STUDIES ON THE EFFECT OF PGR (HUMIC ACID) AND COWDUNG
WITH CHEMICAL FERTILIZERS ON THE GROWTH, YIELD AND
CHEMICAL COMPOSITION OF T. AMAN RICE (cv. BRRI DHAN39)
A THESIS
BY
A. B. M. Rezaur Rahman
Examination Roll No. : 09 Ag. Chem. JD 41M
Semester: July-December, 2011
Registration No. 31124
Session: 2004-2005
MASTER OF SCIENCE (MS)
IN
AGRICULTURAL CHEMISTRY
DEPARTMENT OF AGRICULTURAL CHEMISTRY
BANGLADESH AGRICULTURAL UNIVERSITY
MYMENSINGH-2202
NOVEMBER 2011
STUDIES ON THE EFFECT OF PGR (HUMIC ACID) AND COWDUNG
WITH CHEMICAL FERTILIZERS ON THE GROWTH, YIELD AND
CHEMICAL COMPOSITION OF T. AMAN (cv. BRRI DHAN39)
A THESIS
BY
A. B. M. Rezaur Rahman
Examination Roll No. : 09 Ag.Chem. JD 41M
Semester: July-December, 2011
Registration No. 31124
Session: 2004-2005
Submitted to the Department of Agricultural Chemistry
Bangladesh Agricultural University, Mymensingh
in partial fulfillment of the requirements for the degree of
MASTER OF SCIENCE (MS)
IN
AGRICULTURAL CHEMISTRY
DEPARTMENT OF AGRICULTURAL CHEMISTRY
BANGLADESH AGRICULTURAL UNIVERSITY
MYMENSINGH-2202
November 2011
STUDIES ON THE EFFECT OF PGR (HUMIC ACID) AND COWDUNG
WITH CHEMICAL FERTILIZERS ON THE GROWTH, YIELD AND
CHEMICAL COMPOSITION OF T. AMAN (BRRI DHAN39)
A THESIS
BY
A. B. M. Rezaur Rahman
Examination Roll No. : 09 Ag. Chem. JD.41M
Semester: July-December, 2011
Registration No. 31124
Session: 2004-2005
Approved as to style and contents by:
(Professor Dr. Md. Abul Khair Chowdhury)
Supervisor
(Dr. Md. Zakir Hossen)
Co- Supervisor
(Dr. Md. Zakir Hossen)
Chairman
Examination Committee
&
Head, Department of Agricultural Chemistry
Bangladesh Agricultural University
Mymensingh
November 2011
ACKNOWLEDGEMENT
At first, the author would like to express his gratefulness to the “Almighty Allah” who
kindly enabled him to complete the research work for the degree of Master of Science
(MS) in Agricultural Chemistry.
The author would like to take the opportunity to express his immense indebtedness and
deepest sense of gratitude to his venerable supervisor, Professor Dr. Md. Abul Khair
Chowdhury, Department of Agricultural Chemistry, Bangladesh Agricultural
University (BAU), Mymensingh, for his scholastic guidance, innovative suggestions,
constant supervision, timely instructions and inspirations throughout the tenure of the
research work. His insight and professional skill have made distinct contribution to
complete this research work and to prepare this manuscript.
It is great pleasure for the author to express sincere appreciation and heartfelt thanks
to honorable co-supervisor, Dr. Md. Zakir Hossen , Associate Professor and Head,
Department of Agricultural Chemistry, Bangladesh Agricultural University (BAU),
Mymensingh for his valuable advice, constructive criticism and factual comments in
upgrading the quality of the research work and in the preparation of this manuscript.
The author acknowledges the contribution of all the teachers of the Department of
Agricultural Chemistry, BAU, especially Professor Dr. Nur Mohammad Talukder,
Professor Dr. M. Wahid-U-Zzaman, Professor Dr. Md. Akhter Hossain Chowdhury,
Professor Dr. Md. Mokhlesur Rahman for their endless encouragement, deep feelings
and for improving his knowledge and academic skills in Agricultural Chemistry during
the period of M.S. studies.
The author thanks to his friends especially Nazrul, Babu, Atik and Rajib for their
cordial inspiration and co-operation during the preparation of the manuscript.
The author expresses thanks to all the official and laboratory staffs of the Department
of Agricultural Chemistry, Bangladesh Agricultural University (BAU), and special
thanks to Mr. Mina for their co-operation during data collection.
Special thanks are due to Managing Director, Global Agrovat Company Limited
for his co-operation by supplying PGR (humic acid) required for the research work and
also the research expenses
Last but not the least the author expresses his deepest sense of respect to his beloved
mother, brother and specially father late Muqsadur Rahman for their blessings,
inspiration, advice and moral supports in all phases of his higher studies.
The Author
ABSTRACT
An experiment was conducted at the Bangladesh Agricultural University Farm,
Mymensingh during the aman season of 2010 to study the effect of humic acid (HA)
and cowdung (CD) with chemical fertilizers (N, P, K & S) on the growth, yield and
chemical composition of T. aman rice (cv. BRRI dhan39). The experiment was laid out
in randomized complete block design with three replications. There were nine (9)
treatments comprising of three levels of PGR (humic acid @ 0, 3 and 6 L ha-1
) and
cowdung @ 0, 5, and 10 t ha-1
and recommended doses of chemical fertilizers (N, P, K
& S). The application of different levels of cowdung with chemical fertilizers
significantly increased plant height, effective tillers hill-1
, panicle length, no. of grain
panicle-1
, 1000-grain weight, grain and straw yields of rice (cv. BRRI dhan39). The
highest yields of grain (4.23 t ha-1
) and straw (10.9 t ha-1
) were recorded in T4 where
combined doses of humic acid (3 L ha-1
) and cowdung (5 t ha-1
) were used along with
recommended doses of chemical fertilizers. Significant positive effect on contents and
uptakes of nitrogen, phosphorus, potassium, sulphur, calcium, magnesium, boron and
sodium in grain and straw of rice (cv. BRRI dhan39) were recorded in T4 treatment.
The study clearly indicated the prospect of PGR (humic acid) combined with
recommended doses of chemical fertilizers in rice cultivation in Bangladesh. Humic
acid may be the alternative replacement of organic manure like cowdung during acute
shortage for successful rice production.
CONTENTS
CHAPTER TITLE PAGE
ACKNOWLEDGEMENT i
ABSTRACT ii
LIST OF CONTENTS iii
LIST OF TABLES vi
LIST OF FIGURES vii
LIST OF APPENDICES viii
1. INTRODUCTION 1-3
2. REVIEW OF LITERATURE 4-11
2.1 Effect of humic acid 4-7
2.2 Effect of cowdung 7-11
3. MATERIALS AND METHODS 12-21
3.1 Experimental site and soils 12-13
3.2 Weather and Climatic condition 14
3.3 Test crop 15
3.4 Treatments 15
3.5 Collection of cowdung and humic acid 16
3.6 Land preparation 16
3.7 Layout of the experiment 17-18
3.8 Seedling transplanting 18
3.9 Intercultural operations 18
3.9.1 Gap filling 18
3.9.2 Irrigation and drainage 18
3.9.3 Weeding 18
3.10 General observations of the experimental
field
18
3.11 Plant sampling 18
3.12 Harvesting, threshing, cleaning and
processing
19
3.13 Data collection of crop characters 19
3.14 Procedure of recording data 19-21
CONTENTS (Contd.)
3.14.1 Plant height 20
3.14.2 Panicle length (cm) 20
3.14.3 Number of total tillers hill-1 20
3.14.4 Number of effective tillers hill-1 20
3.14.5 Number of total grains panicle-1
20
3.14.6 Number of filled grains panicle-1
20
3.14.7 1000-grain weight 20
3.14.8 Grain yield 20
3.14.9 Straw yield 21
3.14.10 Biological yield 21
3.14.11 Harvest index (%) 21
3.15 Collection and preparation of soil and plant
samples
21
3.15.1 Pre-planting and post-harvest soil
samples
21
3.15.2 Processing of plant samples 21
3.16 Physical and chemical analysis of initial soil 22-23
3.16.1 Particle size analysis 22
3.16.2 Soil pH 22
3.16.3 Determination of organic matter 22
3.16.4 Determination of total nitrogen 22
3.16.5 Determination of available
phosphorus
23
3.16.6 Determination of exchangeable
potassium
23
3.16.7 Cation exchange capacity 23
3.17 Chemical analysis of grain and straw 23-25
3.17.1 Preparation of sample 23
3.17.2 Digestion of samples 23
3.17.3 Determination of nitrogen 24
3.17.4 Determination of phosphorus 24
CONTENTS (Contd.)
3.17.5 Determination of potassium 24
3.17.6 Determination of sulphur 24
3.17.7 Determination of calcium 24
3.17.8 Determination of magnesium 24
3.17.9 Determination of boron 24
3.17.10 Determination of sodium 24
3.18 Nutrient uptake 25
3.19 Statistical analysis 25
4. RESULTS AND DISCUSSION
26-51
4.1 Effect of PGR (humic acid) and cowdung with
chemical fertilizers (N, P, K & S) on the growth,
yield and chemical composition of T. aman
(BRRI dhan39) 26
4.1.1 Plant height (cm) 26
4.1.2 Panicle length
27
4.1.3 Total tillers hill-1
27
4.1.4 Effective tillers hill-1
28
4.1.5 Total number of grains panicle-1
28
4.1.6 Number of filled grains panicle-1
29
4.1.7 1000-grain weight 29
4.1.8 Grain yield 30
4.1.9 Straw yields 30
4.1.10 Biological Yield 31
4.1.11 Harvest index (%) 31
4.2 Nutrient content of grain and straw
4.2.1 Nitrogen content 35
4.2.2 Phosphorus content 35
4.2.3 Potassium content 36
4.2.4 Sulphur content 37
4.2.5 Calcium content 37
4.2.6 Magnesium content 38
4.2.7 Boron content 38
4.2.8 Sodium content 39
4.3 Nutrient uptake by grain and straw
4.3.1 Nitrogen uptake 43
4.3.2 Phosphorus uptake 43
4.3.3 Potassium uptake 44
CONTENTS (Contd.)
4.3.4 Sulphur uptake 45
4.3.5 Calcium uptake 45
4.3.6 Magnesium uptake 46
4.3.7 Boron uptake 47
4.3.8 Sodium uptake
47
5. SUMMARY AND CONCLUSION 52-53
REFERENCES 54-57
APPENDICES 58-63
LIST OF TABLES
Table TITLE Page
3.1 Morphological characteristics of the soil
13
3.2 Physical properties of the initial soil sample
13
3.3 Chemical properties of the initial soil sample
14
4.1 Effect of PGR (humic acid) on the yield attributes of T.
aman cv. BRRI dhan39
32
4.2 Effect of cowdung on the yield attributes of T. aman cv.
BRRI dhan39
33
4.3 Interaction effects of PGR (humic acid) and cowdung
on the yield attributes of T. aman cv. BRRI dhan39
34
4.4 Effect of PGR (humic acid) on the N, P, K, S, Ca, Mg, B
and Na contents of T. aman rice cv. BRRI dhan39
40
4.5 Effect of cowdung on the N, P, K, S, Ca, Mg, B and Na
contents of T. aman rice cv. BRRI dhan39
41
4.6 Interaction effect of different doses of PGR (humic
acid) and cowdung on the N, P, K, S, Ca, Mg, B and Na
contents of T. aman rice cv. BRRI dhan39
42
4.7 Effect of PGR (humic acid) on the N, P, K, S, Ca, Mg, B
and Na uptake of T. aman rice cv. BRRI dhan39
49
4.8 Effect of cowdung on the N, P, K, S, Ca, Mg, B and Na
uptake of T. aman rice cv. BRRI dhan39
50
4.9 Interaction effect of different doses of PGR (humic
acid) and cowdung on the N, P, K, S, Ca, Mg, B and Na
uptake of T. aman rice cv. BRRI dhan39
51
LIST OF FIGURES
No. Name of Figure Page No.
3.1 Layout of the experimental plots 17
APPENDICES
No. TITLE Page
No.
1. Meteorological data of the experiment period (August to
December, 2004) at BAU Farm, Mymensingh
58
2. Analysis of variance data on effect of PGR (humic acid) and
cowdung on the growth, yield and yield contributing characters
of BRRI dhan39
59
3. Analysis of variance data on effect of PGR (humic acid) and
cowdung on nutrient content in grain of BRRI dhan39
60
4. Analysis of variance data on effect of PGR (humic acid) and
cowdung on nutrient content in straw of BRRI dhan39
61
5. Analysis of variance data on effect of PGR (humic acid) and
cowdung on nutrient uptake in grain of BRRI dhan39
62
6. Analysis of variance data on effect of PGR (humic acid) and
cowdung on nutrient uptake in straw of BRRI dhan39
63
CHAPTER 1
INTRODUCTION
Rice is one of the agronomically nutritionally important cereal crops which are the
staple food of more than 50% of the world’s population. It is the second agricultural
crop plant in the world (FAO, 2007). In Asia rice supplies 30-80% of the daily calories
consumed. Continuous use of chemical fertilizers accelerated the depletion of soil
organic matter and impairs physical and chemical properties of soil in addition to
causing micronutrient deficiencies.
Soil organic matter (OM) plays an important role in maintaining soil fertility and
productivity. OM acts as a reservoir of plant nutrients especially N, P, K, S and
micronutrients and also prevents leaching of the nutrients, which are vital to plant
growth. The use of organic manure and its proper management may reduce the need for
chemical fertilizers thus allowing the small farmers to save in part the cost of
production. In addition to being a good source of plant nutrients, organic manure
improve the physical, chemical and biological properties of soils and thus helps
increase and conserve the soil productivity.
Several reports showed that mobilization of N, P and K from the soil into the root
system is increased in presence of humus substances. The application of humic acid to
soil is also known to decrease phosphorus fixation in soil, particularly in calcareous
soil. Humic acids are known to increase the activity of glutamic acid transaminase and
phosphorylase enzymes and also the synthesis of deoxyribose and ribose nucleic acids.
Humic acid is technically not a fertilizer, although people consider it that humic acid is
an effective agent to use as a complement to synthetic or organic fertilizers. In many
instances, regular humic acid use will reduce the need for fertilization due to the soil's
and plant's ability to make better use of it. In some occurrences, fertilization can be
eliminated entirely if sufficient organic material is present and the soil can become self
sustaining through microbial processes and humus production.
The different humic acids had significant effect on nitrogen and phosphorus uptake by
oats. The efficiency indices of various humic acids ranged between 25 and 65 per cent
(Mishra and Srivastava, 1988). The humate migrated from one part of the root system
into another, contributing to a more intensive absorption of iron (Aso and Sakai, 1963).
Raina and Goswami (1988) reported a significant increase in the uptake of N, P, Cu, Zn
and Fe up to 20-ppm carbon as humic acid over control. Saalbach (1956) stated that
humic acid enhanced the uptake and content of nitrogen in rye. Jelanic et al. (1966)
reported that HA from lignite increased the P content and uptake in maize plants.
Application of 10kg HA ha-1
as potassium humate along with 75 per cent recommended
dose of fertilizer found to increase the crude protein content and mineral nutrition (P, K,
Ca, Mg, Zn, Cu, Fe and Mn) of Amaranthus (Bama and Selvakumari, 2001).
Govindasamy and Chandrasekaran (2002) reported that addition of humic acid was
found to increase the content and enhance the uptake of N, P, K, Ca, Mg, Fe, Mn and
Zn by rice.
Cowdung is a good source of organic matter. It releases nutrient slowly, so that nutrient
loss is less followed by more plant uptake. In addition cowdung accelerates the
development of the rice root system which elongates both the surface level and in deep
soil and produces many branches having a large active surface. The active roots can
absorb the nutrients from the whole layer of soil, transport to the shoot and keep the
leaves active.
Over the years Bangladesh Agriculture has experienced with multiple nutrient
deficiencies. For sustainable agriculture, a soil management strategy must be based in
maintaining soil quality, which is only possible by utilization of high quality organic
manures along with inorganic fertilizers. Chemical fertilizers are always expensive
inputs for crop production, especially in a developing country like Bangladesh. In near
future, chemical fertilizers are likely to be even more costly. Global environment
pollution can also be reduced considerably by reducing the use of chemical fertilizers
and increasing the use of cowdung, poultry manure and rice straw. Studies on the effect
of plant growth hormone humic acid and organic manure cowdung are very limited.
In these contexts, it is imperative to evaluate the organic manure management practices
in order to attain sustainable production within limited means of the country. The
present investigation was, therefore, undertaken to find out a suitable management of
plant growth hormone humic acid and organic manure like cowdung in order to
achieve the following objectives –
i. To examine the effect of humic acid and cowdung on growth, yield and
quality of T. aman rice (cv. BRRI dhan39)
ii. To determine how much of this humic acid can compete with cowdung.
`CHAPTER 2
REVIEW OF LITERATURE
Rice is an important staple crop in Bangladesh. Application of humic acid and cowdung
with chemical fertilizer plays an important role on growth, yield and chemical
composition of rice. The literature dealing with the effects of humic acid and cowdung
with chemical fertilizer on the growth, yield and chemical composition of rice is scarce.
However, the relevant literature so far available is reviewed and discussed in this
chapter.
2.1 Effect of humic acid
Saruhan et al. (2011) reported that humic acid treatments raised the yield and yield
components, and this raising was found to be significant statistically. The highest value
for plant heights, bunch lengths, grain yields, 1000 grain weight, crude protein
concentrations and grain number per bunch were obtained from leafs (100%)
fertilizations and the highest hectoliter weight was obtained from seeds (100%)
fertilizations.
Bama (2009) conducted a field experiment to study the influence of different
concentrations of foliar application of lignite humic acid (0.1, 0.5, 1.0, 1.5 & 2.0 per
cent) on rice. The application of humic acid upto 1.5 per cent increased the grain yield
of 4263 kg ha-1 markedly; beyond that level the grain yield was reduced. The uptake of
N, P and K nutrients increased with increasing concentrations of humic acid i.e, 59.4,
8.18, 13.9 kg ha-1
in grain for 1.5 per cent HA compared to control of 48.9, 6.9 and
12.1 kg ha-1
, respectively. The N, P and K recorded in the straw were 30.1, 16.5 and
78.4 kg ha-1
compared to control of 26.1, 14.4 and 66.6 kg ha-1
, respectively.
Delfinea et al. (2005) studied the effect of foliar application of humic acid on plant
growth, photosynthetic metabolism and grain quality of durum wheat. Four fertilization
treatments were applied: a non-fertilized control, a crop fertilized with foliar application
of humic acid, a crop fertilized with mineral N on soil at sowing, tillering and stem
elongation, and a crop fertilized with foliar application of N (ammonium-nitrate
solution). The foliar application of humic acid caused a transitional production of plant
dry mass with respect to unfertilized control and split soil N application. This effect
was also evident for grain yield, spike fertility and grain protein content during the two
years of the study. They concluded that humic acid had limited promoting effects on
plant growth, grain yield and quality, and photosynthetic metabolism of durum wheat,
with respect to split soil N application.
Nandakumar et al. (2004) conducted field experiments to evaluate the effects of humic
acid (HA) in the form of potassium humate on soil nutrient availability at different
growth stages of rice. The treatments consisted of NPK at 75 and 100% of the
recommended dose (100:50:50 kg ha-1
) alone, HA at 10 or 20 kg ha-1
(soil application)
in combination with the NPK fertilizers, and integrated treatments involving soil
application, foliar spraying and root dipping with HA in combination with the NPK
fertilizers. Application of HA in combination with NPK increased soil nutrient
availability at all growth stages (tillering, flowering and harvest) of rice in both Vertisol
and Alfisol. HA at 10 kg ha-1
as soil application + 0.1% HA as foliar spray (twice) +
0.3% HA as root dip + 100% NPK, and HA at 20 kg ha-1
as soil application + 100%
NPK, were the best treatments for improving soil nutrient availability.
Jones et al. (2004) found that humic substances in organic matter are known to help
with crop growth when present in high enough quantities. Commercial humic acid
(HA) is sometimes applied at low application rates (1 – 3 lb/ac) to enhance P or metal
availability, yet growth responses are mixed. The objectives of this study were to 1)
determine if available P concentrations increase in the presence of low rates of HA in
Montana soil, and 2) determine the inter-actions between P fertilization and HA on crop
yield.
Veeral et al. (2003) conducted field experiments to evaluate the direct and residual
effects of lignite flyash (LFA) at three levels viz., 10, 15 and 20 t ha-1
with or without
farmyard manure (FYM) at 12.5 t ha-1
and humic acid (HA) at 30 kg ha-1
on rice-
blackgram cropping system. Lignite flyash at 10 t ha-1
with FYM at 12.5 t ha-1
and HA
at 30 kg ha-1
exerted a remarkable influence on all the yield attributes, ultimately
leading to increased rice yields of 35% over control. With respect to the residual crop,
blackgram, the above treatment showed distinct influence on both grain and haulm
yields.
Bhattacharya et al. (2003) studied the effects of humic acid and farmyard manure on
the performance of rice. Humic acid was sprayed to the soil at 2 days before
transplanting. Plant height at 45 and 90 days after transplanting was highest in plots
treated with 9.0 t FYM, 7.0 t FYM and 1.0 litre humic acid ha-1
(60.9 and 83.4 cm). The
application of 7.0 t FYM and 1.0 litre humic acid ha-1
resulted in the highest dry matter
accumulation at 45 and 90 days after transplanting. The highest number of effective
tillers (288/m2) and number of filled grains per panicle (72.2) were obtained with 1.0
litre humic acid ha-1
. The application of 7.0 t FYM, 1.0 litre humic acid and 1.5 litre
humic acid ha-1
gave the highest grain and straw yields.
Ozaki et al. (2003) investigated the effect of humic acid and solution pH on the uptake
of the radionuclides, 83Rb, 137Cs, 54Mn, 65Zn, 88Y, 102Rh, and 75Se in rice plants
by the multitracer technique. The addition of humic acid to a culture medium
containing SiO2 increased the uptake of Mn and Zn at pH 4.3, whereas their uptake was
decreased at pH 5.3. The uptake of Se, which does not interact with humic acid, was not
affected by its presence. These results suggest that uptake of the radionuclides by the
rice plant is regulated by the affinity of radioactive nuclides for humic acid, as well as
by the soil solution's pH.
Dhanasekaran and Govindasamy (2002) studied the effect of coated urea with different
lignite derived humic substances (LDHS) on the yield of rice and transformation of
applied N in soil. Application of N through various forms of urea significantly
increased the grain and straw yield of rice over the control. Among the various forms of
coated urea, HACU recorded the highest yield of grain (6.63 t ha-1
) and straw (9.58 t
ha-1
) followed by NCU (6.55 and 9.44 t ha-1
of grain and straw yield, respectively).
Application of HACU also recorded the highest N uptake in rice followed by PCACU,
NCU and NHACU. Application of N at 150 kg ha-1
through HACU maintained the
highest N uptake of 103.9 kg ha-1
in grain and 70.29 kg ha-1
in straw. Nitrogen
application at 150 kg ha-1
as HACU maintained the highest mineral N content of 40.12,
33.14 and 28.25/kg at maximum tillering, panicle initiation and at harvest stage,
respectively. NCU recorded the highest mean response ratio (19.33) followed by
HACU (19.3) and PCACU (18.0).
Ping and Liu (1997-01) studied that under chilling stress, humic acid which was
sprayed to the leave of rice (Ha 93-63) can improved it physiological resistance. Some
physiological factors were raised, such as the content of free proline, the activity of
polyphenol oxidase and the content of abscisic acid in the plant tissue, while both of the
permeability of the plasma membrane and the content of malondialdehyde in the leave.
The experimental results were showed humic acid certainly caused the resistance on
rice to chilling injury.
2.2 Effect of cowdung
Bala and Hossain (2008) conducted a field experiment to evaluate the effect of
molybdenum (Mo) with recommended chemical fertilizer and organic matter on yield
and quality of rice cv. BRRI dhan30. Three levels of Mo viz. 0, 100 and 200 ppm were
applied with recommended dose of chemical fertilizers (80, 15, 40, 10, 1.5 kg ha-1
N, P,
K, S and Zn) and organic matter as both cowdung and compost. Plant height, number of
ear bearing tillers hill-1
, straw yield and biological yield were maximum when 100 ppm
Mo was applied with chemical fertilizer. Number of total spikelet panicle-1
, grains
panicle-1
, nitrogen content, nitrogen uptake in grain and straw, and protein content in
grain were recorded better when 100 ppm Mo was applied with cowdung. Those
parameters were minimum when 0 ppm Mo was applied with either cowdung or
compost or NPK. The best performance was obtained when 100 ppm Mo was applied
either with recommended fertilizers or with cowdung/compost. The performance of rice
with 200 ppm of Mo was better than no addition of Mo in respect of yield and yield
contributing characters.
Solaiman and Rabbani (2006) carried out a field experiment to assess the effects of
inorganic and organic fertilizers on vegetative, flowering and fruiting characteristics as
well as yield attributes and yield of Ratan variety of tomato. The plots were treated with
three levels each of N (62, 100 and 200 kg ha-1
), P (11.7, 17.5 and 35 kg ha-1
), K (26.7,
40 and 80 kg ha-1
), S (5, 7.5 and 15 kg ha-1
) and cowdung (5, 10 and 15 t ha-1
).The
highest plant height and dry weight of shoot, the maximum number of clusters of
flowers and fruits/plant as well as the biggest fruit size and fruit yield/plant, fruit yield
ha-1
were obtained from the application of the recommended dose of nutrients viz. 200
kg N + 35 kg P + 80 kg K + 15 kg S ha-1
, but similar results were obtained from the
treatment receiving 5t cowdung/ha along with half of the recommended doses of
nutrients (100 kg N+ 17.5 kg P + 40 kg K + 7.5 kg S ha-1
). The effect of 10 t cowdung
ha-1
, along with one third of the recommended dose of nutrients, was also comparable
to the effect of employing the recommended dose of nutrients. It was further observed,
from an economic standpoint, that the combination of 5 t cowdung ha-1
along with half
of the recommended doses of nutrients appeared to be a viable treatment which would
offer the maximum benefit for tomato production in Bangladesh.
Singh et al. (2006) conducted an experiment during kharif 2004, on an Inceptisol in
Varanasi, Uttar Pradesh, India to evaluate the effects of chemical fertilizer (urea),
cowdung and biofertilizer (Azospirillum) on the yield of rice and physicochemical
properties of the soil. Application of chemical fertilizer, cowdung and Azospirillum,
individually or in combinations, significantly increased the yield attributes (plant
height, number of tillers, panicle length, grain yield and straw yield) over the control.
The treatment comprising 80 kg N ha-1
+ Azospirillum + 2.5 t cowdung ha-1
was
superior over all other treatments in terms of rice yield.
Bodruzzaman et al. (2004) investigated the effect of integrated use of cowdung and
fertilizers on crop productivity. The added fertilizers and manure significantly
influenced the grain yields of the crops. The highest yield in both wheat and rice was
obtained with 100% NPKSZn (T1) in both the years. The higher yield in T1 was
attributed to better yield contributing characters of the crops compared to those in other
treatments. Fifty percent nutrients plus cowdung or sole cowdung was not sufficient to
produce satisfactory yield in either wheat or rice.
Saleque et al. (2003) conducted field experiments to determine the effect of different
doses of chemical fertilizers alone or in combination with cow dung (CD) and rice husk
ash (ash) on yield of lowland rice. The CD and ash were applied on dry season rice
only. The 10-year mean grain yield of rice with T1 was 5.33 t ha-1
per year, while the
yield with T2 was 6.86 t ha-1
per year. Increased fertilizer doses with T3 increased the
grain yield to 8.07 t ha-1
per year, while the application of recommended chemical
fertilizer doses (T4) gave 8.87 t ha-1
per year. The application of CD and ash (T5 and T6)
increased rice yield by about 1 t ha-1
per year over that obtained with chemical fertilizer
alone (T2 and T3, respectively). Over 10 years, the grain yield trend with the control
plots was negative, but not significantly, both in the dry and wet seasons. Under T3
through T6, the yield trend was significantly positive in the dry season, but no
significant trend was observed in the wet season. The treatments, which showed
positive yield trend, also showed positive total P uptake trend. Positive yield trends
were attributed to the increasing P supplying power of the soil.
Saitoh et al. (2001) performed an experiment to evaluate the effect of organic fertilizers
(cowdung and chicken manure) and pesticides on the growth and yield of rice and
revealed that the yield of organic manure treated and pesticide free plots were 10%
lower than that of chemical fertilizer and pesticide-treated plot due to a decrease in the
number of panicle.
Channabasavanna and Biradar (2001) conducted an experiment with 4 sources of
organic manure (FYM 7 t ha-1
, rice husk 5 t ha-1
, poultry manure 2 t ha-1
and press mud
2 t ha-1
) with one control and 3 levels of zinc (0, 25 and 50 kg ZnSO4). Application of
poultry manure with 25 kg ZnSO4 ha-1
gave significantly higher yields over rest of the
treatments. The residual effect was more prominent when rice husk was applied. They
cited that organic manure increased panicle hill-1
and seed particle-1
.
Singh et al. (2001) reported that the application of FYM @ 10 t ha-1
produced 4.64%
higher grain yield than the control.
Hemalatha et al. (2000) studied on the influence of organic manure: dhaincha, sunhemp
and FYM on rice productivity, quality and soil fertilizer. They reported that all the
sources of organic manures improved the rice yield quality and soil fertility.
Results obtained by Dixit and Gupta (2000) revealed that application of FYM at 10 t
ha-1
and blue green algae (BGA) inoculation either alone or in combination, increased
the economic yield of rice. The average increase in the grain yield due to BGA was
0.24t ha-1
. It is (7.5%) while combined use of FYM and BGA showed the increase of
0.60 t ha-1
(19.2%). Addition of FYM and BGA showed positive change in organic
carbon and N content of the soil. Average P and K content also showed increasing
tendency due to the treatment. Highest economic yield of the crop was noted in the
treatment combination of N and FYM + BGA.
Dihiphale et al. (2000) stated that FYM at 8 t ha-1
+ 75% of the recommended rate (N:
P: K at 75: 50: 50 kg ha-1
) resulted in higher panicle length, crop yield, number of filled
grains panical-1
and panicle weight.
Babu and Reddy (2000) conducted a field experiment on the effect of NPK fertilizer,
FYM and poultry manure on rice. They were given 100:50:50 kg NPK ha-1
, 10 t ha-1
FYM, 5 t FYM +50 kg N as top dressing ha-1
or 3 t poultry manure ha-1
, grain yield
were the highest with 5 t FYM+50 kg N ha-1
.
Ram et al. (2000) reported that the use of 30 or 60 kg N ha-1
from organic sources in a
total application of 120 kg N ha-1
increased grain and straw yields, N uptake and
recovery, grain nutritive value, decreased soil pH and increased soil fertility and
economic returns.
Mannan et al. (2000) conducted a field experiment at the Agronomy Field Laboratory
of Bangladesh Agricultural University, Mymensingh, during August to December 1995
to study the effect of manuring and fertilizer application on growth, yield and quality of
transplanted aman rice. Four varieties, namely, BR10, BR11, BR22 and BR23 and five
fertilizer application treatments namely, Fl-inorganic fertilizers (IF), F2= IF +cow dung
5 t ha-1
, F3 = IF + cowdung 10 t ha-1
. F4 = with N application + cowdung 5 t ha-1
, and
F5 = IF with N application + cowdung 10 t ha-1
. The doses of inorganic fertilizers were
150 kg urea, 90 kg TSP, 40 kg MOP, 60 kg gypsum and 10 kg zinc sulphate ha-1
. In F4
and F5 treatments, urea top dressing was delayed at second and third application by one
and two weeks, respectively. The highest grain yield was produced by BR23, and the
other varieties gave significantly lower but similar grain yields. Straw yield was highest
from BR23 and lowest from BR11. Grain protein content was similar and higher in
BR11 and BR23 than the other varieties. Among the fertilizer application, F5 and F3
produced the highest and F1 the lowest grain and straw yields. Grain protein was higher
in F5, F4 and F3 treatments, respectively. Manuring with cowdung up to 10 t ha-1
in
addition to recommended inorganic fertilizers with N application improved grain and
straw yields and qualities of transplant rice over inorganic fertilizers alone.
CHAPTER 3
MATERIALS AND METHODS
This chapter presents a brief description of the materials used and the methods followed
to conduct the experiment. For convenience, the chapter has been divided into various
sub-heads such as location, climate, soil, experimental design, treatments, cultural
operation, collection of soils and plant samples, harvesting and the methods of chemical
analysis and statistical analysis.
The experiment was carried out during the Aman season from August to November,
2010 at Central Farm of Bangladesh Agricultural University, Mymensingh. The study
was made to evaluate the response of cowdung and humic acid on BRRI dhan39.
3.1 Experimental site and soils
The experiment was set up in a typical rice growing soil at the western corner of
the central farm of Bangladesh Agricultural University, Mymensingh. The experimental
field was geographically stands at 24.750
N latitude and 90.50E longitude at a height
of 18 m above the mean sea level. The land of experimental field was medium
high and agro ecologically it has been categorized under the AEZ "Old
Brahmaputra Floodplain". The soil of experimental field belongs to Sonatola Series
under the general soil type "Non-Calcareous Dark Grey Floodplain Soil". The
morphological, physical and chemical characteristics of the experimental soil are
presented in Tables 3.1 and 3.3.
(1) General characteristics
Table 3.1 Morphological characteristics of the soil
Morphological parameter Characteristics
Location Bangladesh Agricultural University Farm,
Mymensingh
Agro ecological zone (AEZ-9) Old Brahmaputra Floodplain
Order Inceptisols
Soil series Sonatala
General soil type Non-Calcareous Dark Grey Floodplain Soil
Parent material Old Brahmaputra river borne deposit
Land type Medium high land
Flood level Above flood level (18)
Drainage Moderately well drained
Cropping pattern Rice crop grown year round (rice-rice)
Topography Fairly leveled
(2) Physical characteristics
Table 3.2 Physical properties of the initial soil sample
Characteristics Value
% Sand 24.53
% Silt 65.21
% Clay 10.26
Soil Textural type Silt loam
(3) Chemical characteristics
Table 3.3 Chemical properties of the initial soil sample
Characteristics Value
pH (Soil: Water = 1: 2.5) 6.49
Organic matter (%) 1.30
Organic carbon (%) 0.72
Total N (%) 0.11
Available P (µg g-1
) 12.1
Exchangeable K (cmol kg-1
) 0.06
Exchangeable Ca (cmol kg-1
) 5.05
Exchangeable Mg (cmol kg-1
) 2.29
Available S (µg g-1
) 9.29
Available B (µg g-1
) 0.17
Available Na (µg g-1
) 0.07
3.2 Weather and Climatic condition
The experimental area under the sub-tropical climate, which is characterized by high
temperature, high humidity and heavy precipitation with occasional gusty wind in
kharif season (April- September) and scanty rainfall associated with moderately low
temperature during rabi season (October-March). The average monthly air temperature,
rainfall, relative humidity and sunshine hours have been presented in Appendix-1.
3.3 Test crop
Rice cultivar BRRI dhan39 was used as test crop. It was developed by the Bangladesh
Rice Research Institute (BRRI) in 1999 and was recommended for aman season. It is
moderately photosensitive variety. This variety was developed from crossing BR 1185-
23-56-2-1-1, BR 1674-28-3-1-1 and BR 2558-7-3-2-2. Its inheritance number was BR
5969-3-2. The height of this variety is about 141cm, characterized by deep green and
erect leaves. Its life cycle ranges from 130-150 days. Grain sizes are long and fine.
Weight of 1000 grains is about 20 g. Yield potentiality 4.5 t ha-1
. It is reported to be
resistant to tungro and sheath blight disease.
3.4 Treatments
There were 9 treatments consisting of two rates of humic acid (3 and 6 L ha-1
), two
rates of CD (5 and 10 t ha-1
). The treatments are as follows:
Treatment code Treatment combinations
T0 HA0+CD0+ NPKS
T1 HA0+CD5+ NPKS
T2 HA0+CD10 +NPKS
T3 HA3+CD0+ NPKS
T4 HA3+CD5+ NPKS
T5 HA3+CD10+ NPKS
T6 HA6+CD0+ NPKS
T7 HA6+CD5+ NPKS
T8 HA6+CD10+ NPKS
Note: CD == Cowdung, HA= Humic acid, CF = Recommended doses of chemical
fertilizers.
The doses of NPKS were as per the recommendations made by
Bangladesh Rice Research Institute (BRRI) and that was urea 150 kg ha-1
(69 kg N
ha-1
), TSP 100 kg ha-1
, MOP 70 kg ha-1
, Zinc sulphate 5 kg ha-1
and Borax 10 kg
ha-1
.
3.5 Collection of cowdung and humic acid
For the experiment humic acid was collected from Global Agrovat Company
Limited and cowdung was collected from the Dairy farm of Bangladesh
Agricultural University, Mymensingh. Humic acid was used in liquid form.
3.6 Land preparation
Land preparation was done with a power tiller on 08 August 2010. The field was
then thoroughly prepared with the help of ladder. Weeds and stubbles were removed
from the field to obtain desirable puddling condition, the field was carefully irrigated.
The land was finally prepared on 09 August 2010. Field lay out was done on the next
day.
3.7 Layout of the experiment
The experiment was laid out in a randomized complete block design with three
replications. There were altogether (3×9) = 27 unit plots in the experiment. Each
replication was divided into 9 unit plots where the treatment combinations were
located at random. The net size of each unit plot area was 10 m2 (4.0 m x 2.5m). The
spaces between blocks and between plots were 1m and 0.5 m, respectively. The
complete layout of the experiment has been presented in the Figure 3.1.
.
4m
2.5m
E
N S
W
Fig.3.1. Layout of the experiment.
R-I R-II R-III
T2 T7 1 m T4
T7 T3 T2
T0 T5 T7
T3 T8 T1
1m
T1 T2 T3
0.5m
T4 T0 T5
T5 T4 T6
T6 T1 T8
T8 T6 T0
1 m
Legend:
Design: RCBD
Plot length: 4 m
Plot width: 2.5 m
Plot size: 4 m × 2.5 m
Plot to plot distance: 0.5 m
Replication to replication distance: 1 m
Number of replication: 3
Number of plot in each replication: 9
Number of total plot: 3×9=27
Unit plot
3.8 Seedling transplanting
Seedlings of 25 days old were transplanted on 12 August 2010. Seedlings were
planted with the spacing of 15cm x20cm.
3.9 Intercultural operations
3.9.1 Gap filling
Seedlings in some hills died off, and those were replaced by gap filling on 20
August 2010 with seedlings from the same source.
3.9.2 Irrigation and drainage
Experimental field was given flood irrigation to maintain level of standing water
up to 6 cm at the early stage to retard tillering and 8-10 cm in the later stage to
discourage late tillering. Three irrigations were given throughout the growing season.
The field was finally drained out before 15 days of harvest to enhance maturity.
3.9.3 Weeding
Crops were infested with different weed species. Weeding was done twice by hand
pulling on 30 August and 12 September 2010.
3.10 General observations of the experimental field
Observations were regularly made and the field looked nice with normal green
plants. Incidence of stem borer was observed. Disease infestation was not too severe to
cause damage to the crop. Lodging of any plant was not observed.
3.11 Plant sampling
Plant samples were collected for chemical analysis from each plot at the final
harvest. Ten plants from each plot were carefully uprooted by hands through
random selection. The fresh weight of plant samples were recorded and then dried in
air followed by oven drying at 60°C for 48 hours and the dry weight of the plants
were noted.
3.12 Harvesting, threshing, cleaning and processing
Maturity of crop was determined when about 90% of the seeds became golden
yellow. Ten hills were selected randomly from each unit plot and uprooted before
harvesting for recording necessary data. The crop was harvested on 17th
November
2010. The harvested crop of each plot was separately bundled, properly tagged and
then brought to the threshing floor. The plant threshed and crop and straw was collected
plot-wise. The grains were cleaned and sun dried, and straws were sun dried properly. Finally, grain and
straw yields plot-1
were recorded and these were converted to t ha-1
.
3.13 Data collection of crop characters
i. Plant height
ii. Panicle length
iii. Number of total tillers hill-1
iv. Number of effective tillers hill-1
v. Number of grains panicle-1
vi. Number of filled grains panicle-1
vii. 1000-grain weight
viii. Grain yield
ix. Straw yield
x. Biological yield
xi. Harvest index (%)
Data on individual plant parameters were recorded from ten randomly selected hills of
each plot and those on grain yield, straw yield, biological yield and harvest index
were recorded from the whole plot at harvest.
3.14 Procedure of recording data
Ten hills were selected at random from each plot before harvesting and the data were
recorded on the following parameters.
3.14.1 Plant height
The height of the plants was measured from the ground level to the top of the
panicle. From each plot, plants of 10 hills were measured and averaged.
3.14.2 Panicle length
Measurement was taken from the basal node of the rachis to apex of each panicle.
Each observation was a mean of 10 hills.
3.14.3 Number of total tillers hill-1
Ten hills were taken from each plot randomly and the total number of tillers hill-1
was counted.
3.14.4 Number of effective tillers hill-1
Ten hills were taken from each plot randomly and the total number of
effective tillers hill-1
was counted.
3.14.5 Number of total grains panicle-1
Presence of spikelet was considered as grain and total number of grains present
on each panicle was counted.
3.14.6 Number of filled grains panicle-1
Presence of any food material in the spikelet was considered as filled grain and
total number of grains present on each panicle was counted.
3.14.7 1000-grain weight
Thousand grains were taken from each plot and the weights of grains were measured in
gram after sun drying in an electric balance.
3.14.8 Grain yield
Grains obtained from each unit plot were sun dried and weighed separately and
carefully recorded. Grain yield was adjusted to 14% moisture content. The yield was
then converted to t ha-1
.
3.14.9 Straw yield
After the separation of grain from rice plant, the straw were collected and
weighed and then recorded carefully. Straw yield was converted into t ha-1.
3.14.10 Biological yield
Grain yield and straw yield are all together regarded as biological yield. Biological
yield was calculated following the formula-
Biological yield = Grain yield + Straw yield
3.14.11 Harvest index (%)
Harvest index was calculated on the basis of adjusted grain and straw yields, using the
following formula:
Harves t index (%) = Grain yield
Biological yield 100
3.15 Collection and preparation of soil and plant samples
3.15.1 Pre-planting and post-harvest soil samples
One pre-planting soil sample was collected from the experimental plot. The soil
samples were air dried for several days avoiding direct sunlight and dust. The
samples were ground with wooden roller and dry roots, grasses and other
substances were removed from the samples. The samples were then properly
preserved in polyethylene bags for chemical analyses. The post-harvest soil
samples were collected from the each plot and processed as mentioned above.
3.15.2 Processing of plant samples
The plant samples collected from each plot was dried in an oven at 600C for about
48 hours. Then they were ground to pass through a 20-mesh sieve in a grinding mill.
The prepared samples were then put into polyethylene bags and kept in desiccators until
use.
3.16 Physical and chemical analysis of initial soil
3.16.1 Particle size analysis
Particle size analysis of soil was done by hydrometer method (Black, 1965) and
the textural class was determined by plotting the values for % sand, % silt and
% clay to the Marshall's triangular coordinate following USDA system.
3.16.2 Soil pH
Soil pH was measured with the help of a glass electrode pH meter, using soil water
suspension of 1:2.5 as described by Jackson (1962).
3.16.3 Determination of organic matter
Organic carbon of the soil was determined by wet oxidation method of Black
(1965). The underlying principal was used to oxidize the organic matter with an
excess of 1N K2Cr2O7 in presence of concentrated H2SO4 and concentrated H3PO4 and
to titrate the excess K2Cr2O7 solution with 1N FeSO4, to obtain the organic matter content,
the amount of organic carbon was multiplied by the van bammelen factor 1.73. The
result was expressed in percentage (Page et al., 1982).
3.16.4 Determination of total nitrogen
Total nitrogen of each soil sample was determined by semi-micro kjeldahl method
followed by Jackson (1962) through the digestion of organic matter with commercial
sulphuric acid (H2SO4) and catalyst mixture (K2SO4: CuSO4: Se powder) in the ratio
of 100:10:1). Three distinct steps were namely digestion, distillation and
titration. The ammonia evolved in distillation step was collected in boric acid solution
(2%) and was titrated against 0.01 N H2SO4.
3.16.5 Determination of available phosphorus
Available P was determined from the initial soil extracted following the method of Olsen et al.
(1954). By developing the blue colour with SnC12 and the molybdophosphate blue colour
were measured at 660 nm wavelength by a spectrophotometer and available P was calculated
with the help of a standard curve.
3.16.6 Determination of exchangeable potassium
Exchangeable K was determined from 1N NH4OAc (pH 7.0) extract of the
soil by using flame photometer (Black, 1965).
3.16.7 Cation exchange capacity
Cation exchange capacity of soil sample was determined by ammonium acetate
saturation method. In this method, soil samples were saturated with 1N sodium
acetate (NaOAc) solution. Then the soil samples were washed by 99% isopropyl
alcohol. The sodium ions were replaced from saturated samples by NH4OAc solution.
Displaced sodium in the solution was then measured by flame photometer (Black,
1965; Page et al., 1989).
3.17 Chemical analyses of grain and straw
3.17.1 Preparation of samples
Grain and straw samples were dried in an oven at 65°C for 48 hours and after
cooling they were ground by a grinding machine. The prepared samples were then put
into paper bags and kept into the desiccators till being used.
3.17.2 Digestion of samples
Exactly, 1 g of finely grinded plant material was taken into a 250 mL conical flask and
10 mL of di-acid mixture (HNO3: HClO4 = 2:1) was added to it. Then, it was
placed on the electric hot plate for heating at 180-200°C until the solid particles
were nearly disappeared and white fumes were evolved from the flask (Jackson,
1962). It was then cooled at room temperature, washed with distill ed water
repeatedly and filtered through filter paper (Whatman No. 42) into a 100 mL
volumetric flask and the volume was made up to the mark with distilled water. The
grain and straw extracts were preserved separately in plastic bottles for the analysis
of different elements.
3.17.3 Determination of nitrogen
The concentration of N was determined by semi-micro kjeldahl method as followed by
Jackson (1962) through the digestion of organic matter with commercial sulphuric acid
(H2SO4) and catalyst mixture (K2SO4: CuSO4: Se powder) in the ratio of 100:10:1.
Three distinct steps were namely digestion, distillation and titration. The
ammonia evolved in distillation step was collected in boric acid solution (2%) and was
titrated against 0.01 N H2SO4.
3.17.4 Determination of phosphorus
The concentration of P in the digested grain and straw were determined from the
extract by adding ammonium molybdate and SnCl2 solution and measuring the colour
with the help of spectrophotometer at 660 nm wavelength (Jackson, 1962).
3.17.5 Determination of potassium
Potassium concentration in the digested grain and straw were determined directly
with the help of flame photometer (Jackson, 1962).
3.17.6 Determination of sulphur
The S concentration in the digest of grain and straw were determined by adding acid
seed solution and precipitating with BaCl2 crystal and measuring of turbidity with
the help of spectrophotometer at 420 nm wavelengths as outline by Tandon (1995).
3.17.7 Determination of calcium
The content of calcium in digested grain and straw was determined by
complexometric method of titration using Na2EDTA as a complexing agent in the
presence of calcon indicator at pH 12 (Page et al., 1982).
3.17.8 Determination of magnesium
The content of magnesium in digested grain and was determined by
complexometric method of titration using Na2EDTA as a complexing agent in the
presence of EBT indicator at pH 10 (Page et al., 1982).
3.17.9 Determination of boron
Boron concentration in the digested grain and straw were determined by
colorimetric method.(Tandon,1995)
3.17.10 Determination of sodium
Sodium concentration in the digested grain and straw were determined directly
with the help of flame photometer (Jackson, 1962).
3.18 Nutrient uptake
The nutrient uptake was calculated by the formula-
Nutrient uptake (kg ha-1
) = Minerals constituent (%) Dry matter weight (kg ha
-1)
100
3.19 Statistical analysis
Data were statistically analyzed by analysis of variance (ANOVA) technique using
the MSTAT statistical Computer Package Programmed in accordance with the
principles of Randomized Complete Block Design (RCBD). The treatment means
were adjusted by Least Significant Difference (LSD) test as described by Gomez
and Gomez (1984).
CHAPTER 4
RESULTS AND DISCUSSION
This chapter comprises the presentation and discussion of the results of the effect of
humic acid and cowdung with chemical fertilizers on the growth, yield and chemical
composition of rice (BRRI dhan39). The statistical analysis on various yield
contributing characters and nutrient content of grain and straw of rice plant were
tabulated. The results obtained on different agronomic parameter have been shown in
Tables (4.1- 4.3). Nutrient contents in grain and straw of rice (BRRI dhan39) was
presented in Tables (4.4 - 4.6). Nutrient uptake by grain and straw of rice (BRRI
dhan39) was presented in Tables (4.7- 4.9). The results are presented and discussed
under different headings below:
4.1 Effect of PGR (humic acid) and cowdung with chemical fertilizers (N, P, K &
S) on the growth, yield and chemical composition of T. aman rice (BRRI
dhan39)
4.1.1 Plant height
Plant height was significantly influenced by different doses of humic acid (Table 4.1).
Humic acid produced significantly the longest plant (104.09 cm) where the shortest
plant height (94.36 cm) was obtained at control. The application of humic acid at the
rate of 3 L ha-1
produced 101.72 cm plant height whereas at the rate of 6 L ha-1
produced 104.09 cm plant height.
Application of cowdung did not significantly affected the plant height (Table 4.2). The
application of cowdung @ 5 t ha-1
produced 101.51 cm plant height whereas application
of cowdung @ 10 t ha-1
produced 100.56 cm plant height.
There was a significant difference in plant height due to combined application of humic
acid and cowdung (Table 4.3). The highest plant height (106.5 cm) was obtained in T4
due to the interaction of humic acid and @ 3 L ha-1
and cowdung @ 5 t ha-1
respectively
which was statistically higher than T3 (98.11 cm), T1 (94.32 cm) and T2 (97.67 cm).
The lowest plant height (91.08 cm) was obtained at T0 treatment (control).
4.1.2 Panicle length
A significant difference in panicle length was obtained with the application of humic
acid (Table 4.1). In case of humic acid application, the longest (28.50 cm) panicle
length was obtained when humic acid was applied @ 3 L ha-1
and the lowest (23.65 cm)
was obtained at T0 (control). The loss of nitrogen is less in presence of humic acid
which helps in vegetative growth such as panicle length of rice plant. This finding was
corroborated with the observation made by Mishra and Srivastava (1988).
The application of cowdung significantly influenced the panicle length (Table 4.2). The
longest (27.55 cm) panicle length was obtained when cowdung was applied @ 10 t ha-1
and the shortest (25.48 cm) was obtained at T0 (control). This might be due to the
nitrogen which enhanced the vegetative phase of plants.
There was significant difference in panicle length due to interaction of different
application of humic acid and cowdung (Table 4.3). The longest panicle length (29.56
cm) was found in T4 treatment where the combined application of humic acid and
cowdung was @ 3 L ha-1
and 5 t ha-1
, respectively and the lowest panicle length (20.39
cm) was found at T0 (control).
4.1.3 Total tillers hill-1
Total number of tillers hill-1
was significantly influenced by the application of humic
acid (Table 4.1). Humic acid produced significantly highest number of tillers hill-1
(11.80) when humic acid applied @ 3 L ha-1
and the lowest (9.55) was obtained at
(control). Because humic acid influenced plant vegetative growth due to its slow release
and increase availability of nitrogen at various growth phases of plant.
There was an expressive difference in number of total tillers with the application of
cowdung (Table 4.2). The highest number of tillers hill-1
(11.03) was produced by the
application of 5 t ha-1
CD and the lowest (9.88) was obtained at T0 (control).
The interaction application of humic acid and cowdung significantly affected the total
number of tillers hill-1
(Table 4.3). The highest number of tiller (12.48) was obtained in
the interaction of humic acid and cowdung in T4 treatment where humic acid and
cowdung were applied @ 3 L ha-1
and 5 t ha-1
, respectively which was statistically
similar to T5 treatment and the lowest number of tiller (8.48) was obtained at T0
(control). Because humic acid and cowdung is such kind of organic compounds which
promotes nitrogen supply and nitrogen is essential for vegetative growth.
4.1.4 Effective tillers hill-1
The application of humic acid significantly affected the number of effective tillers hill-1
(Table 4.1). The highest effective tiller hill-1
(11.36) was obtained when humic acid was
applied @ 3 L ha-1
and the lowest number of effective tillers hill-1
(9.24) was produced
at T0 (control).
Effective tillers hill-1
was expressively affected by the application of cowdung (Table
4.2). The highest number of effective tillers hill-1
(10.89) was produced when cowdung
was applied @ 5 t ha-1
and the lowest number of effective tillers hill-1
(9.77) was
produced at T0 (control).
Difference in the total number of effective tillers hill-1
was observed due to the
interaction application of humic acid and cowdung (Table 4.3). The highest effective
tiller hill-1
(12.71) was obtained in T4 due to the interaction of humic acid and cowdung
@ 3 L ha-1
and 5 t ha-1
, respectively and the lowest number of effective tillers hill-1
(8.72) was produced at T0 (control). Because humic acid and cowdung were such kind
of compound which promotes supply of nutrients essential for vegetative growth.
4.1.5 Total number of grains panicle-1
Total grains panicle-1
was significantly affected by the application of humic acid (Table
4.1). The highest number of grains panicle-1
(179.89) was found at T3 with the
application of humic acid @ 3 L ha-1
and the lowest was found at T0 (control). It was
noticed that humic acid induced positive effect on number of grain panicle-1
of rice.
The application of cowdung significantly affected total grains panicle-1
(Table 4.2). The
highest number of grains panicle-1
(160.11) was obtained with the application of
cowdung @ 10 t ha-1
and the lowest (145.56) was found at T0 (control).
Total number of grains panicle-1
affected significantly due to interaction of different
application of humic acid and cowdung (Table 4.3). The highest number of grains
(188.00) was obtained at T4 due to the interaction of humic acid and cowdung @ 3 L
ha-1
HA and 5 t ha-1
CD which was statistically similar to T3 and T5 treatments and the
lowest (102.33) was found at T0 (control).
4.1.6 Number of filled grains panicle-1
The application of humic acid significantly influenced filled grains panicle-1
(Table
4.1). Humic acid produced significantly the higher number of filled grains panicle-1
(162.56) when humic acid was applied @ 3 L ha-1
and the lowest filled grains panicle-1
(102.78) was obtained at T0 (control). Humic acid help in uptake of phosphorus as
phosphorus enhances fruiting of plant.
Filled grains panicle-1
was not significantly affected by the application of cowdung
(Table 4.2). The highest number of filled grains panicle-1
(142.11) was obtained by the
application of 10 t ha-1
CD and the lowest filled grains panicle-1
(130.67) was recorded
at T0 (control).
The difference in number of filled grains panicle-1
was obtained due to interaction of
different application of humic acid and cowdung (Table 4.3). The highest number of
filled grains panicle-1
(170.00) was obtained in T4 due to the interaction of humic acid
and cowdung @ 3 L ha-1
HA and 5 t ha-1
CD which were statistically similar to T3 and
T5 and the lowest filled grains panicle-1
(93.00) was obtained at T0 (control).
4.1.7 1000-grain weight
The 1000-grain weight was significantly influenced by the application of humic acid
(Table 4.1). The highest 1000-grain weight (19.51 g) was obtained when humic acid
was applied @ 6 L ha-1
and the lowest (18.29 g) was in control.
The application of cowdung affected 1000-grain weight significantly (Table 4.2). The
highest 1000-grain weight was obtained (19.12 g) when cowdung was applied @ 10 t
ha-1
, the lowest (18. 29 g) was found in control.
The interaction application of humic acid and cowdung affected the 1000-grain weight
significantly (Table 4.3). The highest 1000-grain weight was obtained (19.57 g) in T8
which was similar with T3, T4, T5, T6 and T7, and the lowest 1000- grain weight
(18.17 g) was found in T0 (control).
4.1.8 Grain yield
Grain yield was significantly influenced by the application of humic acid (Table 4.1).
The highest grain yield (4.12 t ha-1
) was obtained when humic acid was applied @ 6 L
ha-1
and the lowest grain yield (2.98 t ha-1
) was at T0 (control).
The application of cowdung affected the grain yield significantly (Table 4.2). The
highest grain yield (3.93 t ha-1
) was obtained when cowdung was applied @ 10 t ha-1
and the lowest grain yield (3.52 t ha-1
) was found in T0 (control).
The combined application of humic acid and cowdung affected the grain yield
significantly (Table 4.3). The highest grain yield (4.23 t ha-1
) was obtained in T8
treatment where humic acid and cowdung were applied @ 6 L ha-1
and 10 t ha-1
,
respectively and the lowest grain yield (2.57 t ha-1
) were found in T0 (control).
4.1.9 Straw yield
The straw yield was significantly influenced by the application of humic acid (Table
4.1). The highest straw yield (10.37 t ha-1
) was obtained when humic acid was applied
@ 3 L ha-1
and the lowest straw yield (7.96 t ha-1
) was in T0 (control).
The application of cowdung affected the straw yield significantly (Table 4.2). The
highest straw yield (9.50 t ha-1
) was obtained when cowdung was applied @ 10 t ha-
1and the lowest straw yield (8.87 t ha
-1) was obtained in T0 (control).
An expressive effect was observed with the combined application of humic acid and
cowdung which affected the straw yield significantly (Table 4.3). The highest straw
yield (10.70 t ha-1
) was obtained when humic acid and cowdung were applied @ 3 L
ha-1
and 10 t ha-1
respectively and the lowest straw yield (7.67 t ha-1
) was found in T0
(control). HA influenced the nutrition and growth of plants in an indirect manner. HA
might also influence the plant growth directly either through its effects on ion uptake or
by more directs effects on the growth regulation of the plant (Vaughan and Linehan,
1976).
4.1.10 Biological yield
The application of humic acid significantly influenced the biological yield (Table 4.1).
The highest biological yield (14.50 t ha-1
) was obtained when humic acid was applied
@ 3 L ha-1
and the lowest biological yield (10.93 t ha-1
) were found at control.
The application of cowdung significantly influenced biological yield (Table 4.2). The
highest biological yield (13.43 t ha-1
) was recorded when cowdung was applied @ 10 t
ha-1
and the lowest biological yield (12.39 tha-1
) were found at control.
The combined application of humic acid and cowdung significantly influenced
biological yield (Table 4.3). The highest biological yield (45.26%) was recorded when
humic acid and cowdung was applied @ 6 L ha-1
and 5 t ha-1
, respectively and the
lowest biological yield (10.23 t ha-1
) were found at control. The humate migrated from
one part of the root system into another, contributing to a more intensive absorption of
iron (Aso and Sakai, 1963).
4.1.11 Harvest index (%)
The application of humic acid significantly influenced harvest index (Table 4.1). The
highest harvest index (43.83%) was found when humic acid was applied @ 6 L ha-1
and
the lowest harvest index (37.32%) was found at control.
The application of cowdung significantly influenced harvest index (Table 4.2). The
highest harvest index (41.52%) was found when cowdung was applied @ 10 t ha-1
and
the lowest harvest index (39.38%) was found at control.
The combined application of humic acid and cowdung significantly influenced harvest
index (Table 4.3). The highest harvest index (45.26%) was recorded when humic acid
and cowdung was applied @ 6 L ha-1
and 5 t ha-1
, respectively and the lowest harvest
index (33.47%) was found at control.
Table 4.1. Effect of PGR (humic acid) on the yield attributes of T. aman (cv. BRRI dhan39)
Treatments Plant
height
(cm)
Panicle
length
(cm )
Total
tillers
hill-1
(No.)
Effective
tillers
hill-1
(No.)
Total
grains
panicle-1
(No.)
Filled
grains
panicle-1
(No.)
1000-
grain
weight
(g)
Grain
yield
(t ha-1
)
Straw
yield
(t ha-1
)
Biological
yield
(t ha-1
)
Harvest
index (%)
HA0 94.36c 23.65b 9.55b 9.24c 117.78c 102.78c 18.29b 2.98b 7.96c 10.93b 37.32c
HA3 101.72b 28.50a 11.80a 11.36a 179.89a 162.56a 19.33ab 4.13a 10.37a 14.50a 40.04b
HA6 104.09a 28.33a 9.85b 9.94b 160.22b 140.89b 19.51a 4.12a 9.41b 13.53a 43.83a
CV (%) 3.06 5.45 5.58 5.34 6.09 8.86 7.23 4.40 4.23 5.23 6.23
Level of
significance ** ** ** ** ** ** ** ** ** ** **
Legend: HA = Humic acid,
** indicates significance at 1 % level
Table 4.2. Effect of cowdung on the yield attributes of T. aman (cv. BRRI dhan39)
Treatments Plant
height
(cm)
Panicle
length
(cm )
Total
tillers
hill-1
(No.)
Effective
tillers
hill-1
(No.)
Total
grains
panicle-1
(No.)
Filled
grains
panicle-1
(No.)
1000-
grain
weight
(g)
Grain
yield
(t ha-1
)
Straw
yield
(t ha-1
)
Biological
yield
(t ha-1
)
Harvest
index
(%)
CD0 98.09 25.48b 9.88c 9.77b 145.56c 130.67 18.92b 3.52c 8.87b 12.39b 39.38b
CD5 101.51 27.45a 11.03a 10.89a 152.22b 133.44 19.09a 3.78b 9.37a 13.14ab 40.30ab
CD10 100.56 27.55a 10.29b 9.89b 160.11a 142.11 19.12a 3.93a 9.50a 13.43a 41.52a
CV (%) 3.06 5.45 5.58 5.34 6.09 8.86 7.23 4.40 4.23 5.23 6.23
Level of
signifiance NS ** ** ** ** NS ** ** ** ** **
Legend: CD= Cowdung
** indicates significance at 1 % level
NS indicates non significance
Table 4.3. Interaction effects of PGR (humic acid) and cowdung on the yield attributes of T. aman cv. BRRI dhan39
Treatments Plant
height
(cm)
Panicle
length
(cm )
Total
tillers
hill-1
(No.)
Effective
tillers
hill-1
(No.)
Total
grains
panicle-1
(No.)
Filled
grains
panicle-1
(No.)
1000-
grain
weight
(g)
Grain
yield
(t ha-1
)
Straw
yield
(t ha-1
)
Biological
yield
(t ha-1
)
Harvest
index
(%)
T0
HA0CD0 91.08f 20.39d 8.48f 8.72e 102.33e 93.00d 18.17c 2.57d 7.67c 10.23f 33.47c
T1
HA0CD5 94.32ef 24.44c 10.51cd 9.39de 111.67e 96.33d 18.37b 2.93c 8.00c 10.93e 36.67c
T2
HA0CD10 97.67de 26.11bc 9.67cde 9.60de 139.33d 119.00c 18.33b 3.43b 8.20c 11.63d 41.83a
T3
HA3CD0 98.11cde 27.61ab 11.03bc 10.76b 180.00ab 164.67a 19.17a 4.03a 9.50c 13.53c 42.51a
T4
HA3CD5 106.50a 29.56a 12.48a 12.71a 188.00a 170.00a 19.37a 4.23a 10.90a 15.13a 45.26a
T5
HA3CD10 100.56bcd 28.33ab 11.87ab 10.61bc 171.67abc 153.00ab 19.47a 4.13a 10.70a 14.83b 38.64b
T6
HA6CD0 105.09ab 28.44a 10.13cde 9.82bcd 154.33cd 134.33bc 19.43a 3.97a 9.43b 13.40c 42.15a
T7
HA6CD5 103.72abc 28.34ab 10.10cde 10.57bcd 157.00c 134.00bc 19.53a 4.17a 9.20b 13.37c 38.96b
T8
HA6CD10 103.45ab 28.22ab 9.32ef 9.44de 169.33bc 154.33ab 19.57a 4.23a 9.60b 13.83b 44.09a
CV 4.40 5.45 5.58 5.34 6.09 8.86 7.23 4.40 4.23 5.23 6.23
Level of
signifiance ** ** * * * ** ** ** * ** **
Legend: HA = Humic acid, CD= Cowdung, * indicates significance at 5 % level, ** indicates significance at 1 % level
4.2 Nutrient content of grain and straw
4.2.1 Nitrogen content
The nitrogen content in grain and straw was significantly influenced by the application
of humic acid (Table 4.4). The highest N content (1.35%) was obtained in grain when
humic acid was applied @ 6 L ha-1
and the lowest N content was obtained at T0
(control). The highest N content (0.91%) in straw was also obtained when humic acid
was applied @ 6 L ha-1
and the lowest N content (0.45%) in straw was recorded at HA0
(control). Govindasamy and Chandrasekaran (2002) reported that addition of humic
acid was found to increase the content and enhance the uptake of N, P, K, Ca, Mg, Fe,
Mn and Zn by rice.
The nitrogen content in grain and straw was significantly influenced by the application
of cowdung (Table 4.5). The highest N content (1.36 %) in grain was obtained when the
dose of cowdung was 10 t ha-1
. The lowest N content (1.28 %) in grain was recorded at
T0 (control). The highest N content (0.75 %) in straw was also recorded when the
cowdung was applied @ 10 t ha-1
and the lowest N content (0.59 %) in straw was at T0
(control).
The interaction effect of humic acid and cowdung significantly affected the nitrogen
content in grain and straw (Table 4.6). The highest N content (1.44%) was obtained in
grain when humic acid and cowdung were applied @ 3 L ha-1
and 5 t ha-1
, respectively
while the lowest N content (1.20%) was found in T0 (control). The highest N content
(0.97%) was obtained in straw when humic acid and cowdung was applied @ 6 L ha-1
and 10 t ha-1
, respectively and the lowest N content (0.35%) was found in T0 (control).
4.2.2 Phosphorus content
The phosphorus content in grain and straw was significantly influenced by the
application of humic acid (Table 4.4). The highest phosphorus content (0.26%) in grain
was found when humic acid was applied @ 6 L ha-1
and the lowest P content (0.23%)
in grain was found in HA0 (control). The highest P content (0.18%) in straw was found
when humic acid was applied @ 6 L ha-1
and the lowest P content (0.12%) in straw was
found in HA0 (control). At optimum level of HA, the roots were highly branched and
this might have resulted an increase in surface area, which would have facilitated more
efficient nutrient absorption (Mallikarjuna rao et al., 1987).
The application of cowdung affected the phosphorus content in grain and straw
significantly (Table 4.5). The highest P content (0.25%) in grain was found when
cowdung was applied @ 10 t ha-1
and the lowest P content (0.23%) was observed in
CD0 (control). The highest P content (0.17%) obtained in straw when cowdung was
applied @ 10 t ha-1
the lowest P content (0.14%) was found in CD0 (control).
The interaction of humic acid and cowdung affected the phosphorus content in grain
and straw significantly (Table 4.6). The highest P content (0.28%) was obtained in
grain at T8 when humic acid and cowdung were applied @ 6 L ha-1
and 10 t ha-1
,
respectively and the lowest P content (0.2%) was found in T0 (control). The highest P
content (0.20%) was obtained in straw at T8 when humic acid and cowdung was applied
@ 6 L ha-1
and 10 t ha-1
, respectively and the lowest P content (0.09%) was found in T0
(control).
4.2.3 Potassium content
The potassium content in grain and straw was significantly influenced by the
application of humic acid (Table 4.4). The highest K content (0.80%) in grain was
obtained when humic acid was applied @ 6 L ha-1
and the lowest (0.62%) in grain was
obtained in HA0 (control). The highest K content (1.36%) in straw was obtained when
humic acid was applied @ 6 L ha-1
and the lowest (0.99%) in straw was found in HA0
(control).
The application of cowdung affected the content of K in grain significantly (Table 4.5).
The highest K content (0.83%) was obtained in grain when cowdung was applied @ 5 t
ha-1
and the lowest K content (0.53%) was found in CD0 (control). There was no
significant effect of cowdung on K content in straw.
The interaction effect of humic acid and cowdung on K content in grain was significant
and non significant in straw (Table 4.6). The highest K content (0.95%) in grain was
found when humic acid and cowdung were applied 6 L ha-1
and 5 t ha-1
, respectively
and the lowest K content (0.04%) was found in T0 (control).
4.2.4 Sulphur content
The sulphur content in straw was influenced by the application of humic acid (Table
4.4). The highest S content (0.09%) in straw was obtained in HA6 where humic acid
was applied @ 6 L ha-1
and the lowest (0.04%) was obtained in HA0 (control). There
was no significant influence of humic acid in grain.
The sulphur content was significantly influenced by the application of cowdung in
straw (Table 4.5). The highest S content in straw (0.08%) was obtained in CD10 when
cowdung was applied @ 10 t ha-1
and the lowest (0.06%) was obtained in HA0
(control). There was no significant influence of cowdung in grain.
The interaction application of humic acid and cowdung affected the S content
significantly in grain (Table 4.6). The highest S content (0.19%) in grain was found in
T4 when humic acid and cowdung were applied combindly @ 3 L ha-1
and 5 t ha-1
,
respectively and the lowest S content (0.16%) was found in T5 and T7. There was no
significant interaction effect of humic acid and cowdung in straw.
4.2.5 Calcium content
The calcium content in grain and straw was significantly influenced by the application
of humic acid (Table 4.4). The highest Ca content (0.25%) in grain was obtained when
humic acid was applied @ 6 L ha-1
and the lowest (0.16%) in grain was in control and
the highest Ca content (0.67%) in straw was recorded when humic acid was applied @
6 L ha-1
and the lowest (0.44%) in straw was in HA0 (control).
The application of cowdung affected the Ca content in grain and straw significantly
(Table 4.5). The highest Ca content (0.25%) was obtained in grain when cowdung was
applied @ 10 t ha-1
and the lowest Ca content (0.18%) was found in CD0 (control). The
highest Ca content (0.65%) was obtained in straw when cowdung was applied @ 10 t
ha-1
and the lowest Ca content (0.48%) was found in CD0 (control).
The interaction effect of humic acid and cowdung affected the Ca contents in grain
significantly (Table 4.6). The highest Ca content (0.28%) was obtained in grain when
humic acid and cowdung were applied @ 6 L ha-1
and 10 t ha-1
, respectively and the
lowest Ca content (0.08%) was found in T0 (control). There was no significant
interaction effect of humic acid and cowdung in straw.
4.2.6 Magnesium contents
The magnesium content in grain and straw was significantly influenced by the
application of humic acid (Table 4.4). The highest Mg content (0.21%) in grain was
obtained when humic acid was applied @ 3 L ha-1
and the lowest (0.16%) in grain was
in HA0 (control). The highest Mg content (0.78%) in straw was found when humic acid
was applied @ 6 L ha-1
and the lowest (0.57%) in straw was in HA0 (control).
The application of cowdung affected the Mg content in grain and straw significantly
(Table 4.5). The highest Mg content(0.21%) was found in grain when cowdung was
applied @ 5 t ha-1
and the lowest Mg content (0.18%) was found in CD0 (control). The
highest Mg content (0.76%) was obtained in straw when cowdung was applied @ 10 t
ha-1
and the lowest Mg content (0.65%) was found in CD0 (control).
The magnesium content has no significant interaction effect due to the combined
application of humic acid and cowdung in the grain and straw (Table 4.6)
4.2.7 Boron content
The boron content in both grain and straw was significantly influenced by the
application of humic acid (Table 4.4). The highest B content (17.0 µg g-1
) in grain was
recorded when humic acid was applied @ 6 L ha-1
and the lowest (16.16 µg g-1
) in grain
was in control. The highest B content (16.90 µg g-1
) in straw was found when humic
acid was applied @ 6 L ha-1
and the lowest (16.51 µg g-1
) in straw was in HA0 (control).
The application of cowdung affected the B content in grain significantly (Table 4.5).
The highest B content (16.81 µg g-1
) was recorded in grain when cowdung was applied
@ 10 t ha-1
and the lowest B content (16.05 µg g-1
) was recorded in CD0 (control). The
B content in straw was not significantly influenced by the application of cowdung.
The boron content has no significant interaction effect due to the combined application
of humic acid and cowdung in the grain and straw (Table 4.6)
4.2.8 Sodium content
The sodium content by both grain and straw was significantly influenced by the
application of humic acid (Table 4.4). The highest Na content (155.24 µg g-1
) in grain
and in straw (288.20 µg g-1
) was recorded when humic acid was applied @ 6 L ha-1
and
the lowest (129.40 µg g-1
) in grain and in straw (250.29 µg g-1
) was in HA0 (control).
The application of cowdung affected the Na content in both grain and straw
significantly (Table 4.5). The highest Na content (157.96 µg g-1
) was obtained in grain
and in straw (297.79 µg g-1
), when cowdung was applied @ 5 t ha-1
and the lowest Na
content (128.36 µg g-1
) in grain and in straw (243.50 µg g-1
) was found in CD0
(control).
There was no significant interaction effect due to the combined application of humic
acid and cowdung in the Na content in grain and straw (Table 4.6)
Table 4.4. Effect of PGR (humic acid) on N, P, K, S, Ca, Mg, B and Na contents of T. aman rice (cv. BRRI dhan39)
Treatments Nitrogen
(%)
Phosphorus
(%)
Potassium
(%)
Sulphur
(%)
Calcium
(%)
Magnesium
(%)
Boron
(µg g-1
)
Sodium
(µg g-1
)
Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw
HA0 1.34a 0.45c 0.23b 0.12b 0.62c 0.99c 0.16 0.04b 0.16b 0.44c 0.16b 0.57c 16.16b 16.51b 129.40c 250.29b
HA3 1.30b 0.67b 0.23b 0.17ab 0.75b 1.16b 0.15 0.08ab 0.24a 0.62b 0.21a 0.72b 16.43ab 16.55b 154.43b 251.24b
HA6 1.35a 0.91a 0.26a 0.18a 0.80a 1.36a 0.15 0.09a 0.25a 0.67a 0.20a 0.78a 17.00a 16.90a 155.24a 288.20a
CV (%) 0.81 1.99 4.32 6.41 2.95 23.36 3.61 12.31 16.61 5.00 13.75 6.20 3.66 5.24 3.62 1.09
Level of
significance ** ** ** ** ** ** NS ** ** ** ** ** ** ** ** **
Legend: HA = Humic acid,
** indicates significance at 1 % level
NS indicates non significance
Table 4.5. Effect of cowdung on N, P, K, S, Ca, Mg, B and Na contents of T. aman rice (cv. BRRI dhan39)
Treatments Nitrogen
(%)
Phosphorus
(%)
Potassium
(%)
Sulphur
(%)
Calcium
(%)
Magnesium
(%)
Boron
(µg g-1
)
Sodium
(µg g-1
)
Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw
CD0 1.28b 0.59c 0.23b 0.14b 0.53b 1.10 0.15 0.06c 0.18c 0.48c 0.18b 0.65c 16.05b 15.94 128.36c 243.50c
CD5 1.35a 0.69b 0.25a 0.16ab 0.83ab 1.14 0.15 0.07b 0.22b 0.60b 0.21a 0.67b 16.74ab 16.82 157.96a 297.79a
CD10 1.36a 0.75a 0.25a 0.17a 0.81a 1.27 0.16 0.08a 0.25a 0.65a 0.18b 0.76a 16.81a 17.20 152.77b 248.44b
CV (%) 0.81 1.99 4.32 6.41 2.95 23.36 3.61 12.31 16.61 5.00 13.75 6.20 3.66 5.24 3.62 1.09
Level of
signifiance ** ** ** ** ** NS NS ** ** ** * ** ** NS ** **
Legend: CD= Cowdung
* indicates significance at 5 % level
** indicates significance at 1 % level
NS indicates non significance
Table 4.6. Interaction effect of different doses of PGR (humic acid) and cowdung on N, P, K, S, Ca, Mg, B and Na contents of
T. aman rice (cv. BRRI dhan39)
Treatments
Nitrogen
(%)
Phosphorus
(%)
Potassium
(%)
Sulphur
(%)
Calcium
(%)
Magnesium
(%)
Boron
(µg g-1
)
Sodium
(µg g-1
)
Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw
T0
HA0CD0 1.20d 0.35i 0.20f 0.09e 0.04f 0.84 0.16bc 0.02 0.08c 0.35 0.13 0.51 15.13 15.58 93.00i 180.57g
T1
HA0CD5 1.27c 0.48h 0.25bcd 0.13d 0.95a 1.05 0.15c 0.04 0.17b 0.47 0.21 0.53 16.82 16.55 146.30h 280.57e
T2
HA0CD10 1.27c 0.53g 0.23e 0.15c 0.85b 1.07 0.17ab 0.05 0.24a 0.51 0.14 0.68 16.54 17.41 148.90g 289.73d
T3
HA3CD0 1.38a 0.59f 0.23de 0.17b 0.76de 1.15 0.15c 0.07 0.23ab 0.54 0.21 0.66 16.03 15.86 160.60f 295.43c
T4
HA3CD5 1.44a 0.64e 0.23e 0.17bc 0.74e 1.01 0.19a 0.07 0.24a 0.64 0.22 0.73 16.82 16.99 169.63e 309.03a
T5
HA3CD10 1.35b 0.77d 0.24cde 0.17b 0.77d 1.33 0.13d 0.09 0.25a 0.67 0.21 0.78 16.44 16.78 133.07c 149.27e
T6
HA6CD0 1.35b 0.84c 0.25bc 0.17b 0.80c 1.31 0.15c 0.08 0.23ab 0.56 0.21 0.77 16.99 16.37 131.47b 254.50f
T7
HA6CD5 1.35b 0.93b 0.26b 0.18b 0.80c 1.36 0.13d 0.09 0.25a 0.70 0.21 0.77 16.57 16.92 157.93d 303.77b
T8
HA6CD10 1.35b 0.97a 0.28a 0.20a 0.81c 1.40 0.17bc 0.09 0.28a 0.76 0.18 0.81 17.44 17.41 176.33a 306.33ab
CV (%) 0.81 1.99 4.32 6.41 2.95 23.36 3.61 12.31 16.61 5.00 13.75 6.20 3.66 5.24 3.62 1.09
Level of
significance ** ** ** ** ** NS ** NS * NS NS NS NS NS ** **
Legend: HA = Humic acid, CD= Cowdung, ** indicates significance at 1 % level, * indicates significance at 5 % level
NS indicates non significance
4.3 Nutrient uptake by grain and straw
4.3.1 Nitrogen uptake
The nitrogen uptake by both grain and straw was significantly influenced by the
application of humic acid (Table 4.7). The highest N uptake (55.36 kg ha-1
) was
obtained in grain and in straw (48.56 kg ha-1
) by the application of humic acid @ 6
L ha-1
. The lowest N uptake (41.21 kg ha-1
) was obtained in grain and in straw
(32.21 kg ha-1
) was found in HA0 (control). Saalbach (1956) stated that humic acid
enhanced the uptake and content of nitrogen in rye.
The nitrogen uptake by both grain and straw was significantly influenced by the
application of cowdung (Table 4.8). The highest N uptake (53.59 kg ha-1
) was
obtained in grain and in straw (43.88 kg ha-1
) by the use of cowdung @ 10 t ha-1
.
The lowest N uptake (46.90 kg ha-1
) was obtained in grain and in straw (36.90 kg
ha-1
) in CD0 (control).
The difference in nitrogen uptake by grain and straw due to interaction effect of
humic acid and cowdung was also significant (Table 4.9).The highest N uptake
(57.40 kg ha-1
) in grain was obtained by the application of humic acid and cowdung
@ 3 L ha-1
and 10 t ha-1
, respectively and 52.67 kg ha
-1 in straw by the use of humic
acid and cowdung @ 6 L ha-1
and 10 t ha-1
, respectively. The lowest N uptake
(32.67 kg ha-1
) in grain and in straw (25.43 kg ha-1
) was found in T0 (control).
4.3.2 Phosphorus uptake
The phosphorus uptake by both grain and straw was significantly influenced by the
application of humic acid (Table 4.7). The highest P uptake (10.61 kg ha-1
) was
obtained in grain and in straw (8.27 kg ha-1
) by the application of humic acid @ 6
L ha-1
. The lowest P uptake (6.72 kg ha-1
) in grain and in straw (6.36 kg ha-1
) was
found in HA0 (control). The different humic acids had significant effect on nitrogen
and phosphorus uptake by oats. The efficiency indices of various humic acids
ranged between 25 and 65 per cent (Mishra and Srivastava, 1988). In the presence
of humates, the plants could use phosphate fertilizers fully at the humic molecules
and the phosphate anion compete on an almost equal basis. Anion exchange
phenomenon could be another reason for increasing P availability and higher P
uptake by rice (Deb and Datta, 1967).
The phosphorus uptake by both grain and straw was significantly influenced by the
application of cowdung (Table 4.8). The highest P uptake (9.55 kg ha-1
) in grain
and in straw (7.28 kg ha-1
)was obtained in CD10 where the application of cowdung
@ 10 t ha-1
and the lowest P uptake (8.27 kg ha-1
) in grain and in straw (7.05 kg
ha-1
) was found in CD0 (control).
The difference in phosphorus uptake by grain and straw due to interaction effect of
humic acid and cowdung was also significant (Table 4.9). The highest P uptake
(11.46 kg ha-1
) in grain and in straw (8.46 kg ha-1
) was obtained by the application
of humic acid and cowdung @ 6 L ha-1
and 10 t ha-1
, respectively and the lowest P
uptake (5.44 kg ha-1
) in grain and in straw (5.77 kg ha-1
) was found in T0 (control).
Jelanic et al. (1966) reported that HA from lignite increased the P content and
uptake in maize plants
4.3.3 Potassium uptake
The potassium uptake by both grain and straw was significantly influenced by the
application of humic acid (Table 4.7). The highest K uptake (32.53 kg ha-1
) in
grain and in straw (63.58 kg ha-1
) was obtained by the application of humic acid @
6 L ha-1
and the lowest K uptake (28.41 kg ha-1
) in grain and in straw (54.44 kg
ha-1
) was found in HA0 (control).
The potassium uptake by both grain and straw was significantly influenced by the
application of cowdung (Table 4.8). The highest K uptake (31.28 kg ha-1
) in grain
and in straw (61.98 kg ha-1
) was obtained by the application of cowdung @ 10 t
ha-1
and the lowest K uptake (29.60 kg ha-1
) in grain and in straw (57.40 kg ha-1
)
was found in CD0 (control).
The potassium uptake was significantly influenced in grain due to the interaction
effect of humic acid and cowdung (Table 4.9). The highest K uptake (33.31 kg ha-
1) in grain and in straw (64.77 kg ha
-1) was obtained by the use of humic acid and
cowdung @ 6 L ha-1
and 10 t ha-1
, respectively and the lowest K uptake (27.54 kg
ha-1
) in grain and in straw (49.71 kg ha-1
) was found in T0 (control).
4.3.4 Sulphur uptake
The sulphur uptake by both grain and straw was significantly influenced due to the
application of humic acid (Table 4.7). The highest S uptake (6.94 kg ha-1
) in grain
and in straw (4.20 kg ha-1
) was obtained by the application of humic acid @ 6 L
ha-1
and the lowest S uptake in grain (5.02 kg ha-1
) and in straw (2.47 kg ha
-1) was
found in HA0 (control). Raina and Goswami (1988) reported a significant increase
in the uptake of N, P, Cu, S and Fe upto 20-ppm carbon as humic acid over control.
The sulphur uptake by both grain and straw was significantly influenced by the
application of cowdung (Table 4.8). The highest S uptake (6.66 kg ha-1
) in grain
and in straw (4.10 kg ha-1
) was obtained by the use of cowdung @10 t ha-1
and the
lowest S uptake (5.86 kg ha-1
) in grain and in straw (3.09 kg ha
-1) was found in CD0
(control).
The interaction effect of sulphur uptake by grain significantly affected by the
application of humic acid and cowdung (Table 4.9). The highest S uptake (8.37 kg
ha-1
) in grain was obtained by the application of humic acid and cowdung @ 3 L
ha-1
and 5 t ha-1
, respectively and in straw (4.86 kg ha-1
) was obtained by the
application of humic acid and cowdung @ 6 L ha-1
and 10 t ha-1
, respectively and
the lowest S uptake in grain(4.11 kg ha
-1) and in straw (1.73 kg ha
-1) was found in
T0 (control).
4.3.5 Calcium uptake
The calcium uptake by both grain and straw was significantly influenced by the
application of humic acid (Table 4.7). The highest Ca uptake (11.08 kg ha-1
) in
grain and in straw (17.71 kg ha-1
) was obtained by the application of humic acid @
6 L ha-1
and the lowest Ca uptake (6.58 kg ha-1
) in grain and in straw (11.79 kg ha
-1)
was found in HA0 (control).
The calcium uptake by both grain and straw was significantly influenced by the
application of cowdung (Table 4.8). The highest Ca uptake (10.39 kg ha-1
) in grain
and in straw (17.0 kg ha-1
) was obtained by the application of cowdung @ 10 t ha-1
and the lowest Ca uptake (8.0 kg ha-1
) in grain and in straw (13.81 kg ha-1
) was
found in CD0 (control).
The calcium uptake by both grain and straw was significantly influenced by the
interaction effect of humic acid and cowdung (Table 4.9). The highest Ca uptake
(11.67 kg ha-1
) in grain and in straw (18.33 kg ha-1
) was obtained by the application
of humic acid and cowdung @ 6 L ha-1
and 10 t ha-1
, respectively and the lowest
Ca uptake (4.93 kg ha-1
) in grain and in straw (8.0 kg ha
-1) was found in T0
(control).
4.3.6 Magnesium uptake
The magnesium uptake by both grain and straw was significantly influenced by the
application of humic acid (Table 4.7). The highest Mg uptake (7.40 kg ha-1
) in grain
and (17.20 kg ha-1
) in straw was obtained by the application of humic acid @ 6 L
ha-1
and the lowest Mg uptake (4.14 kg ha-1
) in grain and in straw (14.96 kg ha-1
)
was found in HA0 (control). Application of 10 kg HA ha-1
as potassium humate
along with 75 per cent recommended dose of fertilizer found to increase the crude
protein content and mineral nutrition (P, K, Ca, Mg, Zn, Cu, Fe and Mn) of
Amaranthus (Bama and Selvakumari, 2001).
The magnesium uptake by both grain and straw was significantly influenced by the
application of cowdung (Table 4.8) The highest Mg uptake 6.57 kg ha-1
in grain
and 16.59 kg ha-1
in straw was obtained by the application of cowdung @10 t ha-1
and the lowest Mg uptake (5.38 kg ha-1
) in grain and in straw (15.93 kg ha
-1) was
found in CD0 (control).
The magnesium uptake by both grain and straw was significantly influenced by the
interaction effect of humic acid and cowdung (Table 4.9). The highest Mg uptake
(8.33 kg ha-1
) in grain was recorded at T8 when the use of humic acid and cowdung
were applied @ 6 L ha-1
and 10 t ha-1
, respectively and in straw (17.39 kg ha-1
) was
obtained at T6 where application rates of humic acid and cowdung were 6 L ha-1
and 10 t ha-1
, respectively. The lowest Mg uptake (3.10 kg ha-1
) in grain and in
straw (14.12 kg ha-1
) was found in T0 (control).
4.3.7 Boron uptake
The boron uptake by both grain and straw was significantly influenced by the
application of humic acid (Table 4.7). The highest B uptake (0.072 kg ha-1
) in grain
and in straw (0.18 kg ha-1
) was obtained with the application of humic acid @ 6 L
ha1, the lowest B uptake (3.97 kg ha
-1)
in grain and in straw (6.46 kg ha
-1) was
found in HA0 (control).
The boron uptake by both grain and straw was significantly influenced by the
application of cowdung (Table 4.8). The highest B uptake (0.069 kg ha-1
) in grain
and in straw (0.17 kg ha-1
) was obtained by the application of cowdung @ 10 t ha-1
and the lowest B uptake (0.058 kg ha-1
) in grain and in straw (0.14 kg ha-1
) was
found in CD0 (control).
The boron uptake was significantly influenced by the application of humic acid and
cowdung (Table 4.9) both in grain and straw. The highest B uptake (0.075 kg ha-1
)
in grain by the application of humic acid and cowdung @ 3 L ha-1
and 10 t ha-1
,
respectively and in straw (0.19 kg ha-1
) was obtained by the application of humic
acid and cowdung @ 6 L ha-1
and 10 t ha-1
respectively. The lowest B uptake (0.036
kg ha-1
) in grain and in straw (0.11 kg ha-1
) was found in T0 (control).
4.3.8 Sodium uptake
The sodium uptake by both grain and straw was significantly influenced by the
application of humic acid (Table 4.7). The highest Na uptake (6.97 kg ha-1
) in grain
and in straw (13.79 kg ha-1
) was obtained by the application of humic acid @ 6 L
ha-1
and the lowest Na uptake (3.97 kg ha-1
) in grain and in straw (6.46 kg ha
-1) was
found in HA0 (control).
The sodium uptake by both grain and straw was significantly influenced by the
application of cowdung (Table 4.8). The highest Na uptake (6.63 kg ha-1
) in grain
and in straw (12.27 kg ha-1
) was obtained by the application of cowdung @ 10 t
ha-1
, the lowest Na uptake (5.20 kg ha-1
) in grain and in straw (9.41 kg ha
-1) was
found in CD0 (control).
The difference in sodium uptake in both grain and straw due to interaction effect of
humic acid and cowdung was also significant (Table 4.9). The highest Na uptake
(7.50 kg ha-1
) in grain and in straw (14.19 kg ha-1
) was obtained by the combined
application of humic acid and cowdung @ 6 L ha-1
and 10 t ha-1
, respectively. The
lowest Na uptake (2.43 kg ha-1
) in grain and in straw (3.12 kg ha
-1) was found in T0
(control).
Table 4.7. Effect of PGR (humic acid) on the N, P, K, S, Ca, Mg, B and Na uptake of T. aman rice cv. BRRI dhan39
Treatments
Nitrogen
(%)
Phosphorus
(%)
Potassium
(%)
Sulphur
(%)
Calcium
(%)
Magnesium
(%)
Boron
(µg g-1
)
Sodium
(µg g-1
)
Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw
HA0 41.21b 32.21c 6.72c 6.36c 28.41c 54.44c 5.02c 2.47c 6.58c 11.79b 4.14b 14.96c 0.049b 0.15b 3.97b 6.46b
HA3 54.67ab 43.06b 9.46b 7.51b 30.52b 61.61b 7.08b 3.97b 10.32b 16.66ab 5.79ab 16.20b 0.071ab 0.15b 6.97a 12.44ab
HA6 55.36a 48.56a 10.61a 8.27a 32.53a 63.58a 6.94a 4.20a 11.08a 17.71a 7.40a 17.20a 0.072a 0.18a 6.97a 13.79a
CV (%) 3.78 5.38 0.76 2.78 0.66 0.41 3.41 6.28 4.43 1.17 4.44 3.15 6.28 2.60 1.26 1.33
Level of
significance ** ** ** ** ** ** ** ** ** ** ** ** ** ** ** **
Legend: HA = Humic acid
** indicates significance at 1 % level
Table 4.8. Effect of cowdung on the N, P, K , S, Ca, Mg, B and Na uptake of T. aman rice cv. BRRI dhan39
Treatments Nitrogen
(%)
Phosphorus
(%)
Potassium
(%)
Sulphur
(%)
Calcium
(%)
Magnesium
(%)
Boron
(µg g-1
)
Sodium
(µg g-1
)
Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw
CD0 46.90c 36.90b 8.27c 7.05b 29.60c 57.40b 5.86b 3.09b 8.00c 13.81c 5.38b 15.93b 0.058b 0.14b 5.20b 9.41c
CD5 50.74b 43.04a 8.99b 7.27ab 30.58b 60.25ab 6.52a 3.45ab 9.59b 15.35b 5.39b 15.84b 0.064ab 0.17a 6.07ab 11.01b
CD10 53.59a 43.88a 9.55a 7.82a 31.28a 61.98a 6.66a 4.10a 10.39a 17.00a 6.57a 16.59a 0.069a 0.17a 6.63a 12.27a
CV (%) 3.78 5.38 0.76 2.78 0.66 0.41 3.41 6.28 4.43 1.17 4.44 3.15 6.28 2.60 1.26 1.33
Level of
significance ** ** ** ** ** ** ** ** ** ** ** ** ** ** ** **
Legend: CD= Cowdung
** indicates significance at 1 % level
Table 4.9. Interaction effect of different doses of PGR (humic acid) and cowdung on N, P, K , S, Ca, Mg, B and Na uptake of T. aman rice
(cv. BRRI dhan39)
Treatments
Nitrogen
(%)
Phosphorus
(%)
Potassium
(%)
Sulphur
(%)
Calcium
(%)
Magnesium
(%)
Boron
(µg g-1
)
Sodium
(µg g-1
)
Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw Grain Straw
T0
HA0CD0
32.67e 25.43f 0.20f 0.09e 0.04f 0.84 0.16bc 0.02 4.93e 8.00g 3.10e 14.12e 0.036c 0.11f 2.43i 3.12
T1
HA0CD5 44.47d 34.50e 0.25bcd 0.13d 0.74e 1.05 0.15c 0.04 6.50d 11.91f 4.63d 15.15d 0.050bc 0.14de 4.37h 7.34
T2
HA0CD10 46.50d 36.70e 0.23e 0.15c 0.85b 1.07 0.17ab 0.05 8.30c 15.45e 4.70d 15.60cd 0.061ab 0.19ab 5.10g 8.91
T3
HA3CD0 53.73bc 41.10d 0.23de 0.17b 0.76de 1.15 0.15c 0.07 8.61c 16.00d 6.10c 16.27bc 0.068ab 0.16cd 6.37f 11.21
T4
HA3CD5 52.87c 45.80bc 0.23e 0.17bc 0.95a 1.01 0.19a 0.07 11.15ab 16.79c 4.60d 15.44cd 0.070a 0.17bc 7.23c 12.40
T5
HA3CD10 57.40a 42.27cd 0.24cde 0.17b 0.77d 1.33 0.13d 0.09 11.21ab 17.21b 6.67b 16.88ab 0.075a 0.13e 7.30b 13.71
T6
HA6CD0 54.30abc 44.17cd 0.25bc 0.17b 0.80c 1.31 0.15c 0.08 10.45b 17.43b 6.93b 17.39a 0.072a 0.15d 6.80d 13.91
T7
HA6CD5 54.90abc 48.83ab 0.26b 0.18b 0.80c 1.36 0.13d 0.09 11.13ab 17.36b 6.93b 16.92ab 0.072a 0.18ab 6.60e 13.28
T8
HA6CD10 56.87ab 52.67a 0.28a 0.20a 0.81c 1.40 0.17bc 0.09 11.67a 18.33a 8.33a 17.29a 0.073a 0.19a 7.50a 14.19
CV (%) 3.78 5.38 4.32 6.41 2.95 23.36 3.61 12.31 4.43 1.17 4.44 3.15 6.28 2.60 1.26 1.33
Level of
significance ** ** ** ** ** NS ** NS ** ** ** ** ** ** ** **
Legend: HA = Humic acid, CD = Cowdung, * indicates significance at 5 % level, ** indicates significance at 1 % level,
NS indicates non significance
CHAPTER 5
SUMMARY AND CONCLUSION
An experiment was conducted at Bangladesh Agricultural University Farm
Mymensingh during the aman season of 2010 to find out the comparative effect of
PGR (humic acid) and manure (cowdung) with chemical fertilizers (N, P, K & S) on
the growth, yield and chemical composition of T. aman rice (cv. BRRI dhan39). The
experiment was laid out in randomized complete block design with three replications.
Each block was divided into 9 unit plots. The treatments were randomly distributed in
each block. The treatments were as follows: T0 (CD0+HA0), T1 (CD5+HA0), T2
(CD10+HA0), T3 (CD0+HA3), T4 (CD5+HA3), T5 (CD10+HA3), T6 (CD0+HA6), T7
(CD5+HA6) and T8 (CD10+HA6).
The treatments comprised of three levels of humic acid and three levels of organic
manures (cowdung) and
recommended doses of chemical fertilizers. The
recommended doses of chemical fertilizers applied were: Urea 150 kg ha-1
(69
kg N ha-1
), TSP 100 kg ha-1
, MOP 70 kg ha-1
, zinc sulphate 5 kg ha-1
and borax
10 kg ha -1
. The unit plot size was 4m x 2.5m and the total number of plots
was 27.
Yield contributing characters like plant height, effective tillers hill-1
, panicle length
and number of grains panicle-1
, 1000 grain weight, grain and straw yield were
significantly influenced by different treatments combination of humic acid and
cowdung along with chemical fertilizers. The results of the study clearly indicated that
plant height, number of effective tillers, panicle length, number of grains panicle-1
and
1000-grain weight were maximum in T4 treatment where humic acid and cowdung
were applied @ 3 L ha-1
and 5 t ha
-1, respectively. However, the lowest values of the
parameters were observed in T0 (control).
Similar trends of the effect of these treatments were reflected on the grain and straw
yield of BRRI dhan39. The grain and straw yields ranged from 2.57- 4.23 t ha-1
and
7.67- 10.9 t ha-1
, respectively. Where the highest grain yield (4.23 t ha-1
) was found in
T4 and T8 when the lowest (2.57 t ha-1
) was found at T0 (control). The highest straw
yield (10.9 t ha-1
) was found in the combination of humic acid and cowdung in T4 and
T5 when the lowest (7.67 t ha-1
) was found at T0 (control).
Nutrient content in both grain and straw of T. aman rice (cv. BRRI dhan39) were
significantly and insignificantly influenced by the application of humic acid and
cowdung along with recommended doses of chemical fertilizers. The contents of N,
P, K, S, Ca, Mg, B and Na in grain ranged from 1.20 to 1.44%, 0.20 to 0.28%,
0.04 to 0.95% , 0.13 to 0.19%, 0.08 to 0.28%, 0.13 to 0.22%, 15.13 to 17.44µg
g-1
, 93.0 to 176.33 µg g-1
and in straw 0.35 to 0.97%, 0.09 to 0.20%, 0.84 to
1.40%, 0.02 to 0.09%, 0.35 to 0.76%, 0.51 to 0.81%, 15.58 to 17.41µg g-1
,
180.57 to 309.03µg g-1
, respectively. The highest N content in grain was 1.44% in
T1 and in straw, it was 0.97% in T8; phosphorus content in grain was 0.28% and in
straw 0.2% in T8; potassium content was in grain 0.95% in T1; and in straw 1.4% in
T8; sulphur content in grain was 0.19% in T4; and in straw 0.09% in T8; calcium
content was in grain 0.28% in T4, T5, T6, T7, T8 and 0.76% in straw in T8; magnesium
was 0.22% in grain and 0.81% in straw; boron content in grain 17.44 µg g-1
and
straw 17.41µg g-1
, sodium in grain 176.33µg g-1
and straw 309.33µg g-1
in T4 and the
treatment T0 gave the lowest content of all parameters studied.
Based on these observation, it may be inferred that incorporation of humic acid @ 3 L
ha-1
along with the recommended dose of chemical fertilizers showed better
performance in yield and yield contributing characters and nutrient content than
cowdung (CD) even at double the dose (CD 5 t ha-1
) in combination with
recommended dose of chemical fertilizers can be better in aman season. However
application of humic acid @ 3 L ha-1
can be better choice. It is therefore concluded
from the present study that the incorporation of humic acid @ 3 L ha-1
plus cowdung
@ 5 t ha-1
with recommended doses of chemical fertilizers may be used for obtaining
higher yield of aman rice particularly BRRI dhan39.
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Appendix1. Meteorological data of the experiment period (August to December, 2004) at BAU Farm, Mymensingh
Month
Air** Pressure
(mbs)
**Air temperature (
0C )
**Dew point
(0C)
"Humidi ty *Rain fall (mm)
**Wind
Speed
(kmph)
*Sun
shine (hrs)
*Evaporation ration (mm)
**Water ration
(mm)
**Soil temperature (°C) Depth
Max. Min. Av. 05
cm.
10
cm
20
cm
30
cm
50
cm
August 999.6 32.03 26.42 29.22 26.03 84.55 253.4 9.88 164.1 147.4 30.3 31.2 31.6 31.2 29.5 30.1
September 1004.5 30.01 25.30 27.66 25.57 91.30 269.7 8.32 65.1 76.9 28.3 29.1 29.2 29.0 27.9 28.8
October 1010.4 30.38 22.34 26.36 23.58 84.17 488.3 4.51 200.9 89.5 27.5 28.2 28.6 28.8 27.2 27.9
November 1002.1 28.98 16.87 22.93 18.90 82.86 00.0 2.29 224.7 79.4 24.3 24.3 14.8 25.4 25.3 25.6
December 1013.0 26.23 13.97 20.10 15.87 81.61 18.0 2.28 197.1 68.4 20.6 21.0 21.7 22.1 21.2 22.8
* Monthly total,
**Monthly average
Source : Weather yard, department of irrigation and water management Bangladesh Agricultural University, Mymensingh.
Appendix 2. Analysis of variance data on effect of PGR (humic acid) and cowdung on the growth, yield and yield
contributing characters of T. aman (cv. BRRI dhan39)
Source of
variance
df Mean sum. of square
Plant
height
(cm)
Panicle
length
(cm )
Total
tillers
hill-1
(No.)
Effective
tillers
hill-1
(No.)
Total
grains
panicle-1
(No.)
Filled
grains
panicle-1
(No.)
1000-
grain
weight
(g)
Grain
weight
(kg)
Straw
weight
(kg)
Replication 2 2.941 0.963 0.687 0.029 31.593 0.704 0.004 0.043 0.034
Factor- A
(HA) 2 231.829** 68.306** 13.363** 10.506** 9069.148** 8242.926** 3.924** 3.968** 13.268**
Factor –B (CD)
2 28.059NS 12.241** 3.074** 3.409** 477.815** 320.704NS 0.103** 0.388** 1.003*
AB 4 31.343* 8.328** 1.141* 1.152* 512.593* 456.648** 0.008** 0.134** 0.528*
Error 16 9.346 1.425 0.337 0.295 86.301 143.954 0.003 0.027 0.153
* = Significant at 5% level
** = Significant at 1% level
NS = Not significant
Appendix 3. Analysis of variance data on effect of PGR (humic acid) and cowdung on nutrient content in grain of T.
aman (cv. BRRI dhan39)
Source of
variance
df Mean sum. of square
Nitrogen
(%)
Phosphorus
(%)
Potassium
(%)
Sulphur
(%)
Calcium
(%)
Magnesium
(%)
Boron
(mg g-1
)
Sodium
(mg g-1
)
Replication 2 0.0001 0.0001 0.002 0.0001 0.003 0.005 0.577 82.847
Factor- A
(HA) 2 0.007** 0.004** 0.086** 0.0001** 0.021** 0.007** 1.644** 1942.892**
Factor –B (CD)
2 0.02** 0.001** 0.251** 0.0001NS 0.013** 0.003* 1.582** 2248.48**
AB 4 0.016** 0.001** 0.251** 0.002** 0.004* 0.002NS 0.969NS 1676.092NS Error 16 0.0001 0.0001 0.0001 0.0001 0.001 0.001 0.367 28.07
* = Significant at 5% level
** = Significant at 1% level
NS = Not significant
Appendix 4. Analysis of variance data on effect of PGR (humic acid) and cowdung on nutrient content in straw of T.
aman (cv. BRRI dhan39)
Source of
variance
df Mean sum. of square
Nitrogen
(%)
Phosphorus
(%)
Potassiu
m (%)
Sulphur
(%)
Calcium
(%)
Magnesium
(%)
Boron
(mg g-1
)
Sodium
(mg g-1
)
Replication 2 0.002 0.0001 0.065 0.0001 0.022 0.002 0.181 39.112
Factor- A
(HA) 2 0.477** 0.009** 0.31** 0.007** 0.125** 0.107** 0.418** 4205.689**
Factor –B
(CD) 2 0.059** 0.002** 0.069** 0.001** 0.065** 0.029** 3.772 NS 8110.252**
AB 4 0.002** 0.001** 0.033NS 0.0001NS 0.001 NS 0.004 NS 0.316 NS 14494.25**
Error 16 0.0001 0.0001 0.075 0.0001 0.001 0.002 0.499 8.278
* = Significant at 5% level
** = Significant at 1% level
NS = Not significant
Appendix 5. Analysis of variance data on effect of PGR (humic acid) and cowdung on nutrient uptake in grain of T.
aman (cv. BRRI dhan39)
Source of
variance
df Mean sum. of square
Nitrogen
(kg ha-1
)
Phosphorus
(kg ha-1
)
Potassium
(kg ha-1
)
Sulphur
(kg ha-1
)
Calcium
(kg ha-1
)
Magnesium
(kg ha-1
)
Boron
(kg ha-1
)
Sodium
(kg ha-1
)
Replication 2 4.751 0.041 0.656 0.152 0.778 0.191 0.0001 0.108
Factor- A
(HA) 2 572.388** 35.972** 38.201** 11.932** 52.378** 23.848** 0.002** 27**
Factor –B
(CD) 2 101.418** 3.699** 6.418** 1.623** 13.389** 4.201** 0.0001** 4.69**
AB 4 44.366** 1.045** 0.061** 3.143** 1.433** 1.819** 0.0001** 1.243**
Error 16 3.632 0.005 0.04 0.046 0.171 0.066 0.0001 0.006
* = Significant at 5% level ** = Significant at 1% level
NS = Not significant
Appendix 6. Analysis of variance data on effect of PGR (humic acid) and cowdung on nutrient uptake in straw of T.
aman (cv. BRRI dhan39)
Source of
variance
df Mean sum. of square
Nitrogen
(kg ha-1
)
Phosphorus
(kg ha-1
)
Potassium
(kg ha-1
)
Sulphur
(kg ha-1
)
Calcium
(kg ha-1
)
Magnesium
(kg ha-1
)
Boron
(kg ha-1
)
Sodium
(kg ha-1
)
Replication 2 10.745 0.317 0.043 0.086 0.01 1.437 0.0001 0.015
Factor- A
(HA)
2 622.489** 8.294** 208.259** 7.933** 89.875** 11.376** 0.002** 137.261**
Factor –B (CD)
2 130.707** 1.428** 48.054** 2.37** 22.856** 1.521** 0.003** 18.456**
AB 4 24.306** 0.344** 9.645** 0.356** 10.421** 0.981** 0.003** 6.902** Error 16 4.925 0.042 0.06 0.05 0.033 0.258 0.0001 0.001
* = Significant at 5% level
** = Significant at 1% level
NS = Not significant