human waste disposal: a biogas feasibility study in pabal

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CRANFIELD UNIVERSITY Thomas Edward Wilson Human Waste Disposal: A biogas feasibility study in Pabal School of Applied Sciences Water Management: Community Water and Sanitation MSc Academic Year: 2008-2009 Supervisor: James Webster September 2009

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A feasibility study on a latrine powered biogas generator that would solve sanitation problems and provide cheap energy.

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Page 1: Human Waste Disposal: A biogas feasibility study in Pabal

CRANFIELD UNIVERSITY

Thomas Edward Wilson

Human Waste Disposal: A biogas feasibility study in Pabal

School of Applied Sciences

Water Management: Community Water and Sanitation MSc

Academic Year: 2008-2009

Supervisor: James Webster

September 2009

Page 2: Human Waste Disposal: A biogas feasibility study in Pabal

CRANFIELD UNIVERSITY

Thomas Edward Wilson

Human Waste Disposal: A biogas feasibility study in Pabal

School of Applied Sciences

Water Management: Community Water and Sanitation MSc

Academic Year: 2008-2009

Supervisor: James Webster

September 2009

This thesis is submitted in partial fulfilment of the requirements for the

degree of MSc Water Management

© Cranfield University 2009. All rights reserved. No part of this publication

may be reproduced without the written permission of the copyright owner

Page 3: Human Waste Disposal: A biogas feasibility study in Pabal
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ABSTRACT

Poor sanitation currently affects 2.6 billion people worldwide, contributing to the deaths

of 1.5 million children every year and inflicting many others with disease and illness.

Sanitation refers to the hygienic and safe way of discharging, collecting and disposing of

excreta and liquid wastes in a manner that promotes the health of individuals and the

community as a whole. Sanitation can easily be improved through education and

improved hygienic techniques, as well as the provision of latrines or structures designed

for removal and disposal purpose.

This study focuses on a project outlined by Engineers Without Borders and EngINdia,

based in the village of Pabal in the Maharashtra district of India. The village suffers from

a lack of water throughout the dry season and poor sanitation, with open defecation still

being prevalent. The proposed solution aims towards a biogas generator design, which

will provide alleviation of the poor sanitary situation and offer an alternative energy

source. Due to numerous practical and socio-cultural influences, it was deemed that a

feasibility study was required to review the current situation within the village, and to

ascertain whether the technology is appropriate or not. The aim of this thesis therefore is

to understand the current sanitation situation within Pabal, relating cultural and social

issues related to the use of nighsoil in biogas production to the appropriateness of this

technology in the village. The results derived from a questionnaire suggest that the

technology can provide numerous benefits to Pabal, yet the implementation project needs

to be tailored appropriately to particular households. The study concludes with

recommendations on how this can be achieved.

Keywords:

Biogas, nightsoil, sanitation, Pabal.

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ACKNOWLEDGEMENTS

This thesis is a combination of the help and support from many generous people, enabling

the research to be undertaken and presented here. Firstly, I would like to thank the people

I met in the village of Pabal in India. Without their patience and generosity the project

would not have been possible. Many thanks to the staff and students of Vigyan Ashram

who supported my studies whilst in India. James Webster and Alison Parker were

fundamental throughout the whole of this thesis and with their guidance and knowledge I

have managed to complete it, to which I am very grateful. Finally, I would like to thank

my parents, for their time, patience and financial support.

TABLE OF CONTENTS

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ABSTRACT...................................................................................................................... i.

ACKNOWLEDGEMENTS.............................................................................................ii.

TABLE OF FIGURES..................................................................................................... v.

TABLE OF TABLES ...................................................................................................... v.

1 Introduction.............................................................................................................. 1.

1.1 Problem Statement ........................................................................................... 3.

1.2 Aims and Objectives ........................................................................................ 6.

2 Literature Review..................................................................................................... 7.

2.1 Introduction...................................................................................................... 7.

2.2 Health and Environmental Benefits ................................................................. 7.

2.3 Sanitation Benefits ........................................................................................... 8.

2.4 Agricultural and Economic Benefits................................................................ 9.

2.5 Social Benefits ............................................................................................... 10.

2.6 Financing Issues............................................................................................. 12.

2.7 Issues of Nighsoil Use ................................................................................... 13.

2.8 Nightsoil Health Concerns ............................................................................. 13.

2.9 Biogas Adoption ............................................................................................ 14.

2.10 Biogas Implementation .................................................................................. 15.

2.11 A Novel Design for a Biogas Generator ........................................................ 16.

3 Methodology.......................................................................................................... 17.

3.1 Previous Work ............................................................................................... 17.

3.2 Theoretical Aspects of Methodology..............................................................17.

3.2.1 Neuman's Four Dimensions of Research......................................................17.

3.2.2 Purpose of the Research...............................................................................18.

3.2.3 Time Dimension of the Study......................................................................18.

3.2.4 Data Collection Techniques.........................................................................18.

3.3 Interview Bias.................................................................................................18.

3.4 Interviews....................................................................................................... 20.

3.5 Pilot ................................................................................................................ 21.

4 Results and Analysis .............................................................................................. 20.

4.1 Introduction.................................................................................................... 20.

4.2 The Current Situation in Pabal....................................................................... 21.

4.2.1 How the village is viewed by people living there........................................ 21.

4.2.2 Changes in the village...................................................................................21.

4.2.3 Infrastructure, development routes, hierarchies............................................21.

4.2.4 Summary.......................................................................................................22.

4.3 Sanitation ......................................................................................................... 22.

4.3.1 Waste disposal problems.............................................................................. 22.

4.3.2 Latrine access............................................................................................... 22.

4.3.3 Prevalence of open defecation ..................................................................... 23.

4.3.4 Summary ...................................................................................................... 23.

4.4 Biogas .............................................................................................................. 24.

4.4.1 General opinions on biogas........................................................................... 24.

4.4.2 Acceptability of using human waste ............................................................. 24.

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4.4.3 Towards an implementation project.............................................................. 25.

4.4.4 Problems towards an implementation project............................................... 25.

4.4.5 Summary ....................................................................................................... 25.

4.5 Overview of Questionnaire Data ..................................................................... 29.

4.6 Tailored Interview Results ............................................................................... 30.

4.6.1 Previous biogas schemes............................................................................... 30.

4.6.2 Future potentials for biogas .......................................................................... 31.

4.7 Pilot Biogas Project ........................................................................................ 32.

4.8 Overall Summary ............................................................................................. 33.

5 Discussion .............................................................................................................. 34.

5.1 Introduction.................................................................................................... 34.

5.2 Review ........................................................................................................... 34.

5.3 Conclusions.................................................................................................... 37.

6 Reccomendations ................................................................................................... 38.

6.1 Introduction.................................................................................................... 38.

6.2 Elements to be reviewed ................................................................................ 38.

REFERENCES .............................................................................................................. 40.

APPENDICES ............................................................................................................... 43.

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TABLE OF FIGURES

Figure 1. (National map of Pabal).......................................................................................4.

Figure 2. (Village map of Pabal).........................................................................................5.

Figure 3. (Photograph of Pabal high street)........................................................................5.

Figure 4. (Photograph of biogas generator)......................................................................21.

Figure 5. (Photograph of biogas latrine)...........................................................................22.

Figure 6. (Chart showing the distribution of number of persons per household).............28.

Figure 7. (Chart showing the acceptance of nighsoil)......................................................28.

Figure 8. (Chart showing biogas adoption).......................................................................28.

Figure 9. (Photograph showing teacher’s biogas).............................................................31.

Figure 10. (Photograph showing farmer’s biogas.............................................................32.

TABLE OF TABLES

Table 1. (Table of an overview of the interview results)..................................................27.

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1. Introduction

Sanitation refers to the safe and hygienic approach to discharging, collecting and

disposing excreta and liquid wastes in a manner that promotes the health of individuals

and the community as a whole (Colford et al 2005). Poor sanitation can have severe

implications for health and hygiene, resulting in numerous illnesses and sicknesses.

Faeces contains disease-causing pathogenic micro-organisms and it is therefore important

to remove these potential hazards. Organisms that can cause disease include viruses,

bacteria and parasitic protozoa, as well as hookworms and other parasitic helminths

(EcoSanRes 2004). These have the potential to cause severe illness and can even be fatal.

There are numerous transition paths through which contamination can occur, including

fluids, fields, flies, food and fingers, ultimately ending up being consumed by a person.

These contamination pathways can be limited through a number of techniques, which

often involve improvements in personal hygiene, food hygiene, adequate cooking, water

disinfection and the provision of toilets. Diarrhoeal disease is one consequence of

contamination and is one of the leading causes of morbidity and mortality in less

developed countries, especially among children under than five years (Colford et al.

2005). Inadequate water, sanitation and hygiene contribute to the deaths of 1.5 million

children every year (Sulabh International 2008).

It is estimated that 2.6 billion people worldwide remain without proper safe facilities for

waste collection and removal, thus lacking protection against preventable diseases that

claim the lives of thousands of people daily (UNICEF 2007). A 2001 census in India

highlighted that 23 per cent of the population currently lack access to a latrine either in

the house or as a shared facility (Water Aid 2006). When populations and families are

consistently affected by illness this inhibits wealth generation as their labour is reduced,

and they often have to spend their limited income on medicines. Improved sanitation can

benefit economics on a household scale, as well as nationally.

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Women and young girls often compromise their safety when a lack of latrines forces

them to relieve themselves in unsafe areas or in darkness, with some girls not attending

school when there is no lavatory facilities for them (Sulabh International 2008). It is

evident that a lack of sanitation infrastructure can have far reaching impacts, affecting

education, dignity and self-esteem.

However, simple interventions to reduce illness can be implemented by improving

sanitary conditions and the construction of basic sanitary structures built for the purpose.

Sanitation interventions often include the provision of some form of excreta disposal

system or latrines (Colford et al. 2005). The provision of latrines can manifest itself in

numerous designs, including pit latrines, composting latrines, urine diversion, Arborloos

and pour-flush latrines to name a few. Sulabh International (2008) have achieved

numerous successful sanitation projects, linking latrines to biogas generators in individual

and communal settings. Biogas is a flammable gas released by decaying organic matter,

commonly consisting of methane and carbon dioxide (UN 1980). This natural gas is

usually obtained from plants and manure and can be exploited for fuel use in cooking,

lighting and electricity generation. With regards to sanitation, night soil (human waste)

can be used as the input to this digestion process as Sulabh International (2008) have

done, utilising a previously wasted source of fuel. Such sanitation interventions usually

consist of single or multiple latrines attached to a digestion chamber of adequate size. The

slurry from this can also be used as a fertilizer for agricultural crops. In Maharashtra,

there have been numerous successful schemes aimed at improving sanitation in villages

(Govt. of Maharashtra 2009), yet a major hurdle in the provision of water and sanitation

services often relates to inadequate financing for development of the required

infrastructure (Water Aid 2006). Programmes are often individual and isolated, rather

than on a larger scale, aimed benefiting numerous villages and households.

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1.1 Problem Statement

The green revolution has provided many benefits for farmers across the globe, increasing

crop yields and easing hunger problems. However, it has also had many negative impacts,

with Pabal being no exception. Environmental degradation and poor soil fertility has

increasingly been noticed as farmers rely on chemical fertilizers and over-use the land.

EWB and EngINdia have undertaken a number of projects to help focus on better

agricultural practice. As previously highlighted, Pabal suffers from a lack of water

resources, and although this has been alleviated by the construction of a new dam five

years ago, the situation is still not ideal. Sanitation in the village has improved drastically,

yet although the Indian government provides subsidies for the construction of outdoor

latrines, many use it as a storeroom. The reason for this is that in the past, population

levels were low enough to continue practicing open defecation. Furthermore, given the

water shortage situation in the village, many cannot spare the water for flushing their

latrine (EWB 2008). This lack of water for flushing toilet systems combined with the

practice of open defecation, has resulted in a solution being proposed by EngINdia to

alleviate these problems, and to provide an alternative energy source for the intermittent

electricity supply available to Pabal.

Pabal is a rural village located in the Maharashtra state of India (figure 1.), with a

population some 15,000 strong (EngINdia 2009). This includes the 5,000 people living in

Pabal itself, and approximately 15 or so hamlets surrounding the village. Many people

living in the surrounding hamlets practice faming on the relatively flat countryside. Being

approximately five hours from Mumbai and two from Pune, the closest city, Pabal is

situated in a remote part of India. Figures 2. and 3. show a local sketch map of the village

and photograph of the high street.

The village experiences heavy monsoons in the wet seasons and vicious droughts in the

dry, offering both climatic extremes for the local population. Dry season temperatures

vary from 20-38 °C, and monsoon temperatures from 10-20 °C (EngINdia 2009). Pabal

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was previously a local regional centre, which attracted development and growth. This

declined at the turn of the 20th

century, with the village consequently suffering from a

lack of investment. It is widely appreciated however, that the introduction of the Jain

temple and Vigyan Ashram to the village has supported the recent growth in the past 20

years. Households typically comprise of 4-7 people in a family, often including 2-3

children and at least one grandparent (EngINdia 2009).

Figure 1. National map of Pabal. (google maps 2009).

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Figure 2. Village map of Pabal (EngINdia 2009).

Figure 3. Pabal high street.

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Vigyan Ashram is an educational centre which specialises in many appropriate rural

technologies, solving practical problems with intuitive designs. The Ashram has many

successful projects labelled to its name and often provides information for villagers in

Pabal on agricultural or technical issues they may have. Many villagers have also

attended short courses run by the Ashram. The main aim of the Ashram is to educate its

students and help them to be successful in future pursuits, yet it is not directly linked with

the village. None the less, its impact cannot be underestimated. Although it is not strictly

an NGO working in Pabal, it can provide some useful insight and support for research,

and will contribute information to this thesis.

1.2 Aims and Objectives

The proposal from Eng INdia is to design and install a biogas generator which utilises

human waste (night soil) on a household scale. The digester would be designed to provide

year round biogas and produce compost from the slurry which famers can use on their

fields, reducing the need for artificial fertilizers. As the generator is run on night soil, a

constant input would be required for gas generation, reducing open defecation in Pabal

and improving the sanitary situation in the village. Vigyan Ashram is interested in

experimenting with a biogas system which will be attached to the guest building and

accommodation of 40 people, whilst providing energy as well as fertilizer. Their main

interest is in performing a trial of this technology so that problems can be identified and

solved before the system is implemented throughout the region (EWB 2008). The aim of

this thesis therefore is to determine the current sanitary situation within Pabal village,

relating the research to many issues that are important to biogas implementation and

adoption. It is desired that local culture and society will be taken into account to

understand the appropriateness of the technology. In order to achieve this, interviews and

questionnaires will be undertaken. These will be discussed in more detail in the

methodology section. It is hoped that the data collected will provide useful information

for use in an implementation scheme for a human waste fed biogas latrine project. The

thesis will ultimately provide a feasibility study into the practicality and appropriateness

of an implementation project in Pabal.

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2. Literature Review

2.1 Introduction

Biogas generation is by no means a new technology to be exploited by populations.

Rather, it has been employed to produce gas and slurry for agricultural fertilizer for

hundreds of years, using a range of fuels and methods (UN 1980). Biogas generation has

numerous benefits for the user and local environment as it is a green and renewable

energy source, often bringing alleviation to many poverty stricken locations across the

globe. However, the development of this technology on a global scale in rural regions,

especially in a developing country context, has been hindered as the decimation of

knowledge has not been successful, uniform or available. Although this technology is

often readily applicable and easily set-up, its adoption has been hindered for the reasons

mentioned previously. Furthermore, local conditions often dictate the design and success

of the technology, with pre-experimentation and feasibility often being required to assess

this. Research has also been undertaken into the socio-cultural aspects of biogas

development, as this can have a significant impact upon the uptake and maintenance of

biogas generators.

2.2 Health and environmental benefits

Rural households in developing countries are often afflicted by the same generic

problems of intermittent water supply, poor sanitation and dwindling energy sources,

with India being no exception. Neudoeffer et al. (2001) examined the energy distribution

of fuel within rural India and highlighted how the population is primarily dependant on

biomass to meet energy needs, with the household sector accounting for nearly 75% of

this, and cooking being the largest household end use, accounting for 90% of the total.

Much of the required fuel is biomass and its demand is currently on the rise, increasing

the issues of sustainable supply and management of biomass resources in rural areas.

Large quantities of biomass energy are wasted because of low utilisation efficiency

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through incomplete combustion in fire stoves (Lianzhong et al. 2008). Around 73% of all

cooking energy requirements in rural areas can be met from biogas (Kishore, 2002).

Research by Agoramoorthy and Hsu (2008) highlights the enormous potential of biogas

plants in relieving ecological stress in India, as of the 125 households implemented with

biogas generators, a total of 79.79 tonnes of forest firewood was saved.

Not only is the local environment increasingly destroyed for this growing demand in

energy supply, but the use of firewood in home cooking has a detrimental effect on the

health of the family members. Thus, respiratory and eye diseases are high in India (Kapdi

et al 2004). Agoramoorthy and Hsu (2008) show that after biogas implementation in

households, the number of times people visited clinics for smoke-related illnesses, such

as eye infection, burns, respiratory problems, asthma, dizziness, headache, intestinal

problems and diarrhoea fell from 6.10±1.25 to 2.62±0.97. Such are the benefits from the

clean burning fuel that Prakash (2005) noted a reluctance of housewives to use firewood

once they became habituated to cook in a smoke free environment when they used

biogas. Biogas implementation schemes therefore often include aims to conserve fuel

wood, reduce deforestation/ environmental degradation and remove/reduce smoke from

kitchens (Kishore, 2002).

2.3 Sanitation benefits

Biogas generation utilising night soil/human waste can have direct improvements on local

sanitary conditions, as it reduces open defecation, where waste can leach into local

streams and cause contamination. The provision of latrines accompanied by biogas are

often more successful when the direct benefit of gas provision can be seen. Improvements

in sanitation often results in better health of the whole family, and reduces the incidences

of disease (UN 1980).

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2.4 Agricultural and economic benefits

The slurry produced by the biogas digester is a rich, fertile source of nutrients for plants

and crops. Its utilisation can increase yield dramatically and reduce the reliance on

artificial fertilisers, thus providing benefit to the farmer as he saves money, and the

environment as it is not overwhelmed with artificial nutrients. The use decreases the need

for chemical fertilisers, with the economic and environmental benefits safeguarding soil

fertility (Prakash 2005). Chemical fertilisers can be expensive and hard to come by in

many communities, and a reduction in their reliance is a positive element of biogas

implementation.

Saving in the quantity of cooking and/or lighting fuel is directly an economic benefit of

the biogas plant to the concerned household with approximately 2 cum of biogas,

equating to 210-150kg firewood per month (Prakash 2005). 70% of households made use

of the slurry in Prakash’s (2005) research. Furthermore, fuel produced locally is not so

vulnerable to disruption as imported sources (Bates 2007), such as grid electricity or

imported bottled gas. Nightsoil-based biogas plants in Maharashtra’s Pune district,

yielded results from the 75 biogas plants in Dehu village supporting this argument. It has

been calculated that the installation of the plants has reduced the demand for LPG gas in

the village by about 100 domestic LPG cylinders per month (Mapuskar 2007).

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2.5 Social benefits

Utilising biogas energy can help reduce the drudgery of rural women and children in their

previous collection of fuel materials from long distances (Lianzhong et al. 2008). As

women in the household are often tasked with fuel collection, the time saved through fuel

collection often creates new opportunities and freedoms for them. Younger members of

the household can attend school with this time saved when previously they could not.

Furthermore, successful biogas implementation can reduce the labour of tasks preformed

by women and girl-children, their consequent exposure to health hazards, as well as

employment in rural areas (Kishore, 2002). Biogas implementation can have wider

ranging economic benefits for non-users and the community as a whole through cleaner

practices and increased conservation of forests (Prakash 2005). Although it is clear that

one biogas generator will not have a significant impact, a successful scheme

incorporating much of the community can help bring lasting benefits to any population.

Biogas fuelled lighting is a major social asset and is often associated with longer periods

for work or study (Bates 2007), combining social and economical benefits.

Thus the clear encompassing benefits of biogas can be seen, having positive impacts

upon human health, sanitation, social elements, local economics and the environment.

Very few other solutions can provide so many benefits under one design. However, the

effectiveness of biogas implementation schemes can be assisted or hindered by a number

of socio-economic influences, each individual to the culture and setting. Drake et al.

(2009) highlight these various influences, and are summarised as follows;

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Age of head of household

As the age of the head of household increases, the chance of adoption of the technology

generally decreases. This is often due to a more open approach by younger members of

society as they are less cautious in adopting new technologies.

Gender of head of household

The gender is not particularly significant in general, even though women are more

involved with fuel collection and energy use. However, this may not be the case in Pabal

however as the Hindu religion has a very strict gender system with women having less

authority then men.

Education

Better education generally results in greater understanding of the technology, including

environmental and economic benefits. However, increased years in education often lead

to more administrative and management based professions, rather than hands-on

professions. Therefore, biogas can often be viewed as a technology for the poor by the

rural educated, but this is often location specific and is unlikely to affect Pabal.

Size of land

The greater the availability of space, the increased likelihood of adoption as the

household has more potential to develop the technology and are not spatially constrained.

Size of household

The greater the household size, the increased likelihood of adoption. Not only is this

important in volume of waste for the generator, but also labour for routine maintenance

and operation of the digester.

Number of cattle

Biogas can offer an effective solution to large quantities of cattle waste whilst also

providing an energy source. A larger cattle herd therefore often increases the likelihood

of adoption.

Location

Each household is individual and location can have either positive or negative impacts on

adoption. Households in more desirable parts of a town or village may hesitate in

adopting biogas as it may not be seen as a desirable technology in that location.

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Income

Generally, a greater income increases the likelihood of adoption as the household has

more capital to invest and use to improve their situation. If a household has very little

spare capital it is increasingly difficult to implement biogas. This also has important

implications for long term repairs and maintenance.

Experiences by Rajam (2003) highlight how social and cultural influences can prevent

development. However, his research shows that after implementation the socio-economic

improvements can create mass strides in the local minds and helps to break away all the

psychological and conventional reservations. It is evident that a successful pilot scheme

can help to develop implementation in socially inhibited locations. The author continues,

that local inhabitants of the research area now realise the importance of hygiene and the

ecological and environmental values. Drake et al. (2009) conclude that an understanding

of the socio economic factors influencing biogas would assist in policy formulation and

implementation of programmes designed to promote voluntary adoption of the

technology by households.

2.6 Financing Issues

Small scale decentralised energy systems are often inhibited by the initial capital cost

required for their set up, even though long term maintenance may be low. Decentralised

energy supply options have high transaction costs associated with putting together

various elements of technology, finance, development and management, which make the

schemes financially unviable (Reddy and Srinivas 2009). Successful decentralised

schemes need to employ designs which are inexpensive, whilst utilising local resources to

keep capital costs to a minimum.

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2.7 Issues of Nightsoil use

Using human excreta as a renewable fuel source can understandably be a difficult social

and cultural issue, inhibiting biogas development and implementation which utilises night

soil. For example the concept of this is unacceptable in much of Bangladesh due to

social-cultural reasons and religion (Prakash 2005).

The taboo over using gas from such a source can severely hinder projects based on such a

fuel. Hindi culture, as found in Pabal, is a structured class system which may not only

affect adoption due to social class, but also how upper classes view the lower classes

(Furedy 1990). Furthermore, although the benefits of using night soil may be understood

and readily accepted, pressure from family, friends and neighbours has previously

prevented adoption (Prakash 2005). If the source of biogas is known to be from human

waste, it can often discourage people from buying food made using such a fuel, or even

accepting tea from a friend or neighbour.

This can potentially be overcome or subdued by an effective education programme,

which aims to highlight the benefits of using such an energy source, whilst showing that

it is a clean substitute to current fuels. Although there is currently no evidence of

educational programmes to alleviate this, it is commonly accepted that education can

overcome this. These issues of acceptability need to be developed as a community project

(Furdy 1990). However, caution must be made not to infringe on the culture of a society

as this may not be accepted.

2.8 Nightsoil Health Concerns

There are possible health concerns over utilizing nightsoil due to potential contamination

through transferring pathogens from human waste. However, these concerns are

unfounded as the process is in fact a positive way of reducing pathogens. It is important

to highlight the research into this which shows how pathogens can be safely removed

through a suitable digestion process. During the digestion process, dangerous bacteria in

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dung and other organic matter are killed, which reduces pathogens dangerous to human

health (Bates 2007). The decay rate of viable bacteria is dependant on many factors, of

which the temperature, treatment time, pH, volatile fatty acids, batch or continuous

digestion, bacterial species and available nutrients are particularly important (Sahlstrom

2003). It is important to highlight the research into this which shows how pathogens can

be safely removed through a suitable digestion process.

2.9 Biogas Adoption

Biogas adoption can be affected by any number of the above influences, with the

magnitude of the significance of each one depending upon the locality and socio-cultural-

economic factors. Extensive research by Prakash (2005) into biogas schemes in

Bangladesh provides useful insight on biogas adoption methods and important adoption

factors. The majority of households which chose to adopt biogas did so after a family

discussion, rather than the head of household making an independent decision (of which

the majority were male). Only 14% however were motivated by other plant users to

install biogas, yet existing plants are to become a tool for promotion and extension of the

technology, intending to increase this as a useful adoption tool. Kishore (2002)

experienced problems when the technology was seen as too cumbersome, with models

promoted being premature prototypes with very low operational reliability. The design

and operation of biogas generators is very important in the acceptability of the technology

to the recipient.

2.10 Biogas Implementation

Agoramoorthy and Hsu (2008) note that the selection of households for implementation

involves three main requirements;

1. Availability of an appropriate quantity of daily feed, cattle dung, night soil etc.

2. Availability of water.

3. Access to land near the kitchen to construct plant.

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Bates (2007) highlights that a number of certain technical, social and financial criteria

must be met if implementation schemes are to be successful;

1. Technically, the availability of sufficient raw feedstuffs is required, as well as a

sufficient temperature of the digester and the skills and technical know-how.

2. Socially, it is more likely to succeed if there is a market for fertilizer, with the

promotion and dissemination of benefits needed if it to be accepted.

3. Financially, set up costs can be relatively high so many may not be able to afford

such a scheme, thus micro credit schemes are advised.

Each household will have individual settings and requirements, yet by using the above

elements and tailoring them to Pabal’s need, a good estimation can be established for

each household as to the implementation of biogas.

Relevant limitations which are often evident in many households and locations, must be

acknowledged as they have a paramount influence over implementation. Firstly is income

and available funds of the household. Depending on the specifics of the programme, the

household may have to provide a contribution or pay for the whole cost of the digester.

Furthermore, repairs and maintenance will require future investment, albeit a lower cost

than the initial implementation. Some families may not have the free capital to provide a

digester for their household. A programme will therefore require information on the cost

of a digester.

Second is the capacity of the location to produce, construct or provide biogas digesters.

This is mainly dependant on design, as construction, materials and skilled labour may be

required. Many towns or villages may lack the infrastructure to do this, therefore

requiring one or all of the above to be imported from a different locality. The two

elements can have a dramatic impact upon the logistics of creating an implementation

scheme and cannot be understated in their importance.

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2.11 A Novel Design for a Biogas Generator- Joanna Read’s Design

A biogas digester design was previously prepared for EngINdia by Joanna Read in 2008.

The ‘plug flow’ type digester is designed to produce 3.2m³ of biogas per day for a family

size of eight people, with the ease of construction, operation and maintenance being

paramount if the generator is to present a viable alternative energy source (Read 2008).

The benefit with this design is that it does not require water for its operation and should

be available for use all year round, however the design cost is currently too great. The

design still needs to be adjusted and a trial of the digester undertaken within Pabal.

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3. Methodology

3.1 Previous work

Local development work has been limited, with Vigyan Ashram being the only external

research centre providing intuitive designs for numerous practical problems. EngINdia

and Engineers Without Borders have also provided design solutions to issues in Pabal,

and highlighted numerous problems which need to be addressed. Jo Read’s biogas design

is one example of this, as described earlier. With relation to biogas, there is very limited

previous experience from Pabal to capitalise upon for this research project.

Vigyan Ashram have previously experimented with a flushing biogas latrine of 1m³, yet

the results were not favourable for a practical biogas generation. The results indicate that

too much flushing water was used and not enough night soil was supplied for the

digestion process. To understand the local conditions, another pilot scheme is to be

undertaken with a greater focus on making a suitable experiment. The results from the

Ashram experiments will be useful for the design and suitability of a biogas scheme

within Pabal.

3.2 Theoretical aspects of methodology

The research was carried out in Pabal village, Maharashtra, over a period of six weeks in

coordination with Engineers Without Borders and EngINdia. This chapter describes the

methods used to achieve the objectives outlined in the aims and objectives section.

3.2.1 Newman’s four dimensions of research

Neuman (1999), highlights that in social research, there are four dimensions of

description; the purpose of the study, its use, its time dimension and the data collection

techniques used.

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3.2.2 Purpose of the research

As the aim of this research was to understand the current situation within the village, with

regards to sanitation, and to review the situation. Under Neuman’s (1999) views, it can be

described as a descriptive piece of research. Although describing the situation can be

useful, explanatory work is required to obtain a complete assessment to understand what

is already known.

3.2.3 Use of the research

The thesis consisted of the research and feasibility component of EWB’s human waste

disposal project in Pabal village, which links biogas with sanitation. Neuman (1999)

divides research into two clear categories, those of basic and applied. Basic research aims

to support and contribute to known theoretical knowledge, whilst applied research relates

to research that is directed at a specific problem and aims to use the results in a practical

fashion. The results obtained from this thesis can be used to construct a project feasibility

study and be used in an implementation scheme.

3.2.4 Time dimension of the study

The research comprised of 22 questionnaires and tailored interviews, conducted over the

six week period, with an aim of understanding the current sanitation situation and biogas

appropriateness. Although a greater, more in-depth survey was desired, the project was

limited economically and temporally which restrained this. Furthermore, there was no

previous data available to utilise or compare with. Therefore, a case-study approach was

undertaken (Neuman 1999).

3.2.5 Data collection techniques

Both quantitative and qualitative data was required for the project in order to understand

the technical aspects of the biogas digester, and the social aspects relating to sanitation.

Qualitative data is the best source of information to understand socio-cultural aspects

within a community, looking at community attitudes and perceptions. Theory can be

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developed from the analysis of this data, which is primarily collected in the form of

interviews and questionnaires.

3.3 Interview bias

Neuman (1999) highlighted how bias can affect the results of the research, changing the

outcome of the findings. Such bias could come about through the respondent

misunderstanding the question or even lying to please the interviewer, or due to the

presence of others. Bias can be limited through highlighting the aims of the research to

the interviewee so they can understand the situation, with open ended questions to allow

in-depth answers to be provided by the respondent. As is typical in any Indian village, the

presence of unusual activity promotes curiosity. Thus when interviews were held outside,

a crowd often gathered. Although this did not hinder the interviews, the presence of

others may have had a direct impact on the answers of the interviewee, particularly on

sensitive subjects. It is often noted that in traditional villages the culture prevents women

from speaking with foreigners and are not allowed to go outside, being limited to the

home. However, this problem was not apparent in Pabal, with women conducting many

of the interviews and even openly correcting their husbands on certain facts relating to

the household.

Some difficulties were encountered when the interviewee could only speak Marathi, the

regional dialect, and not Hindi, which was required by the interpreter. Whenever required

and possible, a second interpreter was introduced, or the interview was conducted

through another family member who could speak Hindi. Translation from one language

to another, especially through a third party can incur bias as some answers may be

simplified or altered. When translation was required through three languages, the risk of

bias was increased. Nevertheless, at every opportunity the utmost care was taken to make

sure that bias was limited and did not affect the results.

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3.4 Interviews

Baseline data is required to understand the actual needs, trends and realities within the

village, with regards to sanitation and biogas. As previously shown, local social,

economic and cultural issues are paramount to successful implementation. With these

elements in mind, it was decided that semi-structured interviews were required to obtain a

greater understanding of the village and its people. Tailored interviews would also be

required to ensure that specific data on the village and previous biogas schemes are

obtained.

Semi-structured interviews were constructed to include thirty-six questions each,

focusing on the village, water quality and treatment, sanitation and finally biogas. The

interviewee’s details were also taken at the end of the interview to obtain a greater

understanding about their situation and to provide useful information relating to the

factors that Drake et al. (2009) highlight for their importance when studying the social

side of biogas. These included the interviewee’s age, sex, size of family, size of land, age

and sex of the head of household. Wherever possible, their education and income was

taken into account, yet it is noted that this can often be a sensitive subject and results are

not always obtainable.

The questions were placed in a logical order so that conversation could flow more freely

as they were relevant to the last question. Although each question focuses on a specific

area with a required answer, they allow scope for the interviewee to elaborate on the

subject and give a fuller response. This is important as it creates a better understanding of

the situation as the interviewee can detail their feelings about the subject, rather than a

limited answer to a specific question.

The interviews were conducted throughout the village and hamlets, with random transects

taken through the village itself and individual days spent in a specific hamlet.

Interviewees were chosen with a view to their openness and availability to spare the time.

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In both cases, the aim was to ensure that biogas is an appropriate technology for the

village and its community, providing an adequate solution to the problems there.

3.5 Pilot

The 1m³ rising-dome biogas digester with attached latrine was prepared by Vigyan

Ashram to begin the pilot scheme trials. For the cultivation of bacteria to produce the gas,

400kg of cattle faeces was used to initiate the start up period. After this period the latrine

will be used in accordance to the UN guidebook (1980) for a 1m³ rising-dome biogas

digester run on night soil. This requires 8 people to use the latrine daily and a maximum

of 1 litre of washing and flush water to be used. It is important that there is enough

human waste available to produce the gas whilst it is not too diluted with flush water.

Issues which need to be considered are the quantity and quality of gas retrieved, any

issues with volume of flush water, if the number of people using the latrine is sufficient,

length of time for the start up period and general practicality of the project.

Figure 4. Biogas generator

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Figure 5. Biogas Latrine.

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4. Results and Analysis

4.1 Introduction

The results are set out in a manner so that specific areas can be easily referred to for

information, which may be useful for project implementation. As in line with the

objectives, the cultural and social issues have been outlined to assess the importance of

each one, and to make the conclusions clearer. Each interviewee was offered

confidentiality of their response, yet as all were happy share their information, full names

are used. Each quotation is followed by the interviewee’s surname and initials, and then

by their interviewee number and questionnaire number. This is for clarity and ease of

reference. The results consist of twenty-two individual interviewee data sets, with another

three tailored interviews. These results are a small selection which aims to represent the

majority in the village. Although it is desirable to interview as many people as possible,

thus making the results more representative and accurate due to differing opinions, they

nonetheless provide a useful insight into the current situation within the village. Thus,

every care has been taken to interview people from various locations throughout Pabal

and its hamlets, from different employment, wealth and gender.

The interviews were often conducted in the afternoon as during the morning most were

working and then sleeping during the heat of the day. In the evening during certain weeks

without night time electricity it was too dark so the afternoon proved the best time.

However, at this time it was also noted that many of the men were out so the women of

the household were more accessible for interviewing. A table can be found in the

appendix which shows a breakdown of the classifications to which each household was

based, depending on size of land and location within the village.

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4.2 The current situation in Pabal

4.2.1 How the village is viewed by people living there.

Almost all of the interviewees had very positive opinions of village, often saying ‘I like it

here’ and ‘it is very nice’, without any direct dislike towards Pabal. A number of

interviewees highlighted some of the problems in the village. (Kedar, C.A. 12:1)

commented that the problems ‘Are not so good and not so bad. It is often the same

problems everywhere in India of no drinking water. The piped water here is not so good

and requires treatment’. Interviewees’ 15 and 21, (Choudhari, R.D 15:1) and (Jadhav,

B.N 21:1) echo this view, saying that ‘It is very arid and there are a lot of water

problems’ and that ‘the scarcity of water is the main problem’. (Salankar, P.G 5:1) also

commented that ‘the lights are bad and there are a lot of mosquitoes’.

4.2.2 Changes in the village.

The results generally indicate that there have been great improvements in the village,

with the construction of schools, roads, water infrastructure, electricity and

communications. The ‘German Arthsahayya Project laid down the new pipe network’

(Roshkar, V.S 5:4), under a contract. These improvements in water have meant that

‘people used the well and it required a lot of labour’ but ‘Now water is in the households’

(Salenkar, P.G 5:5). (Dhole, R 19:4) notes how the village has benefited from ‘A lot of

links have been made with bigger towns and cities, including trade and business’. The

growth of the village is evident, yet this is not without problems. ‘Before it was nicer and

cleaner, but now people throw rubbish outside and even more people are coming’

(Pancar, A 18:4).

4.2.3 Infrastructure, development routes, hierarchies.

From the interview results, most people agree that the Grampanchayat makes the majority

of decisions within the village. Each area of the village and hamlets are represented by

elected members, who are headed by the Sarpanch. (Jayatas D.P 1:6) attributes the

development to the Grampancyahat, saying how ‘The local committee has helped’ and

that ‘The Grampanchayat and police station’ make the decisions (Jadhav, A.R 2:9).

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‘Every decision is made there’ (Pingale, M. P 6:7). (Sambhadas, R.S 8:8) also

commented on the infrastructure, saying that ‘There are facilities but they are not looked

after or taken seriously’.

4.2.4 Summary

The village, like many in India, has seen development in numerous different areas in

recent years and is fondly regarded by those that live there as their home, a nice place to

live. Some interviews (Pingale, M.P 6) give very positive answers about the village,

whilst many other interviewees can see how there are still some problems evident and are

happy to share both sides of the story. The Grampanchayat is an elected village

committee headed by the Sarpanch, an elected leader. Each area within the village and

surrounding hamlets elect a local representative who then joins the Grampanchayat to

discuss local issues.

4.3 Sanitation

4.3.1 Waste disposal problems

There is no central waste disposal system within the village, and this is made evident by

the waste around the centre of the village. ‘There is no refuse collection so we burn our

waste and compost the organic matter’ (Roshkar, V.S 4:26). Some results suggest that

much of the waste composted if it is organic, whilst the rest is burnt, (Sambhadas, R.S

8:27) and (Dada, T 17:26). Others ‘Throw it outside’ (Ratnabarki, S.S 11:26), whilst

(Rathed, S.M 13:26) puts it ‘Every two days into a pit the Grampanchayat has made’. It

is evident that there are numerous methods of dealing with waste in the village, with

different methods being chosen for their suitability to the household.

4.3.2 Latrine Access

Out of the twenty-two questionnaires undertaken, twenty interviewees have access to a

private household latrine, with five having them indoors, and fifteen having them outside.

There are two communal latrine blocks in Pabal, constructed by the Grampanchayat for

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the village (Rathed, S.M 16:24), and were constructed before household latrines were

compulsory in the village (Jadhav, A.R 2:32). However, no interviewees found the need

to use them as those with latrines did not require them. ‘The Grampanchayat made a law

for every house who could afford one to have a toilet’ (Roshkar, V.S 4:26). Those

without latrines said they used other methods, such as open defecation. Although

(Pingale, M.P 6:24) comments that they are good and that ‘people use them, they are not

in bad condition’. Others suggest that ‘they are not good as they are not clean’ (Jadhav,

R. 9:42) and ‘It is a good idea but everyone has a different idea of cleanliness so

sometimes they are not kept clean’ (Choudhari, B.W 16:24).

4.3.3 Prevalence of open defecation

In a recent law, ‘The Grampanchayat has banned it, so no-one does it around here’

(Ratnabarki, S.S 11:25), with many other interviewees firmly stating that it does not

happen in the village anymore (Jayatas, P.D 1:33) and (Dada, T 17:25). However,

experience by the author and other interview results suggests otherwise. ‘Yes, people do.

The Grampachayat brought in a law a year ago so it has reduced it with a Rr1200 fine.

90% of people have a latrine now as there is a Rr2,000 grant for latrine building’

(Rathed, S.M 13:25). ‘Some people around here do but that is only if they can’t afford

their own, don’t have space for one or there isn’t enough water’ (Choudhari, R.D 15:26).

Other interviewees admit that they have no other option as they do not have a latrine,

saying simply, ‘yes, we do’ (Inamdas, S.H 14:25) and ‘We have to go outside. We own the

house but not the land so we don’t have permission to build on it. No-one wants to help,

the Grampanchayat won’t listen’ (Pancar, A 18:23).

4.3.4 Summary

Without a centralised waste disposal system, or official solution to waste disposal, the

village suffers as people provide a solution for themselves and deal with the problem in

different ways. Figure 3. shows a photograph of the village high street and waste allowed

to build up in the gutters. The village has seen a lot of development in the sanitation

sector, with the majority of households owning or having access to a latrine. The success

of this it seems has been due to a government incentive to improve the sanitation situation

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within rural villages, through providing incentives to construct a household latrine.

However, this problem is not completely solved as open defecation is still apparent, albeit

on a smaller scale.

4.4 Biogas

4.4.1 General opinions on biogas

The interview results suggest that biogas is an accepted technology, as the majority of

interviewees had some level of knowledge and a positive opinion about it. This was not a

common trend however, with a number of interviewees unsure about the technology,

saying ‘I don’t know a lot about it’ (Pancar, A 18:27) and ‘I do not know what it is’

(Ratnabarki, S.S 11:27). (Jadhav, A.R 2:35) adds, ‘Don’t know much about it, no-one has

told us about it. It is gas but don’t know much more’.

4.4.2 Acceptability of using human waste

When confronted with the question ‘Is it acceptable for you to use gas produced from

human waste (faeces)?’ the author received many different answers, to greater and lesser

extremes. As highlighted in Table 1, ten interviewees viewed nightsoil as an acceptable

input for a biogas digester, whilst twenty-two did not like the idea of it. ‘I do not want

gas from human waste, it is dirty and I don’t like the idea’ (Jadhav, A.R 2:37). It is

viewed differently from cow dung as ‘People’s minds don’t link it to dirty as it often is

used for making houses and fertilizers. That is not the same with human waste’ (Rathed,

S.M 13:29). Others take a middle ground, saying how it can be used for some things but

not everything. ‘It is very bad that they use human waste. It is not good for cooking but

lighting would be OK’ (Inamdas, H.S 14:29), ‘We don’t mind using it but the idea of

using it for coking is not good’ (Choudhari, B.W 16:30) and ‘Yes, I feel I do if I produce

it. Human waste should have a separate use for lights, but not for cooking’ (Rathed, S.M

13:31). Others however, are happy to accept the idea as (Sambhadas, R.S 8:30) suggests

that ‘Not many people here understand what it is. Yes, it is acceptable’ and ‘Yes,

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according to my opinion it is fine’ (Kedar, C.A 12:29). (Pingale, E.K 20:30) sums up the

majority of the farmer’s opinions with ‘I won’t do the human one, but I will with cattle’.

4.4.3 Towards an implementation project

(Jayatas, D.P 1:37) notes that their HP fuel source is ‘Bought gas is from a human waste

biogas plant so acceptable’. The biogas plant in Pune, a nearby city, distributes HP gas

from a nightsoil fed biogas plant. This HP gas however, can be an unreliable energy

source. ‘Biogas is your own and a regular source. Sometimes with HP gas they say they

don’t have any and run out. It is not a big problem but it does happen’ (Pingale, E.K

20:27). He also adds that ‘Yes, I really want more [information], but if it was a group

scheme then it would be cheaper. I would provide half but on my own it is too much’

(20:31). ‘For me it is not acceptable. If science says it is fine, then it is. The

Maharashtran people don’t understand a lot so introducing new things to them is good’

(Dhole, R 19:29).

4.4.4 Problems towards an implementation project

Many interviewees’ suggest a number of problems which may affect an implementation

project. Some highlight how there are ‘Not enough persons in household to be interested

in biogas’ (Jayatas, D.P 1:37), ‘It could be useful but we use HP gas and don’t have

enough animals’ (Jadhev, R 9:28) and that ‘We have no cattle here, there is no point

learning more. We won’t be able to use it’ (Choudhari, R.D 15:32). (Jadhav, A.R 2:39)

does not see the relevance for biogas as ‘We can use the container gas, so there is no

need for biogas. It is not relevant to us’ and (Roshkar, V.S 4:37) ‘We are used to using

the canisters so we don’t need to change’. Others view the cost aspect as being important,

as ‘I would be interested, it would be useful, but I don’t have the investment to start it off’

(Choudhari, B.W16:32), ‘It could be useful, but the cost is too great’ (Dada, T 17:28) and

‘Yes, if it is in my budget and if everyone else did it too’ (Pancar, A 18:32) adds.

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4.4.5 Summary

Knowledge on biogas within the village is generally good, as most people know it is an

energy source collected from animal dung, which has previously been used in the village.

However, the idea of using human waste is new and not readily accepted. A number of

problems have been highlighted which may hinder an implementation scheme, including

acceptability, quantity of feed, cost and want to adopt the technology. (Jayatas, D.P 1:37)

and (Dhole, R 19:29) indicate that education may be important in initiating and

strengthening a project. (Pingale, M.P 6) provides a useful case study. The household

were initially against biogas as they used the cattle dung as fertilizer on their fields.

However, once they understood that the slurry waste from the generator could be used to

the same affect, they were more open to the idea of a digester. They highlighted that cost

was still a main deterrent.

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Table 1. An overview of the interview results.

ID Head of H/H Age Size of Family Land Employment Location Education Fuel Livestock Latrine Human Waste Contribution Adoption

1 M 60 2 None Shopkeeper Central Pabal Educated HP gas No Indoor Acceptable N/A N/A

2 M 32 4 Limited Housewife Central Pabal Educated HP gas No Outside Not Acceptable No No

3 M 6 Available Housewife Central Pabal Educated HP gas No Indoor Acceptable N/A Yes

4 M 42 5 Available Student Pabal Outsirts Educated HP gas No Outside Acceptable No No

5 M 26 7 Limited Business Central Pabal Educated HP gas No Indoor Not Acceptable N/A No

6 M 85 10 Open Farmer Outside Pabal Poor Wood + HP Yes Outside Not Acceptable Yes Yes

7 M 55 10 Open Librarian/farmer Outside Pabal Educated Wood + HP Yes Outside Acceptable Yes Yes

8 M 53 3 Limited Student/shopkeeper Central Pabal Educated Everything No Indoor Acceptable Yes Yes

9 M 42 4 Available Student Pabal Outskirts Educated HP gas Yes Outside Not Acceptable Yes No

10 M 40 6 Open Student Outside Pabal Educated HP gas No Outside Acceptable Yes Yes

11 M 30 4 Limited Housewife Central Pabal Educated HP gas No Outside Acceptable N/A N/A

12 M 50 2 Limited Teacher Central Pabal Educated HP gas No Outside Acceptable Yes Yes

13 M 41 2 Limited Shopkeeper Central Pabal Educated HP gas No Indoor Not Acceptable Yes Yes

14 F 45 6 None Housewife Central Pabal Poor HP gas No None Not Acceptable N/A No

15 M 6 Available Housewife Outside Pabal Educated HP gas No Outside Acceptable N/A N/A

16 M 52 3 Available Farmer Outside Pabal Poor Firewood Yes Outside Acceptable Yes Yes

17 M 35 6 Available Farmer Outside Pabal Educated HP gas Yes Outside Not Acceptable Yes Yes

18 F 29 4 None Tailor Pabal Outskirts Educated HP gas No None Not Acceptable Yes Yes

19 M 23 3 Open Farmer Outside Pabal Educated HP gas Yes Outside Not Acceptable Yes Yes

20 M 70 10 Available Farmer Outside Pabal Educated HP gas Yes Outside Not Acceptable Yes Yes

21 M 52 5 Available Teacher Outside Pabal Educated HP gas No Outside Not Acceptable No No

22 M 56 5 Available Farmer Outside Pabal Educated HP gas Yes Outside Not Acceptable Yes Yes

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Figure 6. The distribution of number of persons per household.

Figure 7. Acceptance of nightsoil.

Figure 8. Biogas Adoption.

Biogas Adoption

0

2

4

6

8

10

12

14

1

Willingness to adopt

Nu

mb

er

of

ho

useh

old

s

N/A

Unwilling

Willing

Acceptance of nightsoil

0

2

4

6

8

10

12

1

Acceptability

Nu

mb

er

of

ho

useh

old

s

Acceptable Not Acceptable

Distribution of number of persons per household

5-7

1-4

8-10

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4.5 Overview of Questionnaire Data

Table 1. shows the overall results of the questionnaire data, including important

aspects highlighted by Drake et al. (2009), and willingness to contribute and adopt. A

table in the appendix provides the definitions for size of land and location. The results

below are outlined with relation to Drake et al. (2009):

Gender of head of household

Out of twenty-two households, twenty had a male head of house, 90.9% were male

and only two had females.. However, the majority of the interviews were carried out

with women and not done with the head of house.

Age of head of household

The mean age of the age of household is 45.9.

Size of Land

Three households were deemed to have no land available. Six households were

deemed to have limited land available. Four households were deemed to have open

space. Nine households were deemed to have available land.

Size of household

The average household size 5.1 persons per household, with 12 interviewees having a

family size of five or greater. Figure 6. shows the distribution of people per household

within the village. The majority of households are in the smaller group of 1-4 persons

per household.

Availability of cattle

Eight households had cattle and fourteen did not. Should a nightsoil based biogas

generator need supplementing, only a few households have livestock to do this with.

Location

Nine interviews were in the centre of Pabal, three were on the outskirts of Pabal and

ten were outside Pabal, located in hamlets.

Fuel

Eighteen use HP gas, two use wood and HP gas, one used Firewood and one uses

everything. Most people in Pabal use HP bottled gas as their main source of energy

within the household.

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Contribution

In six cases, it was not applicable as they were not interested, three said they would

not contribute to the cost and twelve said they would contribute to the cost. The

majority of people would be happy to make a contribution to the cost of instillation.

Adoption

Figure 8. shows the number of people willing to adopt the technology.

In three cases it was not applicable, six were not interested (31.6%) and thirteen

wanted to adopt the technology (68.4%). Although not every household is suited to

biogas adoption, this majority to adopt is a positive strength towards an

implementation project.

Human Waste

Figure 7. shows the number of people who find using human waste acceptable and the

number who do not. Ten interviewees accepted nightsoil as a fuel input (45.5%) and

twelve did not accept nightsoil as a fuel input (54.5%). This majority opposition

towards utilising nightsoil is a negative impact towards an implementation project.

The majority of interviewees did not like the idea of using human waste in a biogas

generator.

4.6 Tailored Interview Results

4.6.1 Previous Biogas Schemes

It is evident that there has previously been a government led scheme, in which

subsidies were given to farmers as incentives to construct biogas generators. ‘20 years

ago with the help of the government, biogas subsidies for farms started’ (Sarpanch

a1). Initially, around one hundred people adopted the scheme (Jadhav B.N b), yet the

majority of them are no-longer in use. There are a number of reasons for this, as it

may be ‘Because they could not maintain them. The iron tank may have ended its

lifespan and they can’t afford another one’. It is also evident that there was no

government support after implementation for repair and maintenance, thus resulting in

the reduction of working biogas generators today. ‘Those that have them left don’t

know what to do as there is no help and support from the government scheme, no

training’ (Chaudri Wasti c). Figures 9. and 10. show biogas generators from this

previous scheme which are still operational, owned by a farmer and a teacher from

Pabal.

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4.6.2 Future potential for Biogas

Currently, there are no plans within the village, but this does not mean that there is not

potential. ‘The concept is very big, no-one can follow it. It is good if someone can

come here and show us how to do it and the benefits, but there is no idea here. We

need a revelation to bring back these technologies’ (Sarpanch a3). ‘Maybe it is

possible to have another scheme and maintain it, but the problem is that people are

scattered’ (Jadhav B.N b). The previous scheme was promoted through newspapers

and TV, thus attracting a lot of attention and becoming successful in the initial stages

of development. ‘The subsidies are there, but no-one is here to teach us and set it up.

15-20 years ago it was a new concept, but no-one cares now’ (Sarpanch a3).

Figure 9. A local teacher’s biogas generator.

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Figure 10. A local farmer’s biogas generator.

4.7 Pilot Biogas Project

The set-up for the trial biogas scheme was successfully accomplished, with the

following notes being taken:

After 15 days (05/07/09), the first batch of dung had created an amount of gas to the

capacity of the digester. The pressure of the gas was sufficient for it to be released

from the outlet at the source, yet was only flammable for a maximum of 10 seconds,

with moisture being evident in the gas. There was not sufficient pressure to reach the

kitchen initially and it was not flammable at the cooker. The gas was subsequently

drained so a new batch could be generated. This will have a greater percentage of

methane and therefore be more flammable as the bacteria have had more time to

develop.

However, the Ashram informed the author that the pilot scheme did not continue due

to the climate being cloudy all the time; hence not much biogas was produced and no

results have been collected. The project will begin when the climate improves. This

provides important information on how the climate can influence biogas generation.

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4.8 Overall Summary

The results show a positive foundation for a biogas implementation project. The

results cover various aspects important to biogas schemes and provide useful

information on reasons why a project may or may not work. The interviews are

helpful in achieving the thesis’s aims, to understand the sanitary situation in Pabal, to

assess the appropriateness of the technology, and to include any important social or

cultural influences relevant to the scheme. It is evident that certain parts of the

community should be targeted and there will be more acceptability and greater

success in different areas to others.

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5. Discussion

5.1 Introduction

It is evident from the results that the previous government led biogas scheme had

initial success in the provision of biogas digesters for farmers and villagers. They

benefited from the free source of energy and fertilizer that subsequently went on their

fields. However, due to a lack of education and maintenance, this scheme ended as the

biogas generators fell into disrepair. Although a couple were lucky enough to keep

theirs running, the majority of people had to revert to alternative sources of energy. It

was highlighted that a lack of education and maintenance were paramount in the

decline of the last government led scheme. The results indicate that biogas is an

appropriate technology for Pabal as it is commonly accepted as a good source of fuel,

with the majority of people having some understanding of it.

5.2 Review

With a 68% of people interested in this technology, a case is already set to consider an

implementation scheme. Furthermore, it was felt that of the 32% who were not

interested in the technology, a number could be persuaded through education and

promotion. The questionnaire aimed to understand the current situation and views

within Pabal, rather than promote biogas. This was important for the aims and

objectives, outlined previously. However, although the technology may be willingly

adopted, there are numerous practical and socio-economic factors which need to be

taken into consideration beforehand.

Primarily, the quantity of human and/or cattle waste available for the biogas digester

is a major deciding factor in the practicality of any scheme. Without enough feed, the

generator simply won’t produce gas. This divides the results into two important

sectors: Those with enough feed from either household members or cattle, and those

who do not have enough people to use the latrine or any cattle. With the average

household having a family size of 5.1, and the requirements for a 1m³ rising-dome

biogas digester run on night soil needing 8 people (UN guidebook 1980), the average

family size is not large enough. There is potential however to supplement this with

cattle dung, providing the household has livestock. From the results, there are only six

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households to which this would apply and only three households with eight or above

family members.

The proposed solution aims to alleviate the problem of open defecation and poor

sanitation through running a biogas generator on nightsoil. However, the results

indicate that there is a majority resistance to this, as it is seen as unhygienic and dirty.

A similar situation was experienced by Prakash (2005) in Bangladesh, as it was

deemed unacceptable to utilize or certainly cook from gas produced by such a source.

In Pabal, 55% of interviewees did not wish to use gas from a biogas generator run on

human waste. Nightsoil run generators are a new concept in Pabal, and although the

results are unfavourable, they are encouraging. A strong educational programme

could highlight the benefits of biogas run on human waste, whilst also quelling any

doubts about the hygienic standards of such a practice. ‘For me it is not acceptable. If

science says it is fine, then it is. The Maharashtran people don’t understand a lot so

introducing new things to them is good’ Dhole, R (19:29).

The availability of land was naturally varied from location to location, with some

offering greater potential for implementation to others. Generally, the results were in

favour of development, with only three households being limited spatially.

Furthermore, many biogas digesters designed on a household level with limited space,

removing the availability of land as an essential limitation.

Prakash (2005) outlines a complex relationship between age and gender of the head of

household to the adoption of biogas. This would suggest that a male head of

household may hold different views to it, often negative, compared to a female one.

No correlation was found in the results to this view, even though the majority of the

heads of household were male.

The average age was 45.9 years old, with the youngest being twenty three, and eldest

eighty five. No correlation was seen here either between age and adoption.

Furthermore, the mix of male and female interviewees is fair, and no correlation can

be seen between adoption and sex. It was also noted that during interviews with either

male or female partner, the other felt at ease to add comments and opinions to the

interview, without any attached stigma. This suggests that there is no hierarchy

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between males and females and that females are not treated as a second class citizens.

It is noted though that this is a small data set and any correlation may no be evident

over greater results.

The majority of villagers in Pabal use HP gas as their main energy source, which costs

Rs 200 per canister (14kg). There is a certain amount of apathy towards converting

from one gas source to another, especially when the initial capital costs for investment

is so high. A reliable, decentralized energy source could provide a suitable alternative

to HP gas, yet the benefits of this need to be highlighted if the scheme is to be

successful, as HP gas is convenient for many people.

Any biogas implementation project requires a certain amount of input from the

beneficiary to instil a feeling of ownership and investment to promote sustainability.

Users should be provided with basic orientation on various aspects of operation and

maintenance such as proper feeding of the plant, optimal use of biogas, effective

application of slurry and timely maintenance of plant components (Prakash 2005).

Thus, the results are encouraging as 80% of interviewees who were interested said

they would contribute to the initial cost. When a scheme with full information on the

project is proposed, it is likely that those who were initially against contributing

would, as the benefits would be seen.

The three criteria outlined by Bates (2007) which are important if an implementation

scheme is to be successful are related to the results below:

1). Technically, the availability of sufficient raw feedstuffs is required, as well as a

sufficient temperature of the digester and the skills and technical know-how.

As the results show, sufficient feedstuff is currently an issue with regard to utilizing

nightsoil and having enough members in a family to produce enough biogas. A

scheme should focus on households with this potential, or ability to supplement their

biogas generator.

2). Socially, it is more likely to succeed if there is a market for fertilizer, with the

promotion and dissemination of benefits are needed if it to be accepted.

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The majority of farmers in Pabal require fertilizer for their fields, using dung cakes

prepared from cattle dung, or artificial chemical fertilizer. There is evidently a market

for fertilizer in Pabal.

3). Financially, set up costs can be relatively high so many may not be able to afford

such a scheme, thus micro credit schemes are advised.

If government subsidies are still available, then these need to be exploited for the

project. A design needs to be made which is affordable and available to those with

lower incomes.

5.3 Conclusions

The aim of this project was to understand the current sanitary situation within Pabal,

to assess the appropriateness of the technology; relating it to social and cultural

influences, and to determine the suitability of a biogas development project in the

village.

The majority of results are in favour of an implementation project. However, the issue

of quantity of feed and the use of nightsoil poses considerable opposition. This would

suggest that a household level biogas generator run on night soil would be an

impractical solution for a twofold reason: Households are not large enough to provide

adequate feed for biogas generation, to which there is a lot of social stigma and

opposition to such a fuel source. To this end, it is evident that a human waste disposal

project need to be tailored to those with enough human or animal waste, along with

other practicalities as stated above.

It is paramount that an education program coincides with this, to highlight the benefits

of the project and provide information on long-term maintenance and sustainability.

Ideally, a follow up project would ensure this. ‘24 years ago people here used to use

gobar gas. We need the old technologies again but they have been lost. Once they got

old we could not replace and maintain them. We need to go back to them’ Pingale,

E.K (20:4). Biogas is not an uncommon technology in Pabal. It needs reinvigorating

with a strong development project, designed to meet the aims highlighted throughout

this thesis, and offer support through education and maintenance.

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6. Recommendations

6.1 Introduction

This thesis has outlined numerous elements important in the start-up, implementation

and success of a biogas project, with specifics to Pabal. The information collected

here will be useful in planning an implementation project and developing biogas

within the region.

6.2 Elements to be reviewed

It is firstly imperative that the pilot scheme at Vigyan Ashram is re-instated and

results are collected from this. It will be important to review local conditions and

tailor a design to the specifications outlined by the results. Jo Read’s design needs to

be reviewed and ideally constructed in Pabal to run similar a similar project to the

initial pilot scheme, and outline its strengths and weaknesses.

It is evident that a project which utilizes nightsoil will not be immediately met with a

warm reception. The concept of using human waste for a biogas fuel could either be

overcome through an education program, or through using the fuel to provide an

alternative end product, like street lighting. This has been suggested by a number of

households as Pabal currently has no street lights.

Clear beneficiary targets need to be made to which the scheme should focus, using the

results produced here. Although the amount of data is currently limited, the basic

requirements are highlighted. The NGO should identity target groups and the

community development necessary to enable the group to acquire the capabilities to

take and run energy service schemes (Reddy and Srinivas 2009).

Furthermore, the importance of providing training and orientation for biogas

implementation has previously been highlighted throughout this thesis. Any potential

scheme cannot underestimate education and continual support, and it is highly

recommended that these be included in the project.

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It is suggested that another biogas scheme be implemented, at least for rural farmers,

if not for the village as a whole. As most people have personal latrines and the

communal ones are not particularly popular, it seems that a community scheme or a

sharing scheme would not be appropriate, yet this can still be considered by the

Grampanchayat. The use of human waste appears to be more successful when it is

associated with and institution such as a school or hospital rather than an individual

household (Bates 2007). Although the price of biogas digesters have increased,

government grants are still available, yet capital for the scheme needs to be

developed. There are many routes an implementation plan can take, and it will have

support from the community as they have shown their enthusiasm towards it.

Promotion, education, maintenance and sustainability are crucial in a successful

implementation project, and these need to be considered.

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APPENDIX

SIZE OF LAND LOCATION

None There is no room for any form of digester Central Pabal Along or near the highstreet

Limited A smaller design could potentially be considered Pabal Outskirts

At the fringe of the village, near the main roads

Open A digester could be installed Outside Pabal Usually one of the hamlets

Available Available space is not an issue