Showing posts with label biogas research paper pdf. Show all posts
Showing posts with label biogas research paper pdf. Show all posts

Sunday, 19 August 2012

Research Paper | Household Biogas Digesters

Household Biogas Digesters—A Review 

Karthik Rajendran *, Solmaz Aslanzadeh and Mohammad J. Taherzadeh 
School of Engineering, Universityof Borås, Borås 50190, Sweden;
E-Mails: Solmaz.Aslanzadeh@hb.se (S.A.); Mohammad.Taherzadeh@hb.se (M.J.T.)
*Author to whom correspondence should be addressed; E-Mail: Karthik.Rajendran@hb.se;
Tel.: +46-33-435-4855; Fax: +46-33-435-4008.
Received: 11 May 2012; in revised form: 27 July 2012 / Accepted: 30 July 2012 /
Published: 8 August 2012
Bio gas digester

Abstract:This review is a summary of different aspects of the design and operation of small-scale, household, biogas digesters. It covers different digester designs and materials used for construction, important operating parameters such as pH, temperature, substrate, and loading rate, applications of the biogas,the government policies concerning the use of household digesters, and the social and environmental effects of the digesters. Biogas is a value-added product of anaerobic digestion of organic compounds. Biogas production depends on different factors including: pH, temperature, substrate, loading rate, hydraulic retention time (HRT), C/N ratio, and mixing. Household digesters are cheap, easy to handle, and reduce the amount of organic  household waste. The size of these digesters varies between 1 and 150 m3. The common designs include fixed dome, floating drum, and plug flow type. Biogas and fertilizer obtained at the end of anaerobic digestion could be  used for cooking, lighting, and electricity.

Keywords:biogas; household digesters; bioenergy; waste management; fixed dome digesters; floating drum digesters; plug flow digesters

1. Introduction
Due to the increasing prices of fossil fuels and taxes on energy sources, finding alternative, clean
and economical sources of energy has nowadays become a major concern for households’ and nations’
economies. In addition, economic prosperity and quality of life, which are linked in most countries to
per-capitaenergy consumption, is a great determinant and indicator of economical development
Energy demand is a critical reason for extensive climate change, resource exploitation, and also
restricts the living standards of humans [5,6].  By the time fuel and fertilizer reaches rural areas, the end price is relatively expensive due to high  transport costs, leaving people to find alternative resources other thanoil [7]. Starke [8] reported wood  as the traditional source of fuel to produce energy for domestic purposes for 2.5 billion people in Asia. Many of the rural communities in developing countries are forced torely on the traditional energy  sources such as firewood, dung, crop residues, and paraffin. These traditional methods are often expensive and/or time-consuming [9–11]. Cooking accounts for 90% of energy consumption in the households of developing countries [12]. Furthermore, access to electricity in rural areas is relatively scarce [13]. Biogas is a substitute for firewood and cattle dung that can meet the energy needs of the rural population [14,15]. Biogas is a renewable source of energy that can be used as a substitute for natural gas or liquefied petroleum gas [16]. There are different models to assess the energy content of different energy sources, which includes water boiling test, controlled cooking test and kitchen performance test [17]. The energy content of 1.0 m3 of purified biogas is equal to 1.1 L of gasoline, 1.7 L of bioethanol, or 0.97 m3 of natural gas [16]. The application for rural and urban waste biogas production is widely spread. It is a challenge for engineers and scientists to build an efficient domestic digesters with the materials available, at the same time taking the local and economical considerations into the account. Although many digesters have been built, additional research and awareness are needed to meet the changing needs and conditions [18]. Biogas production can be carried out in very small reactors ranging from100-mL serum bottles in the lab up to 10,000 m3large digesters as normally used, for example, in Europe. This review deals with a summary of different household biogas digesters, their operating parameters, cost and materials used to build them, startup, and maintenance, the variety of applications employed, and associated social and environmental effects. 

 Biogas
Biogas, the metabolic product of anaerobic digestion, is a mixture of methane and carbon dioxide with small quantities of other gases such as hydrogen sulfide [19,20]. Methane, the desired component of biogas, is a colorless, blue burning gas used for cooking, heating,and lighting [21]. Biogas is a clean, efficient, and renewable source of energy, which can be used as a substitute for other fuels in order to save energy in rural areas [22]. In anaerobic digestion, organic materials are degraded by bacteria, in the absence of oxygen, converting it into a methane and carbon dioxide mixture. The digestate or slurry from the digester is rich inammonium and other nutrients used as an organic fertilizer [11,23–27]. Methane formation in anaerobic digestion involves four different steps, including hydrolysis, acidogenesis, acetogenesis, and methanogenesis. Different bacterial/archaea communities work in a syntrophic relationship with each other to form methane. In hydrolysis, complex carbohydrates, fats, and proteins are first hydrolyzedto their monomeric forms by exoenzymes and bacterial cellulosome. In the second phase (acidogenesis), monomers are further degraded into short-chain acids such as: acetic acid, propionic acid, butyric acid, isobutyric acid, valeric acid, isovaleric acid, caprionic acid,lcohols, hydrogen, and carbon dioxide. During acetogenesis, these short-chain acids are converted into acetate, hydrogen, and carbon dioxide. In the last phase, methanogens convert the intermediates produced into methane and carbon dioxide. Almost one-third of methane formation is due to reduction of carbon dioxide by hydrogen

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Monday, 23 April 2012

Research Paper | Hydrogen Production Biogas Plant Slurry


Hydrogen Production from Kitchen Waste using Heat Treated Anaerobic Biogas Plant Slurry
Hydrogen Production Biogas Plant Slurry

S. Jayalakshmi1, V. Sukumaran2 and Kurian Joseph3

1

Civil Department, Periyar Maniammai College of Technology for Women, Vallam, Thanjavur.
Dept. of Biotechnology, Periyar Maniammai College of Technology for Women, Vallam, Thanjavur
3
Centre for Environmental Studies, Anna University, Gundy, Chennai
Email: j_lak2001@yahoo.co.in

ABSTRACT

Anaerobic digestion of kitchen waste for hydrogen production was performed in lab scale reactors, using heat-treated anaerobically digested biogas plant slurry. The biogas plant slurry was given heat treatment at varying temperatures ranging from 70oC to 100 oC for 15 minutes.The reactor operated with 100 oC heat-treated inoculum was efficient in hydrogen production from kitchen waste. The rate of hydrogen production was 176.2 mL/kg TS/ h. Methane was not reported in all the operated reactors except that the reactor operated with 70 oC heat-treated inoculum. The hydrogen concentration was found to be 55-60% and the remaining was CO2. Normal butyrate was the main acid product, and the percentages of butyrate, acetate and propionate at tested conditions were 45 – 50 %, 20 – 25% and 20 – 25% respectively.

Keywords: Anaerobic Digestion, Kitchen Waste, Heat-treated inoculum, Hydrogen gas

1.0 INTRODUCTION

Hydrogen is a promising alternate to fossil fuels due to its clean and high-energy potential. Anaerobic  Digestion of organic waste produces various volatile fatty acids (VFA), H2, CO2 and other intermediates (Rustrian et al 1999). The reactions involved in hydrogen production are rapid and making them useful for treating large quantities of organic wastes. Hydrogen gas is not the only beneficial energy source, but also VFA can be used for methane production by methanogenes (Llabres et al, 1999). Acidification of organic wastes, however, needs hydraulic retention time (HRT) longer than 3 days in which hydrogen consumers such as methanogenes could be multiplied. Because of this reason, most researches on hydrogen production have been carried out under inhibitory condition of hydrogen consumers. In order to inactivate hydrogen consumers, inoculum was cultured with pure chemicals such as glucose or sucrose at short HRT and /or low pH (Fang et al, 2002) or preheated inoculum to harvest spore-forming anaerobic bacteria (Lay et al, 1999). Continuous production of hydrogen was also tried at short HRT to prevent the growth of hydrogen consumers (Mizuno et al,2000). However, there have been no studies on continuous hydrogen production at enough HRT from organic solid wastes. So far, majority of research work has been directed at expensive pure substrates to a much lesser quantity of solid waste (Hawkes et al, 2002). Therefore the aim of this current work was to investigate the feasibility of hydrogen production from kitchen waste using heat-treated
anaerobic biogas plant slurry.

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