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Int. J. Life. Sci. Scienti. Res. March 2018
Copyright © 2015-2018| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1670
Rapid Composting of Different Wastes with
Yash Activator Plus
Mohammad Hafeez1*
, Pramila Gupta2
, Yash Pal Gupta3
1
Microbiologist, Yash Krishi Takniki Evam Vigyan Kendra, Allahabad, Uttar Pradesh, India
2
Secretarty, Yash Krishi Takniki Evam Vigyan Kendra, Allahabad, Uttar Pradesh, India
3
Chairman, Yash Krishi Takniki Evam Vigyan Kendra, Allahabad, Uttar Pradesh, India
*
Address for Correspondence: Mr. Mohammad Hafeez, Microbiologist, Yash Krishi Takniki Evam Vigyan Kendra,
Allahabad, Uttar Pradesh, India
Received: 12 Dec 2017/Revised: 15 Jan 2018/Accepted: 22 Feb 2018
ABSTRACT- Microbial composting play an important role in the recycling of different processing wastes and the
compost generated by bio-conversion of wastes offers several benefits such as enhanced soil fertility and soil health that
can lead to increased agricultural productivity, improved soil biodiversity, reduced ecological risks and a healthier
environment. The present experiment was conducted in Plastic pots, which were filled with the different wastes, namely
Sugarcane waste, Plants waste, Flower waste, Mausmi waste and Mixed waste, which was inoculated by Yash Activator
Plus (2% w/w) with a set control pot of each. The results of this study revealed that with Yash Activator Plus, the
temperature was increased rapidly at 20 days of composting which were 50, 52, 58, 54 and 54˚C. Control treatments
increased temperature up to 45, 44, 48, 46, and 46˚C respectively. The total loss of dry matter content at the end of
composting amounted to be 37.73, 39.67, 52.94, 51.25 and 40% from the initial amount of Sugarcane waste, Plants
waste, Flower waste, Mausmi waste and Mixed waste respectively. The maximum and minimum dry matter contents
were decreased in flower waste and sugarcane waste respectively. Increased temperature enhanced the process of
composting rapidly due to the thermophilic microorganisms, which reduces the time of composting. On the basis of this
study, we can conclude that the mixed consortia of mesophilic and thermophilic microorganisms increased the process
of composting, which reduces the time of degradation of different wastes.
Key-words- Compost, Microbial composting, Different waste, Yash Activator Plus
INTRODUCTION
"Yash Activator Plus" is a very effective microbial
consortium for rapid composting. It is a mixture of
culture of mesophilic and thermophilic microorganisms
specifically for accelerating the composting of organic
waste. It contains cultures of Bacteria and fungi along
with enzymes, which facilitate bio conversion of organic
waste into a stabilized end product called “compost. Use
of this microbial consortium for rapid composting: The
microbiology of composting is very complex. It involves
consortium of fungi and bacteria Actinomyces for bio
conversion of organic waste into end product for various
uses. Microbial growth in composting depends upon so
many factors. Carbon and nitrogen sources are the most
critical in terms of bio-degradability of the waste/
biomass. Microbial composting refers to microbiological
process which converts waste materials into organic
manure, which are rich in plant nutrients and humus [1]
.
Aeration and moisture control are the main key operating
parameters for operating the windrow compost plant.
Access this article online
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DOI: 10.21276/ijlssr.2018.4.2.9
Addition of specialized bio-culture consortium is
proposed for increasing composting activity has great use.
Microbial composting gets advantages not only by
reducing the volumes of waste materials but also by
recycling of nutrients and organic matter to improve the
soils. Aerobic decomposition process also generates
fewer greenhouse gases as compared to land filling.
Thermophilic composting associated with disadvantages
of long duration process by which loss of the nutrient
occurs during the process and it needed frequent turning
to maintain aerobic.
Microbial populations are the active components of
biodegradation processes and conversion during
composting. Thus, compost quality is directly related to
the composition and sequence of microbial communities
in the process, being the fungi and bacteria that perform
the degradation of organic matter [2]
. Composting of
agricultural waste is an alternative trail to alleviate the
negative impact of its accumulation and/or avoid the
environmental pollution. Abou et al. [3]
concluded that
recycling agriculture wastes is a must for environment as
well as economical saving. This recycling will not only
increase agricultural production but also will improve its
quality. Composting is considered a biological process in
which microorganisms convert organic residues into
soil-like material called compost. El-Haggar et al. [4]
and
Geisel [5]
reported windrows composting is a commonly
used processing method. The microbial decomposition of
RESEARCH ARTICLE
Int. J. Life. Sci. Scienti. Res. March 2018
Copyright © 2015-2018| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1671
organic wastes is controlled by environmental factors
affecting microbial activity within the windrow piles.
There are some factors affecting composting and directly
influence the rate of decomposition, such as particle size,
moisture content, aeration, temperature, C/N ratio and
pH. Therefore, intensive management of the composting
process by turning and moisture addition is likely to
affect the N fertilizer value of the mature compost.
Microbial inoculation of compostable material could
allow the inoculated microorganisms like (Streptomyces
aurefaciens, Trichoderma viride, Trichoderma
harzianum, Thermomyces lanuginosus, Aspergillus niger,
Bacillus subtilis, Bacillus sphaericus, B. licheniformis,
Bacillus stearothermophilus) to dominate over the
indigenous micro-biota and successfully develop
appropriate degradation [6]
. The important advantages of
composting are the reduction of the wastes, the
destruction of weed seeds and of pathogenic
microorganisms [7]
. Additional benefits of composting as
mechanism for waste management are production of
valuable soil amendments, low operation costs, easy to be
applied in most of developing countries, and
encouragement of environmentally friendly practices such
as reduction of the emission of greenhouse gases,
promote the efficiency of fertilizer application [8]
.
Microbial composting technologies for agriculture and
other waste management are very significant to meet the
need of developing countries. Therefore, the present work
aims to rapid composting of agricultural and other wastes
through the microbial composting process using Yash
Activator Plus.
MATERIALS AND METHODS
Place of work- The present study was conducted in the
Yash Krishi Takniki Evam Vigyan Kendra, Allahabad,
Uttar Pradesh, India in the duration of 2017.
Experimental details- The experiment was conducted
in Plastic pots, which were filled with the different
wastes, namely Sugarcane waste, Plant waste, Flower
waste, Mausmi waste and Mixed waste with a set of
control pot and 3 replicates of each. All the weighted
amount of wastes were inoculated with the Yash
Activator plus, which are a mixed culture of Mesophilic
and Thermophilic microbial consortia. Inoculum cultures
were inoculated with the rate of 2% w/w. The moisture
content was maintained at 50-60% and turning of material
at one week interval for proper aeration were achieved.
The data was taken before and after inoculation of
cultures at the interval of 20 days up to 60 days. The data
were recorded during the course of study at an
appropriate time interval.
RESULTS AND DISCUSSION
Composting generally take place within two temperatures
ranges known as mesophilic (10-40⁰C) and thermophilic
(over 40⁰C). Although mesophilic temperatures allow
effective composting, experts suggest maintaining
temperatures between 43⁰C and 65⁰C. The thermophilic
composting is desirable, because they destroy more
pathogens, weed seeds and fly larvae in the composting
materials. The experimental results showed that the
temperature of the waste materials before inoculation was
34, 35, 37, 35 and 35 ˚C namely Sugarcane waste, Plant
waste, Flower waste, Mausmi waste and Mixed
waste respectively. Temperature variations during the
composting process are shown in Table 1. The data
obtained at 20 days of inoculation with Yash Activator
Plus the temperature were increased rapidly at 20 days of
composting which were 50, 52, 58, 54 and 54˚C with
comparison to controls which were 45, 44, 48, 46, and
46˚C respectively. The temperature of composting
decreased slowly at 47, 48, 55, 51 and 50˚C respectively
at 40 days of composting and at 60 days almost the
temperature were stabilized, which were 35, 36, 37, 35
and 36˚C with comparison to controls which were 37, 38,
40, 38 and 37˚C respectively. Temperature, which is an
important factor in composting process, its influences on
the activity and diversity of microorganisms [9]
. Liang et
al. [10]
reported that the enhancement of microbial
activities was induced by increasing temperature.
The results indicate that the maximum temperature
increased in flower waste which was 58˚C at 20 days of
composting this increased temperature rapidly and
enhanced the composting process in comparison to
natural composting. This rising of temperature during
composting was due to the microorganism activity in the
waste. Kanotra S and Mathur [11]
reported that fungi,
bacteria, and actinomycetes play unique and important
roles during the composting, mixed cultures of
microorganisms enhanced the rate of lignocelluloses
degradation, due to their synergistic activity through
utilization of intermediate degradation products. The
results can be correlated with the findings of El-Meniawy
[12]
; Abdel-Aziz and Al-Barakah [13]
; Eida [14]
. The
maturity of composting stage was started with the
temperature decreased to normal air daily temperature
and remains almost constant with turning of the piles [15]
.
Therefore, this is considered as a good indicator for the
end of the biodegradation phase in which the compost
achieves maturity [16]
. The decrease in temperature after
peak value was related to the decrease in microbial as
well as enzymatic activities. The results are with the
agreements of Noguerira et al. [17]
study.
Int. J. Life. Sci. Scienti. Res. March 2018
Copyright © 2015-2018| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1672
Table 1: Temperature variations during the composting process of different waste materials
Waste materials
Temperature variations (˚C)
Before
Inoculation
At 20 days At 40 days At 60 days
Control Treated Control Treated Control Treated
Sugarcane waste 34.0 45.0 50.0 42.0 47.0 37.0 35.0
Plant waste 35.0 44.0 52.0 42.0 48.0 38.0 36.0
Flower waste 37.0 48.0 58.0 45.0 55.0 40.0 37.0
Mausmi waste 35.0 46.0 54.0 44.0 51.0 38.0 35.0
Mixed Waste 35.0 46.0 54.0 43.0 50.0 37.0 36.0
Fig. 1: Different waste materials before inoculation of Yash Activator Plus
Dry matter content results of the different wastes
treatments showed that there are decreased gradually
during the whole period of composting, which is shown
in Table 2. The initial amounts of different waste were
2650, 3000, 3400, 4000 and 3200 gm respectively. The
maximum reductions of dry matter are achieved at 20
days data of composting stage, which was characterized
by the maximum microbial activity. The total loss of dry
matter content at the end of composting amounted to be
37.73, 39.67, 52.94, 51.25 and 40 % from the initial
amount, which are Sugarcane waste, Plant waste, Flower
waste, Mausmi waste and Mixed waste respectively. The
maximum and minimum dry matter content was
decreased in flower waste and sugarcane waste, which
were 52.94 and 37.73 % respectively. These results can
be correlated with those of Wallace [18]
and Kuok et al.
[19]
. The turning effects on the microbial consortia during
the composting enhanced the degradation of organic
matter by transferring the undamaged organics at
unfavorable temperatures to favorable temperatures, to
allow degradation by microorganisms that degrade more
vigorously reported by Kuok et al. [19]
.
Table 2: Effect of Yash Activator plus on dry matter of different waste materials during composting
Waste materials
Weight of the dry matter (gm)
Before
Inoculation
At 20 days At 40 days At 60 days
Control Treated Control Treated Control Treated
Sugarcane waste 2,650 2,313 2,005 2,050 1,830 1905 1,650
Plant waste 3,000 2,410 2,205 2,235 2,005 2,150 1,810
Flower waste 3,400 2,000 1,742 1,860 1,645 1,860 1,600
Mausmi waste 4,000 2,610 2,400 2,330 2,130 2,220 1,950
Mixed Waste 3,200 2,660 2,260 2,440 2,165 2,220 1,920
Int. J. Life. Sci. Scienti. Res. March 2018
Copyright © 2015-2018| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1673
Fig. 2: Different waste materials after composting with Yash Activator Plus at 60 days
CONCLUSIONS
The main objective of the research included the
characterization and study of the wastes generated in
daily life. We could get an idea that the main constituent
in the waste was the biodegradable fraction, which
included the Flower, Mausmi, market wastes like raw
fruits, vegetables, leaves etc. thereby making it ideal for
utilizing for composting rather than the land spreading
utilized in the dump yard. The present experimental
results indicate that the rapid degradation of different
wastes treated with Yash Activator Plus compared to
control treatments. This may be due to the increase of
microorganism's activity in biodegradation and more
effective way of biodegradation of waste. Our results
showed that the microbial consortium offered a faster
medium of treatment or recycling where results were
obtained in a span of 60 days.
REFERENCES
[1] Sharma S, Mathur RC, and Vasudevan P. Composting
silkworm culture waste. Compost Sci Util, 1999; 7:74-81.
[2] Palm CA, Gachengo CN, Delve RJ, Cadisch G, and Giller
KE. Organic inputs for soil fertility management in tropical
agroecosystems: Application of an organic resource
database. Agriculture Ecosystems and Environement,
2004; 83:27-42.
[3] Abou Hussein ShD, and Sawan M. The Utilization of
Agricultural Waste as the Environmental Issues in Egypt
(A Case Study). J. of Applied Sci. Res., 2010; 6(8):
1116-1124.
[4] El-Haggar SM, Mounir G, and Gennaro L. Agricultural
waste as an energy source indeveloping countries, a case
study in Egypt on the utilization of agricultural waste
through complexes. International Centre for Science and
High Technology (ICS).United Nations Industrial
Development organization (UNODO), 2004; pp: 1-10.
[5] Geisel PM. Compost in a Hurry. Compost in Hurry
University of California, Agriculture and neutral recourses,
2001; 8037:1-4.
[6] Badr El-Din, SMS, Attia M, and Abo Sedera SA. Field
assessment of composts produced by highly effective
cellulolytic microorganisms. Biol. Fertil. Soils, 2000;
32:35 -40.
[7] Bernal MP, Albur querque JA, and Moral R. Composting
of animal manures and hemical criteria for compost
maturity assessment. A review Bioresource Technol. 2009;
100: 5444-5453.
[8] Hoornweg DL, Thomas and Otten. Composting and its
applicability in developing countries. The International
Bank for Reconstruction and Development/ The World
Bank, Washington, D.C., USA, 2000.
[9] Finstein MS, Miller FC, and Strom PF. Waste treatment
composting as a controlled system. Biotechnol, 1986;
8:363-398.
[10]Liang C, Das KC, McClendon RW. The influence of
temperature and moisture contents regimes on the aerobic
microbial activity of a biosolids composting blend.
Bioresour Technol, 2003; 86:131-137.
[11]Kanotra S and Mathur RS. Bioresource Technology, 1994;
47:185-188.
[12]El-Meniawy MA. Microbiological Studies on the
Production of Non- Traditional Animal Feed from
Agricultural wastes. M. Sc. Thesis, Faculty of Agriculture,
Al- Azhar University, Cairo, Egypt, 2003.
[13]Abdel-Aziz RA, and Al-Barakah FN. Composting
technology and impact of compost on soil biochemical
properties. Arab Gulf J. Scientific Res. 2005; 23(2):80-91.
[14]Eida MF. Application of biological farming principals for
producing safe vegetable crops. M. Sc. Thesis, Faculty of
Agriculture, Kafrelsheikh University, 2007.
[15]Harada Y, Inoko A, Tadaki, M, and Izawa T. Maturity
process of city refuse compost during piling. Soil Sci. and
Plant Nutr., 1981; 27:357-364.
[16]Jimenez El and Garcia VP. Evaluation of city refuse
compost during piling. Biological Wastes, 1989; 27:
55-142.
[17]Noguerira WA, Nogueira FN, and Devens DC.
Temperature and pH control in composting of coffee and
agricultural wastes. Water Sci. and Technol., 1999; 40
(1):113-119.
Int. J. Life. Sci. Scienti. Res. March 2018
Copyright © 2015-2018| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1674
[18]Wallace, PA. Compost Use in Agriculture, EB Nationwide,
2003.
[19]Kuok F, Mimoto H, and Nakasaki K. Effects of turning on
the microbial consortia and the in situ temperature
preferences of microorganisms in a laboratory-scale swine
manure composting. Bioresour Technol, 2012; 16:
421-427.
International Journal of Life Sciences Scientific Research (IJLSSR)
Open Access Policy
Authors/Contributors are responsible for originality, contents, correct
references, and ethical issues.
IJLSSR publishes all articles under Creative Commons
Attribution- Non-Commercial 4.0 International License (CC BY-NC).
https://creativecommons.org/licenses/by-nc/4.0/legalcode
How to cite this article:
Hafeez M, Gupta P, Gupta YP. Rapid Composting of Different Wastes with Yash Activator Plus. Int. J. Life. Sci. Scienti.
Res., 2018; 4(2): 1670-1674. DOI:10.21276/ijlssr.2018.4.2.9
Source of Financial Support: Nil, Conflict of interest: Nil

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Rapid composting with microbial activator

  • 1. Int. J. Life. Sci. Scienti. Res. March 2018 Copyright © 2015-2018| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1670 Rapid Composting of Different Wastes with Yash Activator Plus Mohammad Hafeez1* , Pramila Gupta2 , Yash Pal Gupta3 1 Microbiologist, Yash Krishi Takniki Evam Vigyan Kendra, Allahabad, Uttar Pradesh, India 2 Secretarty, Yash Krishi Takniki Evam Vigyan Kendra, Allahabad, Uttar Pradesh, India 3 Chairman, Yash Krishi Takniki Evam Vigyan Kendra, Allahabad, Uttar Pradesh, India * Address for Correspondence: Mr. Mohammad Hafeez, Microbiologist, Yash Krishi Takniki Evam Vigyan Kendra, Allahabad, Uttar Pradesh, India Received: 12 Dec 2017/Revised: 15 Jan 2018/Accepted: 22 Feb 2018 ABSTRACT- Microbial composting play an important role in the recycling of different processing wastes and the compost generated by bio-conversion of wastes offers several benefits such as enhanced soil fertility and soil health that can lead to increased agricultural productivity, improved soil biodiversity, reduced ecological risks and a healthier environment. The present experiment was conducted in Plastic pots, which were filled with the different wastes, namely Sugarcane waste, Plants waste, Flower waste, Mausmi waste and Mixed waste, which was inoculated by Yash Activator Plus (2% w/w) with a set control pot of each. The results of this study revealed that with Yash Activator Plus, the temperature was increased rapidly at 20 days of composting which were 50, 52, 58, 54 and 54˚C. Control treatments increased temperature up to 45, 44, 48, 46, and 46˚C respectively. The total loss of dry matter content at the end of composting amounted to be 37.73, 39.67, 52.94, 51.25 and 40% from the initial amount of Sugarcane waste, Plants waste, Flower waste, Mausmi waste and Mixed waste respectively. The maximum and minimum dry matter contents were decreased in flower waste and sugarcane waste respectively. Increased temperature enhanced the process of composting rapidly due to the thermophilic microorganisms, which reduces the time of composting. On the basis of this study, we can conclude that the mixed consortia of mesophilic and thermophilic microorganisms increased the process of composting, which reduces the time of degradation of different wastes. Key-words- Compost, Microbial composting, Different waste, Yash Activator Plus INTRODUCTION "Yash Activator Plus" is a very effective microbial consortium for rapid composting. It is a mixture of culture of mesophilic and thermophilic microorganisms specifically for accelerating the composting of organic waste. It contains cultures of Bacteria and fungi along with enzymes, which facilitate bio conversion of organic waste into a stabilized end product called “compost. Use of this microbial consortium for rapid composting: The microbiology of composting is very complex. It involves consortium of fungi and bacteria Actinomyces for bio conversion of organic waste into end product for various uses. Microbial growth in composting depends upon so many factors. Carbon and nitrogen sources are the most critical in terms of bio-degradability of the waste/ biomass. Microbial composting refers to microbiological process which converts waste materials into organic manure, which are rich in plant nutrients and humus [1] . Aeration and moisture control are the main key operating parameters for operating the windrow compost plant. Access this article online Quick Response Code Website: www.ijlssr.com DOI: 10.21276/ijlssr.2018.4.2.9 Addition of specialized bio-culture consortium is proposed for increasing composting activity has great use. Microbial composting gets advantages not only by reducing the volumes of waste materials but also by recycling of nutrients and organic matter to improve the soils. Aerobic decomposition process also generates fewer greenhouse gases as compared to land filling. Thermophilic composting associated with disadvantages of long duration process by which loss of the nutrient occurs during the process and it needed frequent turning to maintain aerobic. Microbial populations are the active components of biodegradation processes and conversion during composting. Thus, compost quality is directly related to the composition and sequence of microbial communities in the process, being the fungi and bacteria that perform the degradation of organic matter [2] . Composting of agricultural waste is an alternative trail to alleviate the negative impact of its accumulation and/or avoid the environmental pollution. Abou et al. [3] concluded that recycling agriculture wastes is a must for environment as well as economical saving. This recycling will not only increase agricultural production but also will improve its quality. Composting is considered a biological process in which microorganisms convert organic residues into soil-like material called compost. El-Haggar et al. [4] and Geisel [5] reported windrows composting is a commonly used processing method. The microbial decomposition of RESEARCH ARTICLE
  • 2. Int. J. Life. Sci. Scienti. Res. March 2018 Copyright © 2015-2018| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1671 organic wastes is controlled by environmental factors affecting microbial activity within the windrow piles. There are some factors affecting composting and directly influence the rate of decomposition, such as particle size, moisture content, aeration, temperature, C/N ratio and pH. Therefore, intensive management of the composting process by turning and moisture addition is likely to affect the N fertilizer value of the mature compost. Microbial inoculation of compostable material could allow the inoculated microorganisms like (Streptomyces aurefaciens, Trichoderma viride, Trichoderma harzianum, Thermomyces lanuginosus, Aspergillus niger, Bacillus subtilis, Bacillus sphaericus, B. licheniformis, Bacillus stearothermophilus) to dominate over the indigenous micro-biota and successfully develop appropriate degradation [6] . The important advantages of composting are the reduction of the wastes, the destruction of weed seeds and of pathogenic microorganisms [7] . Additional benefits of composting as mechanism for waste management are production of valuable soil amendments, low operation costs, easy to be applied in most of developing countries, and encouragement of environmentally friendly practices such as reduction of the emission of greenhouse gases, promote the efficiency of fertilizer application [8] . Microbial composting technologies for agriculture and other waste management are very significant to meet the need of developing countries. Therefore, the present work aims to rapid composting of agricultural and other wastes through the microbial composting process using Yash Activator Plus. MATERIALS AND METHODS Place of work- The present study was conducted in the Yash Krishi Takniki Evam Vigyan Kendra, Allahabad, Uttar Pradesh, India in the duration of 2017. Experimental details- The experiment was conducted in Plastic pots, which were filled with the different wastes, namely Sugarcane waste, Plant waste, Flower waste, Mausmi waste and Mixed waste with a set of control pot and 3 replicates of each. All the weighted amount of wastes were inoculated with the Yash Activator plus, which are a mixed culture of Mesophilic and Thermophilic microbial consortia. Inoculum cultures were inoculated with the rate of 2% w/w. The moisture content was maintained at 50-60% and turning of material at one week interval for proper aeration were achieved. The data was taken before and after inoculation of cultures at the interval of 20 days up to 60 days. The data were recorded during the course of study at an appropriate time interval. RESULTS AND DISCUSSION Composting generally take place within two temperatures ranges known as mesophilic (10-40⁰C) and thermophilic (over 40⁰C). Although mesophilic temperatures allow effective composting, experts suggest maintaining temperatures between 43⁰C and 65⁰C. The thermophilic composting is desirable, because they destroy more pathogens, weed seeds and fly larvae in the composting materials. The experimental results showed that the temperature of the waste materials before inoculation was 34, 35, 37, 35 and 35 ˚C namely Sugarcane waste, Plant waste, Flower waste, Mausmi waste and Mixed waste respectively. Temperature variations during the composting process are shown in Table 1. The data obtained at 20 days of inoculation with Yash Activator Plus the temperature were increased rapidly at 20 days of composting which were 50, 52, 58, 54 and 54˚C with comparison to controls which were 45, 44, 48, 46, and 46˚C respectively. The temperature of composting decreased slowly at 47, 48, 55, 51 and 50˚C respectively at 40 days of composting and at 60 days almost the temperature were stabilized, which were 35, 36, 37, 35 and 36˚C with comparison to controls which were 37, 38, 40, 38 and 37˚C respectively. Temperature, which is an important factor in composting process, its influences on the activity and diversity of microorganisms [9] . Liang et al. [10] reported that the enhancement of microbial activities was induced by increasing temperature. The results indicate that the maximum temperature increased in flower waste which was 58˚C at 20 days of composting this increased temperature rapidly and enhanced the composting process in comparison to natural composting. This rising of temperature during composting was due to the microorganism activity in the waste. Kanotra S and Mathur [11] reported that fungi, bacteria, and actinomycetes play unique and important roles during the composting, mixed cultures of microorganisms enhanced the rate of lignocelluloses degradation, due to their synergistic activity through utilization of intermediate degradation products. The results can be correlated with the findings of El-Meniawy [12] ; Abdel-Aziz and Al-Barakah [13] ; Eida [14] . The maturity of composting stage was started with the temperature decreased to normal air daily temperature and remains almost constant with turning of the piles [15] . Therefore, this is considered as a good indicator for the end of the biodegradation phase in which the compost achieves maturity [16] . The decrease in temperature after peak value was related to the decrease in microbial as well as enzymatic activities. The results are with the agreements of Noguerira et al. [17] study.
  • 3. Int. J. Life. Sci. Scienti. Res. March 2018 Copyright © 2015-2018| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1672 Table 1: Temperature variations during the composting process of different waste materials Waste materials Temperature variations (˚C) Before Inoculation At 20 days At 40 days At 60 days Control Treated Control Treated Control Treated Sugarcane waste 34.0 45.0 50.0 42.0 47.0 37.0 35.0 Plant waste 35.0 44.0 52.0 42.0 48.0 38.0 36.0 Flower waste 37.0 48.0 58.0 45.0 55.0 40.0 37.0 Mausmi waste 35.0 46.0 54.0 44.0 51.0 38.0 35.0 Mixed Waste 35.0 46.0 54.0 43.0 50.0 37.0 36.0 Fig. 1: Different waste materials before inoculation of Yash Activator Plus Dry matter content results of the different wastes treatments showed that there are decreased gradually during the whole period of composting, which is shown in Table 2. The initial amounts of different waste were 2650, 3000, 3400, 4000 and 3200 gm respectively. The maximum reductions of dry matter are achieved at 20 days data of composting stage, which was characterized by the maximum microbial activity. The total loss of dry matter content at the end of composting amounted to be 37.73, 39.67, 52.94, 51.25 and 40 % from the initial amount, which are Sugarcane waste, Plant waste, Flower waste, Mausmi waste and Mixed waste respectively. The maximum and minimum dry matter content was decreased in flower waste and sugarcane waste, which were 52.94 and 37.73 % respectively. These results can be correlated with those of Wallace [18] and Kuok et al. [19] . The turning effects on the microbial consortia during the composting enhanced the degradation of organic matter by transferring the undamaged organics at unfavorable temperatures to favorable temperatures, to allow degradation by microorganisms that degrade more vigorously reported by Kuok et al. [19] . Table 2: Effect of Yash Activator plus on dry matter of different waste materials during composting Waste materials Weight of the dry matter (gm) Before Inoculation At 20 days At 40 days At 60 days Control Treated Control Treated Control Treated Sugarcane waste 2,650 2,313 2,005 2,050 1,830 1905 1,650 Plant waste 3,000 2,410 2,205 2,235 2,005 2,150 1,810 Flower waste 3,400 2,000 1,742 1,860 1,645 1,860 1,600 Mausmi waste 4,000 2,610 2,400 2,330 2,130 2,220 1,950 Mixed Waste 3,200 2,660 2,260 2,440 2,165 2,220 1,920
  • 4. Int. J. Life. Sci. Scienti. Res. March 2018 Copyright © 2015-2018| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1673 Fig. 2: Different waste materials after composting with Yash Activator Plus at 60 days CONCLUSIONS The main objective of the research included the characterization and study of the wastes generated in daily life. We could get an idea that the main constituent in the waste was the biodegradable fraction, which included the Flower, Mausmi, market wastes like raw fruits, vegetables, leaves etc. thereby making it ideal for utilizing for composting rather than the land spreading utilized in the dump yard. The present experimental results indicate that the rapid degradation of different wastes treated with Yash Activator Plus compared to control treatments. This may be due to the increase of microorganism's activity in biodegradation and more effective way of biodegradation of waste. Our results showed that the microbial consortium offered a faster medium of treatment or recycling where results were obtained in a span of 60 days. REFERENCES [1] Sharma S, Mathur RC, and Vasudevan P. Composting silkworm culture waste. Compost Sci Util, 1999; 7:74-81. [2] Palm CA, Gachengo CN, Delve RJ, Cadisch G, and Giller KE. Organic inputs for soil fertility management in tropical agroecosystems: Application of an organic resource database. Agriculture Ecosystems and Environement, 2004; 83:27-42. [3] Abou Hussein ShD, and Sawan M. The Utilization of Agricultural Waste as the Environmental Issues in Egypt (A Case Study). J. of Applied Sci. Res., 2010; 6(8): 1116-1124. [4] El-Haggar SM, Mounir G, and Gennaro L. Agricultural waste as an energy source indeveloping countries, a case study in Egypt on the utilization of agricultural waste through complexes. International Centre for Science and High Technology (ICS).United Nations Industrial Development organization (UNODO), 2004; pp: 1-10. [5] Geisel PM. Compost in a Hurry. Compost in Hurry University of California, Agriculture and neutral recourses, 2001; 8037:1-4. [6] Badr El-Din, SMS, Attia M, and Abo Sedera SA. Field assessment of composts produced by highly effective cellulolytic microorganisms. Biol. Fertil. Soils, 2000; 32:35 -40. [7] Bernal MP, Albur querque JA, and Moral R. Composting of animal manures and hemical criteria for compost maturity assessment. A review Bioresource Technol. 2009; 100: 5444-5453. [8] Hoornweg DL, Thomas and Otten. Composting and its applicability in developing countries. The International Bank for Reconstruction and Development/ The World Bank, Washington, D.C., USA, 2000. [9] Finstein MS, Miller FC, and Strom PF. Waste treatment composting as a controlled system. Biotechnol, 1986; 8:363-398. [10]Liang C, Das KC, McClendon RW. The influence of temperature and moisture contents regimes on the aerobic microbial activity of a biosolids composting blend. Bioresour Technol, 2003; 86:131-137. [11]Kanotra S and Mathur RS. Bioresource Technology, 1994; 47:185-188. [12]El-Meniawy MA. Microbiological Studies on the Production of Non- Traditional Animal Feed from Agricultural wastes. M. Sc. Thesis, Faculty of Agriculture, Al- Azhar University, Cairo, Egypt, 2003. [13]Abdel-Aziz RA, and Al-Barakah FN. Composting technology and impact of compost on soil biochemical properties. Arab Gulf J. Scientific Res. 2005; 23(2):80-91. [14]Eida MF. Application of biological farming principals for producing safe vegetable crops. M. Sc. Thesis, Faculty of Agriculture, Kafrelsheikh University, 2007. [15]Harada Y, Inoko A, Tadaki, M, and Izawa T. Maturity process of city refuse compost during piling. Soil Sci. and Plant Nutr., 1981; 27:357-364. [16]Jimenez El and Garcia VP. Evaluation of city refuse compost during piling. Biological Wastes, 1989; 27: 55-142. [17]Noguerira WA, Nogueira FN, and Devens DC. Temperature and pH control in composting of coffee and agricultural wastes. Water Sci. and Technol., 1999; 40 (1):113-119.
  • 5. Int. J. Life. Sci. Scienti. Res. March 2018 Copyright © 2015-2018| IJLSSR by Society for Scientific Research is under a CC BY-NC 4.0 International License Page 1674 [18]Wallace, PA. Compost Use in Agriculture, EB Nationwide, 2003. [19]Kuok F, Mimoto H, and Nakasaki K. Effects of turning on the microbial consortia and the in situ temperature preferences of microorganisms in a laboratory-scale swine manure composting. Bioresour Technol, 2012; 16: 421-427. International Journal of Life Sciences Scientific Research (IJLSSR) Open Access Policy Authors/Contributors are responsible for originality, contents, correct references, and ethical issues. IJLSSR publishes all articles under Creative Commons Attribution- Non-Commercial 4.0 International License (CC BY-NC). https://creativecommons.org/licenses/by-nc/4.0/legalcode How to cite this article: Hafeez M, Gupta P, Gupta YP. Rapid Composting of Different Wastes with Yash Activator Plus. Int. J. Life. Sci. Scienti. Res., 2018; 4(2): 1670-1674. DOI:10.21276/ijlssr.2018.4.2.9 Source of Financial Support: Nil, Conflict of interest: Nil