1) The study examined the effect of different amounts of worms (50g, 100g, 150g) on the degradation of organic matter in cattle manure during vermicomposting.
2) Results showed that organic matter degradation occurred faster with 150g of worms compared to lower amounts.
3) Over 45 days, the chemical composition of the vermicompost was altered as organic matter and carbon decreased while nitrogen increased in all treatments.
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*Download the file to view the presentation with its effects.
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HERE IS THE LINK:
http://www.slideshare.net/shayangreen/solution-for-introduction-to-environment-engineering-and-science-2nd-edition-by-gilbert-m-masters
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Proceedings available at: http://www.extension.org/67580
The use of wet distiller's grains with solubles (WDGS) in feedlot diets has increased as a result of the growing U.S. ethanol industry. However, few studies have evaluated the use of WDGS in finishing diets based on steam-flaked corn (SFC), the processing method used extensively in the Southern Great Plains. The effects of corn processing method and WDGS on enteric methane (CH4) production, carbon dioxide (CO2) production and energy metabolism were evaluated in two respiration calorimetry studies. In Exp. 1, the effects of corn processing method (SFC or dry rolled corn -- DRC) and WDGS inclusion (0 or 30% of diet dry matter- DM) were studied using a 2 x 2 factorial arrangement of treatments and four Jersey steers in a 4 x 4 Latin square design. In Exp. 2, the effects of WDGS inclusion rate (0, 15, 30, or 45% of diet DM) on CH4 and CO2 production were measured in a 4 x 4 Latin square design. Results indicate that cattle consuming SFC-based diets produce less enteric CH4 and retain more energy than cattle fed DRC-based diets. When dietary fat levels were held constant, dietary inclusion of WDGS at 15% of diet DM did not affect enteric CH4 production, WDGS inclusion at 45% of diet DM significantly increased enteric CH4 production and WDGS inclusion at 30% of diet DM had variable effects on enteric CH4 production.
Francisco Cabezon - Heat Stress Alleviation in Lactating Sows by Dietary Beta...John Blue
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Solution for Introduction to Environment Engineering and Science 3rd edition ...shayangreen
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IMPORTANT NOTE:IF YOU WANT TO USE THIS SOLUTION YOU MUST DOWNLOAD THE SECOND EDITION AS WELL.
SOLUTION TO SECOND EDITION IS IN MY PROFILE TOO.
HERE IS THE LINK:
http://www.slideshare.net/shayangreen/solution-for-introduction-to-environment-engineering-and-science-2nd-edition-by-gilbert-m-masters
Effect of Fractionation and Pyrolysis on Fuel Properties of Poultry LitterLPE Learning Center
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Proceedings available at: http://www.extension.org/67633
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Effect of the amount of worms on Organic matter degradation in cattle manure - Akib Sumon
1.
2. EFFECT OF THE AMOUNT OF WORMS ON
ORGANIC MATTER DEGRADATION IN CATTLE
MANURE
AKIBUR RAHMAN
ID. No.: 18AS-JJ- 12M
Reg. No.: 40313, Session: 2012-2013
Department of Animal Science
Bangladesh Agricultural University,
Mymensingh-2202
3. Supervisor
Dr. Md. Mukhlesur Rahman
Professor
Department of Animal Science
Bangladesh Agricultural University
Co-supervisor
Dr. Md. Abul Hashem
Professor
Department of Animal Science
Bangladesh Agricultural University
SUPERVISORY COMMITTEE
5. INTRODUCTION
• Vermicomposting is a process that involves
chemical, physical, and biological
transformation of solid organic materials
(agricultural residues of plant and animal
origin) through the use of worms and
microorganisms.
• There are 1800 species of earthworm present in
the. But the most commonly used is Eisenia
fetida, commonly known as the “compost
worm”, manure worm and red worm.
6. Vermicompost is rich in nitrogen, Phosphorus & potassium.
Nitrogen 2 - 3%
Phosphorus 1.55 - 2.25%
Potassium 1.85 - 2.25% and
Micronutrients, beneficial soil microbes and plant growth
hormones and enzymes.
Figure: Vermicomposting worms
INTRODUCTION (contd.)
7. OBJECTIVES
To compare the efficiency of OM degradation
among different amounts of worms used for
vermicomposting.
To know the efficiency of earthworm activity
during decomposition of cow manure with
different amounts of worms used.
To know the chemical composition of
vermicompost produced from cattle manure.
11. Chemical composition of raw cattle manures:
T1=Vermicomposting of cattle manure with 50 g worms, T2 =
Vermicomposting of cattle manure with 100 g worms, T3 =Vermicomposting
of cattle manure with 150 g worms.
RESULTS
Parameters T1 T2 T3
DM
20.99±0.61 20.79±0.76 21.05±0.51
OM 16.12 ±0.78 16.21 ±0.67 16.19 ±0.66
Ash
2.67 ±0.16 2.81 ±0.24 2.76 ±0.19
OC
11.32 ± 0.30 11.25 ± 0.10 11.28 ± 0.45
TKN
1.26 ± 0.08 1.18 ± 0.09 1.32 ± 0.08
CF
4.43 ±0.05 4.32 ±0.06 4.23 ±0.06
C/N
16.26 ± 0.14 16.33 ± 0.10 16.36 ± 0.19
PH
8.31 ± 0.09 8.45 ± 0.08 8.27± 0.09
12. DM alteration over time (from 0 to 45 days)
T1=Vermicomposting of cattle manure with 50 g worms, T2 = Vermicomposting of
cattle manure with 100 g worms, T3 =Vermicomposting of cattle manure with 150 g
worms.
RESULTS (contd…)
DI Treatments Mean Level of significance
T1 T2 T3 Treat DI T*DI
0 20.99±0.61 20.79±0.76 21.05±0.51 20.94±0.63
<.0001 <.0001 0.0205
15 21.13 ±0.88 22.08±0.06 23.43±0.82 22.21±0.58
30 23.71 ±0.55 24.41±0.56 25.43±0.46 24.51±0.52
45 25.36 ±1.20 26.71±0.21 28.46 0.90 28.84±0.69
13. OM alteration over time (from 0 to 45 days)
T1=Vermicomposting of cattle manure with 50 g worms, T2 = Vermicomposting
of cattle manure with 100 g worms, T3 =Vermicomposting of cattle manure with
150 g worms
RESULTS (contd…)
DI Treatments Mean Level of significance
T1 T2 T3 Treat DI T*DI
0 16.12 ± 0.78 16.21±0.67 16.19±0.66 16.17±0.70
p<.0001 p<.0001 0.0651
15 15.71 ±0.98 15.49±0.95 15.32±0.70 15.50±0.87
30 15.48 ± 0.71 15.23±0.27 15.16±0.40 15.29±0.46
45 14.60 ± 1.29 14.38±0.15 14.11±0.81 14.36±0.75
14. Ash alteration over time (from 0 to 45 days)
T1=Vermicomposting of cattle manure with 50 g worms, T2 = Vermicomposting
of cattle manure with 100 g worms, T3 =Vermicomposting of cattle manure with
150 g worms
RESULTS (contd…)
DI Treatments Mean Level of significance
T1 T2 T3 Treat DI T*DI
0 2.67±0.16 2.81 ±0.24 2.76 ±0.19 2.74±0.19
P<.0001 P<.0001 P<.0011
15 2.52 ±0.11 2.48 ±0.04 2.31±0.11 2.43±0.08
30 2.43 ±0.15 2.10±0.04 2.16 ±0.07 2.23±0.09
45 1.95 ±0.08 2.03 ±0.06 1.84 ±0.09 1.97±0.07
15. RESULTS (contd…)
DI Treatments Mean Level of significance
T1 T2 T3 Treat DI T*DI
0 11.32±0.31 11.25±0.10 11.28 ±0.45 11.28±0.28
P<.0001 P<.0001 0.0006
15 11.06±0.11 11.03±0.05 10.96±0.41 10.68±0.18
30 10.63±0.16 10.53±0.15 10.17±0.22 10.44±17
45 10.44±0.11 10.41±0.09 9.91 ±0.47 10.25±0.22
T1=Vermicomposting of cattle manure with 50 g worms, T2 = Vermicomposting
of cattle manure with 100 g worms, T3 =Vermicomposting of cattle manure with
150 g worms
OC alteration over time (from 0 to 45 days)
16. TKN alteration over time (from 0 to 45 days):
T1=Vermicomposting of cattle manure with 50 g worms, T2 = Vermicomposting
of cattle manure with 100 g worms, T3 =Vermicomposting of cattle manure with
150 g worms
RESULTS (contd…)
DI Treatments Mean Level of significance
T1 T2 T3 Treat DI T*DI
0 1.26 ±08 1.18 ± 0.09 1.32 ± 0.08 1.25 ±08
0.0001 P<.0001 P<.0001
15 1.61 ±0.04 1.34 ±0.05 1.40 ±0.08 1.45±0.05
30 1.82 ±0.08 1.56 ±0.06 1.85 ±0.09 1.74±0.07
45 1.98 ±0.06 2.38 ±0.81 2.95 ±0.07 1.77±0.31
17. CF alteration over time (from 0 to 45 days)
T1=Vermicomposting of cattle manure with 50 g worms, T2 = Vermicomposting
of cattle manure with 100 g worms, T3 =Vermicomposting of cattle manure with
150 g worms
RESULTS (contd…)
DI Treatments Mean Level of significance
T1 T2 T3 Treat DI T*DI
0 4.43 ±0.04 4.32 ±0.06 4.23 ±0.06 4.32 ±0.05
P<.0001 P<.0001 P<.0001
15 3.16 ±0.05 2.94 ±0.06 2.86 ±0.16 2.98±0.09
30 2.99 ±0.07 1.82 ±0.07 1.56 ±0.12 2.12±0.08
45 2.38 ±0.10 0.72 ±0.08 0.66 ±0.06 1.25±0.08
18. C/N alteration over time (from 0 to 45 days)
T1=Vermicomposting of cattle manure with 50 g worms, T2 = Vermicomposting
of cattle manure with 100 g worms, T3 =Vermicomposting of cattle manure
with 150 g worms
RESULTS (contd…)
DI Treatments Mean Level of significance
T1 T2 T3 Treat DI T*DI
0 16.26±0.13 16.33±0.10 16.36±0.19 16.31±0.14
P<.0001 P<.0001 P<.0001
15 15.98±0.24 15.87±0.45 15.69±0.25 15.84±0.23
30 14.40±0.13 13.81±0.47 13.23±0.21 13.81±0.27
45 13.26±0.13 12.97±0.28 11.91±0.15 12.71±0.18
19. pH alteration over time (from 0 to 45 days)
T1=Vermicomposting of cattle manure with 50 g worms, T2 = Vermicomposting
of cattle manure with 100 g worms, T3 =Vermicomposting of cattle manure with
150 g worms
RESULTS (contd…)
DI Treatments Mean Level of significance
T1 T2 T3 Treat DI T*DI
0 8.31±0.09 8.45 ± 0.08 8.27± 0.09 8.34±0.08
0.0450 P<.0001 0.5711
15 8.14 ± 0.05 8.76 ±0.05 8.72 ±0.03 8.70±0.04
30 9.07 ±0.11 9.17 ±0.07 8.23 ±0.05 8.82±0.7
45 9.01 ±0.05 9.10 ±0.05 8.47 ±0.20 8.76±0.10
20. CONCLUSION
Organic matter degradation rate is faster in
vermicomposting of cattle manure which
treated with 150 gm of worms than the
vermicomposting of cattle manure which
treated with 100 gm and 50 gm of worms
respectively.
45 days is enough for vermicomposting of cattle
manure.