有機農業廢棄物應用於能、資源再利用推展之研究

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有機農業廢棄物應用於能、資源再利用推展之研究

Utilization promotion of energy and resource in organic agricultural waste

蕭國柱 , Masters　　Advisor：羅煌木　　

繁體中文

有機農業廢棄物；厭氧消化； Organic-agricultural waste ； Anaerobic digestion

Abstract │ Reference (24) │ Altmetrics

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Agriculture can use biomass concentrated resources from waste of farming, forestry, fishery and animal husbandry…etc and kitchen waste., those large amount of organic biomass energy can be converted into vapor or electricity and methane and hydrogen energy by heat and biological processing, organic waste will be recycled some of the available material utilization. Organic waste processing methods is suitable for Taiwan which is to carry out its recovery anaerobic fermentation processing and to achieve the purpose of the abatement and recovery of energy. Therefore, organic waste such as food waste, agricultural waste and sewage sludge and others is very suitable for co-digestion object. While anaerobic fermentation of organic waste gas process, it is arising in about 65% of the methane gas. Thus, for recent years some countries have built biological anaerobic fermentation of organic waste treatment plant. It has anaerobic digestion of organic solid waste processing plant, organic waste carried sorting, crushing and after preprocessing, carry out anaerobic fermentation, methane gas generated from available fuel or combustion power generation, and waste composting efficiency gains in the domestic fertilizer use as an evaluation . There is a good example in Munich, Germany for the world's most successful application of the recovery plan. It proves the correctness of this research is correct.
The research sets up an effective method for the processing of organic solid waste and energy technology and resources, the experiment will be food waste, What we need for the experimental materials is municipal sludge, municipal waste and agricultural waste, it bases on 500 mL of anaerobic and the reaction vessel for a period time of solids in accordance with the feed material and the semi-continuous experiments. It will be monitored daily by gas production, pH, redox potential (ORP), conductivity (EC), salinity (Salinity), to analysis of chemical oxygen demand (COD), TS, VS, and other physical and chemical parameters every single week.
In this research, organic-agriculture solid waste: there is main 8 different kind of resources: rice, rice straw, flowers residue, fruit and vegetable residues, oyster shells, fishing residues, livestock manure, poultry residue, respectively, by way of a single or mixed batch anaerobic digestion experiments, and the anaerobic sludge wastewater processing plant as a matrix organics.  Anaerobic treatment-plant feed rate will get better combination Institute SRT for 20 days to adjust experiment with feed concentration. A preliminary study found that in eight of solid organic waste to livestock residue as substrate anaerobic tank, the gas efficiency of its most significant 112 days can produce 8147 mL of gas production, average yield 72.7 mL / a day, which is far another seven kinds of experiments in higher organic solid waste, and end of the experiment after 112 days the mean of gas production can be on going. About pH, between 6.5 to 7.5, In order to help the growth of the microorganism environment, although the phenomenon of livestock residue was acidified, in the experiment of the substrate has been added to alkaline, which can stabilize the pH at 6.6 between ~ 7.4, which is the range to grow of beneficial microorganisms. Comparison of eight kinds of organic solid waste, the residue with the highest gas production livestock and stable and its pH measurement can also be beneficial to the maintenance of microbial growth environment, so to livestock residues as high feasibility of anaerobic digestion tank main matrix.

Reference ( 24 ) 〈TOP〉

1.Duku, M. H., Gu, S., and Hagan, E. B., “A comprehensive review of biomass resources and biofuels potential in Ghana. Renewable and Sustainable Energy Reviews,” Vol. 15, pp. 404-415(2011).
連結：
2.Panwar, N. L., Kaushik, S. C., and Kothari, S., “Role of renewable energy sources in environmental protection: A review. Renewable and Sustainable Energy Reviews,” Vol. 15, pp. 1513-1524(2011).
連結：
3.Lo, H. M., Liao, Y. L., “The metal-leaching and acid-neutralizing capacity of MSW incinerator ash co-disposed with MSW in landfill sites,” Journal of Hazardous Materials, Vol. 142, pp. 512–519(2007).
連結：
4.Lo, H. M., Kurniawan, T. A., Sillanpaa, M. E. T., Pai, T. Y., Chiang, C. F., Chao, K. P., Liu, M. H., Chuang, S. H., Banks, C. J., Wang, S. C., Lin, K. C., Lin, C. Y., Liu, W. F., Cheng, P. H., Chen, C. K., Chiu, H. Y., and Wu, H. Y., “Modeling biogas production from organic fraction of MSW co-digested with MSWI ashes in anaerobic bioreactors,” Bioresource Technology, Vol. 101, pp.6329-6335(2010).
連結：
5.Lo, H. M., Chiang, C. F., Tsao, H. C., Pai, T. Y., Liu, M. H., Kurniawan, T. A., Chao, K. P., Liou, C. T., Lin, K. C., Chang, C. Y., Wang, S. C., Banks, C. J., Lin, C. Y., Liu, W. F., Chen, P. H., Chen, C. K., Chiu, H. Y., Wu, H. Y., Chao, T. W., Chen, Y. R., Liu, D. W., and Lo, F. C., “Effects of spiked metals on the MSW anaerobic digestion,” Waste Management & Research, Vol. 30, pp.32-48(2012).
連結：

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