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Characterisation Peal of Fruit and Leaf of Vegetable Waste with Cow Dung for Maximizing the Biogas Yield

Received: 24 November 2016     Accepted: 24 March 2017     Published: 17 April 2017
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Abstract

The biogas production and methane (CH4) enrichment for anaerobic digestion (AD) of fruit and vegetable waste (FVW). The biogas production and methane content of fruit and vegetable wastes (FVW) degradation were evaluated against a treatment combination with a cow dung at a Ratio of FVW to Cow dung T1 (cow dung alone), T2 (1:3), T3 (1:1), T4 (3:1),and T5 (FVW alone). The digesters were operated for 80 days. The highest total methane yields about 78.35% was obtained from the cow dung digester (T1). The highest production of biogas yield (7552.67 ml) was observed in T1 and the lowest biogas production rate (2652.83ml) was from a reactor operated by FVW alone. Similar to the biogas yield, higher percentage of methane was produced in 1. Anaerobic digestion; vegetable and fruit wastes of high calorific contents can be transformed to a source of energy through the production of biogas in this day and age of energy insufficiencies. Role in maximizing the process of anaerobic digestion through speeding up hydrolysis and to compare production potentials of commonly available wastes in Addis Ababa for possible co-digestion in large scale production of biogas. Thermo-chemical pre-treatment was the most effective for speeding up hydrolysis with the co-digested substrates producing maximum biogas. The moisture content ranged between 67-83%. The pH reduced from 6.8-7.2 before digestion to 6.2-6.8 after digestion. The desired C: N ratio was between 18:1 to 32:1 for Anaerobic Digestion. The gas produced was found to contain 63.89% methane, 33.12% CO2 and 3% other gases.

Published in International Journal of Energy and Power Engineering (Volume 6, Issue 2)
DOI 10.11648/j.ijepe.20170602.12
Page(s) 13-21
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2017. Published by Science Publishing Group

Keywords

Anaerobic Digestion, Co-digestion, C: N Ratio, Hydrolysis, Substrate Pre-treatment

References
[1] Alvarez, R. and Lidén, G. (2009). Low Temperature Anaerobic Digestion of Mixtures of llama, Cow and Sheep Manure for improved Methane Production. Biomass and bioenergy. Vol. 33: 527_533.
[2] Bardiya, N., Somayaji, D., Khanna, and S. (1996): Biomethanation of banana peel and pine-apple waste. Bioresource Technology 58: 73-76.
[3] Dahlman, J, and Forst, C. (2001). Technologies Demonstrated at Echo. Floating Drum Biogas Digester; Echo, 17391 Durance Rd, North Ft. Myers FL 33917, USA.
[4] El-Mashad, H. M., Zhang, R. (2010): Biogas production from co-digestion of dairy manure and food waste.–Bioresource Technology 101: 4021–4028.
[5] Ethiopian Horticultural Development Agency (2011). Exporting Fruit and Vegetable from. Ethiopian Horticultural Producers and Exporters Association; Report; Addis Ababa, Ethiopia.
[6] European Energy Manager Biogas Preparation Material (EEMBPM) (2006), pp 2-5.
[7] Fang C. (2010). Biogas production from food-processing industrial wastes by anaerobic digestion. PhD
[8] Garba, B. and Atiku, S. (1992). Effect of some Operating Parameters on Biogas Production Rate. Nigeria Journal of Renewable energy 6(3): 343-344.
[9] Gerardi, M. H. (2003). The Microbiology of anaerobic digesters, Wiley Interscience, pp. 1 – 85.
[10] Jemmett, R. (2006). Methane-Biogas Production Guide; Version 1.0, UK, pp3-4
[11] Khan, S., Afzal, M., Iqbal, S., Mirza, M. S., Khan, Q. M., 2013. Inocu-lum pretreatment affects bacterial survival, activity and catabolic gene expression during phytoremediation of diesel contaminated soil. Chemosphere.
[12] L. Neves, R. Oliveira, and M. M. Alves, Fate of LCFA in the co-digestion of cow manure, food waste and discontinuous addition of oil, Water Res. 43 (2009), pp. 5142–5150.
[13] Nelson, D. W. and L. E. Sommers. 1996. Total carbon, organic carbon, and organic matter. In: Methods of Soil Analysis, Part 2, 2nd ed., A. L. Page et al., Ed. Agronomy. 9:961-1010. Am. Soc. of Agron. Inc. Madison, WI.
[14] Murto M., Björnsson L. and Mattiasson B. (2004). Impact of food industrial waste on anaerobic co-digestion of sewage sludge and pig manure, Journal of Environmental Management 70, 101–107.
[15] NRCS (2005). Conservation Practice Standard. Anaerobic Digester in Controlled Temperature. Number code 366. IA, pp 4-6.
[16] Polprasert C (1989) Organic waste recycling, John Willey and Sons, Chichester-New York, Brisbane-Toronto-Singapore
[17] Pyle, L. (1978). Anaerobic digestion; the technical options in Biogas Technology in the Third World: A multidisciplinary review, (Ed) A. Barnett, L. Pyle, and S. K. Subramanian. International Development Research centre, Ottawa: pp47-52.
[18] Rai, G. D. (2004). Non-conventional Energy Resources, 2nd edn. Khpu Khanna, India. pp 331-337, 369.
[19] Rahmat, BudyR ahmat, Tedi Hartoyo and Yaya Sunarya (2014). Biogas Production from TOFU Liquid waste on Treated Agricultural Waste, American Journal of Agricultural and Biological Sciences 9 (2): 226-231.
[20] Saxon, J. (1998). Troubled Times. Renewable Energy 2: 519-520. Thesis, Technical University of Denmark,
[21] Steffen, R.; Szolar, O. and Braun, R. (2000). Feedstock for Anaerobic Digestion. Anaerobic Digestion, making Energy and Solving. Modern Waste Problem, AD-Nett report.
[22] Wilkie, A. C. (2008). Bioenergy: Biomethane from biomass, Biowaste and Biofuel, J. Well ET al. Washington DC, pp195-199.
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  • APA Style

    Massreshaw Assnakew Abebe. (2017). Characterisation Peal of Fruit and Leaf of Vegetable Waste with Cow Dung for Maximizing the Biogas Yield. International Journal of Energy and Power Engineering, 6(2), 13-21. https://doi.org/10.11648/j.ijepe.20170602.12

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    ACS Style

    Massreshaw Assnakew Abebe. Characterisation Peal of Fruit and Leaf of Vegetable Waste with Cow Dung for Maximizing the Biogas Yield. Int. J. Energy Power Eng. 2017, 6(2), 13-21. doi: 10.11648/j.ijepe.20170602.12

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    AMA Style

    Massreshaw Assnakew Abebe. Characterisation Peal of Fruit and Leaf of Vegetable Waste with Cow Dung for Maximizing the Biogas Yield. Int J Energy Power Eng. 2017;6(2):13-21. doi: 10.11648/j.ijepe.20170602.12

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  • @article{10.11648/j.ijepe.20170602.12,
      author = {Massreshaw Assnakew Abebe},
      title = {Characterisation Peal of Fruit and Leaf of Vegetable Waste with Cow Dung for Maximizing the Biogas Yield},
      journal = {International Journal of Energy and Power Engineering},
      volume = {6},
      number = {2},
      pages = {13-21},
      doi = {10.11648/j.ijepe.20170602.12},
      url = {https://doi.org/10.11648/j.ijepe.20170602.12},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ijepe.20170602.12},
      abstract = {The biogas production and methane (CH4) enrichment for anaerobic digestion (AD) of fruit and vegetable waste (FVW). The biogas production and methane content of fruit and vegetable wastes (FVW) degradation were evaluated against a treatment combination with a cow dung at a Ratio of FVW to Cow dung T1 (cow dung alone), T2 (1:3), T3 (1:1), T4 (3:1),and T5 (FVW alone). The digesters were operated for 80 days. The highest total methane yields about 78.35% was obtained from the cow dung digester (T1). The highest production of biogas yield (7552.67 ml) was observed in T1 and the lowest biogas production rate (2652.83ml) was from a reactor operated by FVW alone. Similar to the biogas yield, higher percentage of methane was produced in 1. Anaerobic digestion; vegetable and fruit wastes of high calorific contents can be transformed to a source of energy through the production of biogas in this day and age of energy insufficiencies. Role in maximizing the process of anaerobic digestion through speeding up hydrolysis and to compare production potentials of commonly available wastes in Addis Ababa for possible co-digestion in large scale production of biogas. Thermo-chemical pre-treatment was the most effective for speeding up hydrolysis with the co-digested substrates producing maximum biogas. The moisture content ranged between 67-83%. The pH reduced from 6.8-7.2 before digestion to 6.2-6.8 after digestion. The desired C: N ratio was between 18:1 to 32:1 for Anaerobic Digestion. The gas produced was found to contain 63.89% methane, 33.12% CO2 and 3% other gases.},
     year = {2017}
    }
    

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  • TY  - JOUR
    T1  - Characterisation Peal of Fruit and Leaf of Vegetable Waste with Cow Dung for Maximizing the Biogas Yield
    AU  - Massreshaw Assnakew Abebe
    Y1  - 2017/04/17
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    T2  - International Journal of Energy and Power Engineering
    JF  - International Journal of Energy and Power Engineering
    JO  - International Journal of Energy and Power Engineering
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    UR  - https://doi.org/10.11648/j.ijepe.20170602.12
    AB  - The biogas production and methane (CH4) enrichment for anaerobic digestion (AD) of fruit and vegetable waste (FVW). The biogas production and methane content of fruit and vegetable wastes (FVW) degradation were evaluated against a treatment combination with a cow dung at a Ratio of FVW to Cow dung T1 (cow dung alone), T2 (1:3), T3 (1:1), T4 (3:1),and T5 (FVW alone). The digesters were operated for 80 days. The highest total methane yields about 78.35% was obtained from the cow dung digester (T1). The highest production of biogas yield (7552.67 ml) was observed in T1 and the lowest biogas production rate (2652.83ml) was from a reactor operated by FVW alone. Similar to the biogas yield, higher percentage of methane was produced in 1. Anaerobic digestion; vegetable and fruit wastes of high calorific contents can be transformed to a source of energy through the production of biogas in this day and age of energy insufficiencies. Role in maximizing the process of anaerobic digestion through speeding up hydrolysis and to compare production potentials of commonly available wastes in Addis Ababa for possible co-digestion in large scale production of biogas. Thermo-chemical pre-treatment was the most effective for speeding up hydrolysis with the co-digested substrates producing maximum biogas. The moisture content ranged between 67-83%. The pH reduced from 6.8-7.2 before digestion to 6.2-6.8 after digestion. The desired C: N ratio was between 18:1 to 32:1 for Anaerobic Digestion. The gas produced was found to contain 63.89% methane, 33.12% CO2 and 3% other gases.
    VL  - 6
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Author Information
  • Addis Ababa City, Addis Ababa City Cleansing Management Office, Addis Ababa, Ethiopia

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