrigation, also with use of 6 ton/
ha vermicompost and Azotobacter and 50% chemical
fertilizer NDVI was 0.78 and no signi cant different was
observed. Minimum NDVI (0.61) was observed in de cient
Irrigation and without chemical and bio fertilizer. In both
irrigation treatments with increasing of chemical and bio
fertilizer 0.61 was increased (Table 3). On the other hand
de cient irrigation decreased leaf NDVI from 0.76 to 0.68.
The NDVI was developed to assess plant greenness
and The Chllorophyll in leaves is responsible for the
variability in greenness within a canopy. Data obtained
from greenseeker, can be used for estimate yield pre-
diction, biomass accumulation and growth rate, ground
cover and early vigor, senescence pattern estimates, and
for biotic and abiotic stress detection. NDVI technology
is also used for making decisions in precision agriculture
such as rate and timing of nitrogenous fertilizer applica-
tions (Pask et al., 2012). The NDVI has been correlated
to many variables such as crop nutrient de ciency and
long-term water stress and relationship between leaf N
and leaf chlorophyll has been demonstrated for maize
(Verhulst and Govaerts, 2010 A).
Results obtained in this experiment indicated that
RWC decreased from 80.4% to 66.9% by de cient irri-
gation. Moreover vermicompost and chemical fertilizers
had a signi cant effect on RWC (Table 4). Vermicom-
post and Azotobacter increased RWC, also by increasing
the amount of chemical fertilizer, RWC increased. The
maximum of RWC (81%) was recorded in the plots where
applied 6 ton/ha vermicompost and Azotobacter and
chemical fertilizer but there was no signi cant differ-
ence between 0, 50 and 100 percent of chemical fertiliz-
ers. The largest increased in Leaf relative water content
due to the use of vermicompost. Whereas without chem-
ical fertilizer and with use of 6 ton/ha vermicompost and
Azotobacter, RWC was 80.6% and 69.4% in normal and
De cient Irrigation condition respectively.
Jabasingh & Saravana Babu (2014) had similar results
and reported that the relative water content in leaves
of different maize cultivars decreased signi cantly and
with drought stress, the membrane permeability of the
leaf cell markedly increased. Also Higher RWC indicates
better growth and development, which in turn depends
on leaf area (Sivakumar, 2014).
The yield of maize was signi cantly in uenced by
de cient irrigation; Results showed that grain yield was
decreased from 8.2 ton/ha to 4.4 ton/ha by de cient
irrigation. Water de cit in maize is one of limiting fac-
tors of yield and at the time of pollination, drought may
Table 3: Effects of Chemical and bio fertilizer on NDVI
De cient Irrigation Normal Irrigation
Vermicompost (ton/ha)
Chemical Fertilizers
02460246
No Fertilizer 0.61 0.63 0.65 0.66 0.69 0.73 0.75 0.75
50% Recommendation 0.68 0.69 0.69 0.71 0.77 0.77 0.77 0.78
100% Recommendation 0.72 0.72 0.72 0.72 0.78 0.78 0.78 0.78
388 VERMICOMPOST AND AZOTOBACTER AS AN ECOLOGICAL PATHWAY BIOSCIENCE BIOTECHNOLOGY RESEARCH COMMUNICATIONS
Nasrolahzadeh and Shirkhani
have severe impact on yield. These results are consistent
with previous work; Dagdelen et al. (2006) reported that
water de ciency signi cantly affected maize yield and
the highest maize yield was obtained from the full irri-
gation treatments. Stone et al. (2001) reported that water
de cit reduces crop growth and morphological charac-
teristics of maize plant. Pandey et al. (2000) reported
that yield reduction (22.6 - 26.4%) was found with de -
cit irrigation and this was associated with decrease in
kernel number and weight.
Analysis of variance showed that Azotobacter increased
grain yield about 89 kg/ha in all treatments (Table 5). In
addition the use of vermicompost at 2, 4 and 6 ton/ha
consistently and signi cantly increased grain yield in
normal and de cit irrigation (Table 5). Although, applica-
tion of vermicompost led to increase in grain yield, the
highest grain yield was related to integrated treatments
6 ton/h vermicompost and 100% chemical fertilizers rec-
ommendation based on soil test. Results also indicated
that the use of 6 ton/ha vermicompost and Azotobacter in
soil, 50% of the maize fertilizer supplied.
The results showed that combined use of bio-ferti-
lizers with chemical fertilizers increased the grain yield.
Therefore the uses of biological fertilizers signi cantly
reduce the consumption of chemical fertilizers and
reduce the adverse environmental effects. On the other
hand from this experiment, application of vermicompost
in combination with chemical fertilizers showed better
performance than only chemical fertilizers, even in 100%
recommendation based on soil test treatments. It can be
stated that the increase in growth parameters of maize
are due to greater availability of nitrogen in full organic
and integrated treatments. In full chemical treatments
most of nitrogen would be leached from the soil pro le.
In addition, high porosity and water holding capacity of
vermicompost that helps in better aeration and drain-
age. Moreover use of 6 ton/ha vermicompost and Azo-
tobacter in treatments with no chemical fertilizers pro-
duced 7 and 4.4 ton/ha grain yield in normal and de cit
irrigation respectively. Application of organic manures
either alone or integrated with chemical amendments for
maize, performed better than all amendments tested in
laboratory trails studied by Mujeeb et al. (2010).
Recommendations of organic matter alone with syn-
thetic fertilizers could be helpful for enhancing stagnant
wheat grain yield which have been reported by Tahir et al.
(2011). Similarly Kemal and Abera (2015) reported applica-
tion of recommended dose of inorganic fertilizer along with
vermicompost at 6 ton/ha to maize not only enhanced pro-
ductivity of maize but also improved soil fertility in terms
of higher available N, P, K and organic carbon content over
the control and recommended N, P and K.
CONCLUSION
Results obtained in this experiment indicated that,
although the vermicompost and Azotobacter were not
Table 4: Effects of Chemical and bio fertilizer on RWC
De cient Irrigation Normal Irrigation
Vermicompost (ton/ha)
Chemical Fertilizers
02460246
No Fertilizer 61.3 64.4 65.3 69.4 79.7 80 80.6 80.6
50% Recommendation 62.8 65.3 65.3 69.8 80 80 80.6 80.7
100% Recommendation 62.8 66.7 66 70 80 80 80.8 81
Table 5: Effects of Chemical and bio fertilizer on yield
De cient Irrigation Normal Irrigation
Azotobacter Vermicompost (t/ha)
NPK Recommendation
02460246
non-inoculation No Fertilizer 2.6 3 3.7 4.1 4.3 5.1 5.7 6.8
inoculation No Fertilizer 2.8 3.1 3.9 4.4 4.4 5.4 5.9 7
non-inoculation 50% 3.9 4.6 4.7 5.1 7.2 7.9 8.4 10
inoculation 50% 4.3 4.8 4.9 5.3 7.4 8.1 8.5 10.4
non-inoculation 100% 4.8 5.2 5.2 5.4 10 10.2 10.2 10.5
inoculation 100% 4.7 5.3 5.4 5.5 10.2 10.3 10.3 10.6
BIOSCIENCE BIOTECHNOLOGY RESEARCH COMMUNICATIONS VERMICOMPOST AND AZOTOBACTER AS AN ECOLOGICAL PATHWAY 389
Nasrolahzadeh and Shirkhani
able to provide all the nutritional requirements for
maize, but the results showed that combined use of bio-
fertilizers with chemical fertilizers increased the evalu-
ated characters. Hence the use of biological fertilizers
also signi cantly reduce the consumption of chemical
fertilizers and reduce the adverse environmental effects
however, a good performance can be achieved in maize.
On the other hand, the results showed that under de -
cient irrigation vermicompost and Azotobacter increased
grain yield. As a general conclusion these results sug-
gest that integrating organic sources with 50% of rec-
ommended NPK fertilizers are appropriate for sustain-
able crop production in normal and de cient irrigation.
Similary Vanlawe et al (2002) reported that the conjunc-
tive application of organics with inorganic sources of
nutrients reduces the dependence on chemical inputs.
ACKNOWLEDGMENT
This work was supported by Agricultural and Natural
Resources Research And Education Centre, Kermanshah,
Iran
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