Bui Xuan An1, L. Rodr�guez J.2, S.V. Sarwatt3, T.R. Preston4 and F. Dolberg5
The authors can be contacted as follows: 1 University of
Agriculture and Forestry, Thu Duc District, Ho Chi Minh City, Viet Nam, e-mail:
an%bui%sarec%ifs.plants@ox.ac.uk.
2 University for Tropical Agriculture-UTA, Finca Ecologica, Thu Duc
District, Ho Chi Minh City, Viet Nam, e-mail: lylian%sareclr%sarec%ifs.plants@ox.ac.uk;
and Fundaci�n Centro para la Investigaci�n en Sistemas Sostenibles de Producci�n
Agropecuaria-CIPAV, Cali, Colombia, e-mail: cipav@cali.cetcol.net.co. 3
Department of Animal Science and Production, Sokoine University of Agriculture, PO Box
3004, Morogoro, Tanzania. 4 University for Tropical Agriculture-UTA, Finca
Ecologica, Thu Duc District, Ho Chi Minh City, Viet Nam, e-mail:
thomas%preston%sarec%ifs.plants@ox.ac.uk.. 5 Institute of Political
Science, University of Aarhus, Denmark, e-mail: Frands@po.ia.dk.
Les biodigesteurs peuvent apporter une importante contribution �
l'agriculture � petite �chelle, d'une part en limitant la pollution et, d'autre part, en
valorisant les d�jections animales � travers la production de biogaz et en am�liorant
la valeur fertilisante des effluents.
Le biodigesteur tubulaire en poly�thyl�ne est int�ressant pour les populations
rurales en raison de son faible co�t d'installation et de production de gaz. Il est
utilisable aussi bien en milieu rural que dans les zones urbaines.
Divers facteurs conditionnent l'adoption de cette technologie et les r�sultats
obtenus, � savoir notamment le site (disponibilit� de combustibles traditionnels) et la
fa�on dont la technologie est introduite et modifi�e pour convenir aux conditions
locales.
Cette technologie a �t� test�e de fa�on suffisamment approfondie pour
justifier son introduction � grande �chelle dans les pays o� les conditions
socio�conomiques y �taient propices comme au Viet Nam et au Cambodge. Il convient,
toutefois, de poursuivre les travaux de recherche avec la collaboration �troite des
exploitants, afin que cette technologie puisse continuer � �voluer et � se
perfectionner.
Los biodigestores pueden contribuir de manera considerable a mejorar las explotaciones en peque�a escala, facilitando el control de la contaminaci�n y a�adiendo al mismo tiempo valor a la excreta del ganado mediante la producci�n de biog�s y la mejora del valor como nutriente del efluente utilizado como fertilizante. El biodigestor de pel�cula tubular de polietileno despierta atractivo entre la poblaci�n rural debido al bajo costo de la instalaci�n y la producci�n de gas. Se puede aplicar en zonas tanto rurales como urbanas. El �xito de la adopci�n de esta tecnolog�a y los resultados conseguidos dependen de factores como el lugar (disponibilidad de combustible tradicional) y la manera de introducir y modificar la tecnolog�a a fin de adaptarla a las condiciones locales. La tecnolog�a se ha ensayado suficientemente para justificar su introducci�n en gran escala en pa�ses cuyas condiciones socioecon�micas son favorables a su aceptaci�n, como por ejemplo Viet Nam y Camboya. No obstante, se debe proseguir la investigaci�n con la participaci�n directa de los agricultores, de manera que la tecnolog�a pueda seguir evolucionando y mejorando.
During the course of this century the global demand for power has
increased sixteenfold. Today the industrial countries, with 32 percent of the world
population, consume 82 percent of energy produced. On average, a person in an
industrialized country uses 20 times more energy than someone living in Africa.
In many developing countries there is a serious shortage of fuel and the energy crisis is
a daily reality for most families. Using renewable energy sources such as solar energy and
low-cost biodigesters is advantageous to both the farmers and the environment (Rodr�guez,
Preston and Dolberg, 1996).
Already many developing countries, such as Colombia, Ethiopia, the United Republic of
Tanzania, Viet Nam and Cambodia, have adopted the low-cost biodigester technology with the
aim of reducing production costs by using local materials and simplifying installation and
operation (Solarte, 1995; Chater, 1986; Sarwatt, Lekule and Preston, 1995; Soeurn Than,
1994; Khan, 1996). The model used was a continuous-flow flexible tube biodigester based on
the "red mud PVC" (Taiwan) bag design as described by Pound, Bordas and Preston
(1981) and later simplified by Preston and co-workers, first in Ethiopia, then in Colombia
(Botero and Preston, 1987) and later in Viet Nam (Bui Xuan An et al., 1994). Within
three years, more than 800 polyethylene digesters had been installed in Viet Nam, mainly
paid for by the farmers (Bui Xuan An and Preston, 1995).
There are many designs of biogas plants but the most common are the floating canopy (Indian) and fixed dome (Chinese) models. The poor acceptability of many of these digesters has been due mainly to high costs, the difficulty of installation and problems in procuring spare parts.
This biodigester consists of a drum, originally made of mild steel but later replaced by fibreglass reinforced plastic (FRP) to overcome the problem of corrosion. The reactor wall and bottom are usually constructed of brick, although reinforced concrete is sometimes used. The gas produced is trapped under a floating cover which rises and falls on a central guide. The pressure of the gas available depends on the weight of the gas holder per unit area and usually varies between 4 to 8 cm of water pressure. The reactor is fed semi-continuously through an inlet pipe, and displaces an equal amount of slurry through an outlet pipe (Figure 1).
This reactor consists of a gas-tight chamber constructed of bricks,
stone or poured concrete. Both the top and bottom are hemispherical and are joined
together by straight sides. The inside surface is sealed by many thin layers of mortar to
make it gas-tight. The inlet pipe is straight and ends at mid-level in the digester. There
is an inspection plug at the top of the digester to facilitate cleaning, and the gas
outlet pipe exits from the inspection cover.
The gas produced during digestion is stored under the dome and displaces some of the
digester contents into the effluent chamber, leading to gas pressures in the dome of
between 1 and 1.5 m of water. This creates quite high structural forces and is the reason
for the hemispherical top and bottom. High-quality materials and expensive human resources
are needed to build this kind of digester (Figure 1).
More than five million biodigesters have been built in China and are functioning well
(FAO, 1992) but, unfortunately, the technology has not been so popular outside China.
The high investment required to construct biodigesters of fixed
structure proved to be a major constraint for low-income small farmers. This motivated
engineers in the Province of Taiwan in the 1960s (FAO, 1992) to make biodigesters from
cheaper flexible materials. Initially nylon and neoprene were used but they proved
relatively costly. A major development in the 1970s was to combine PVC with the residue
from aluminium refineries to produce the product named "red mud PVC". This was
later replaced by less costly polyethylene which is now the most common material used in
Latin America, Asia and Africa (Figure 2).
Since 1986, the Centre for Research in Sustainable Systems of Agricultural Production
(CIPAV), a non-governmental organization in Colombia, has been recommending low-cost
plastic biodigesters as the appropriate technology for making better use of livestock
excreta, thus reducing the pressure on other natural resources.
Biogas plants may offer several advantages to low-income rural communities, including:
Tubular polyethylene is produced in most countries. The choice of supplementary fittings and related materials has been limited to those available locally on farms or in rural markets; they are the basic components of sanitary installations which are similar all over the world. The materials required (Photo 1) for both the biodigester and the stove are listed below.
An important improvement to the biodigester technology was the installation of a reservoir, made of the same tubular plastic as the digester, for storing the gas in close proximity to the kitchen (Figure 2). This has overcome the problem of low rates of gas flow when the digester is located a long way from the kitchen and when the connecting gas tube has a narrow diameter.
The biodigester plant includes a simple stove with a galvanized pipe of 12.5 mm id, two burners using the same kind of pipe and two ball taps of the same diameter (Photo 2). Measurements of gas consumption show that it takes one hour to boil 6 litres of water and that, on average, 26 litres of gas are needed to boil 1 litre of water (Rodr�guez, Preston and Dolberg, 1996). Users have developed many modifications to the basic design to combat wind effects and to suit personal needs. A lot of research has been put into improving more conventional stoves, but very little on stoves used with biodigesters (Rodr�guez, Preston and Dolberg, 1996).
The cost of the plastic biodigester is relatively low, varying according to size and location. For instance, in Colombia the cost per m3 of liquid volume is around $US30, taking into account that this includes the container and its connection, cement boxes for the inlets and outlets, plastic gas reservoir, stove, labour to prepare the trench and installation of the biodigester. In Viet Nam the average cost per m3 is only $US7 (materials only), giving a total cost for one biodigester of 5.4 m3 of US$37.80, including two burners.
The first plastic biodigester was installed in Colombia in 1986 and continued to operate until 1995 when the plastic membrane/film was changed (the plastic had lasted for nine years!). Since 1986, about 30 biodigesters per year have been installed with the help of CIPAV. The most common size is 10 m in length (9 m3 total volume). Over the last three years biodigesters of 3 and 5 m length (3 m3 to 5.5 m3 liquid volume) have also been installed with gas storage reservoirs of 3 m3 (Luis Solarte, 1996, personal communication).
Many people from different countries have visited CIPAV in Colombia to learn about the low-cost biodigesters and related technologies for sustainable agriculture. In 1992, following a visit by a study group from a SAREC-sponsored project in Viet Nam, demonstration biodigesters were installed on small farms in Song Be and Dong Nai provinces around Ho Chi Minh City (Bui Xuan An and Preston, 1995). In April 1993, a local source of polyethylene was located in Ho Chi Minh City. The cost was only US$1.25/kg, enabling the complete construction of a digester at a cost of US$25 (materials only) plus two person days for preparing the trench and installation. This was much lower than in Colombia and encouraged farmers to accept the technology (Figure 4). After about three years, more than 800 units have been installed in Viet Nam, 90 percent of which in rural areas (Bui Xuan An, Preston and Dolberg, 1996).
In mid-1993, the first low-cost plastic biodigesters were introduced into the United Republic of Tanzania as part of the FAO/TCP/URT/2255A project. So far, more than 100 biodigesters have been installed and the number is likely to increase owing to the high adoption rate by farmers. Experience has shown that the technology can be easily introduced in rural communities (Sarwatt, Lekule and Preston, 1995).
FIGURE/FIGURA 1
Fixed dome biodigester
Biodigesteur � calotte fixe
Biodigestor fijo de b�veda
PHOTO/FOTO 1
Materials for the low-cost plastic biodigester
Mat�riel pour l'installation du biodigesteur en plastique � faible co�t
Materiales para el biodigestor de pl�stico de bajo costo
Photo/Foto: Lylian Rodr�guez
FIGURE/FIGURA 2
Low-cost plastic biodigester
Biodigesteur en plastique � faible co�t
Biodigestor de pl�stico de bajo costo
FIGURE/FIGURA 3
Integrated system
Syst�me int�gr�
Sistema integrado
When choosing a suitable location for a biodigester, a site close to the
shed holding the livestock is preferable. The location of the kitchen is not usually an
issue since the gas can be transported long distances using cheap, narrow-bore PVC tubing.
Next, a trench in which to place the biodigester must be dug. The walls must be firm and
the floor flat or with only a minimum slope from entrance to exit (Figure 5). Any
protruding matter such as sharp stones or roots must be removed from the walls and floor.
On sloping land, the trench should be situated on the contour and a channel dug on the
high side to deviate rainwater.
Trials are currently in progress to evaluate a modified design in which the bottom of the
trench has a uniform slope of 1 percent from entrance to exit. The biodigester is then
filled almost completely with substrate which forces the gas to accumulate in the upper
part of the tube, close to the entrance where the gas pipe is located. In this way the
maximum volume of the digester is used for fermentation, with the gas being stored in the
reservoir.
The dimensions of the trench should be sized to accommodate the plastic tube. For example,
in Colombia this is normally 1.25 m in diameter so the trench is 1.20 m wide at the top,
80 cm at the bottom and 1 m deep; the length may vary from 3 to 10 m according to the
needs of the family and the availability of manure (Photo 3).
Two pieces of the tubular film are cut, each 1 m longer than the length of the
biodigester. They are laid on smooth ground and one is inserted into the other.
For the gas outlet, a small hole is made in the two layers of the plastic tube,
approximately 1.5 m from the entrance. One rigid PVC washer and one rubber washer are
fitted on the flange of the male adapter which is then threaded through the hole from the
inside to the outside. A second PVC washer and rubber washer are put on the male adapter
from the outside of the tube and secured tightly with the female adapter. The exit of the
female adapter is closed with a small square of plastic film and a rubber band (Figure 6).
A ceramic inlet pipe (concrete or PVC pipes can also be used but are more expensive) is
inserted up to two-thirds of its length into one end of the plastic tube. The plastic film
is folded around the pipe and secured with 5 cm rubber bands (made from the used inner
tubes). The bands are wrapped in a continuous layer to cover completely the edges of the
plastic film, finishing on the ceramic tube. The inlet tube is then closed with a square
of plastic (or a plastic bag) and a rubber band (Photo 4).
The installation procedure in Viet Nam involves filling the polyethylene tube with air
before placing it in the trench. From the open end, air is forced into the tube in waves
formed by flapping the end of the tube. The tube is then tied with a rubber band about 3 m
from the end so that the air does not escape (Photo 5). In Colombia, the most common way
to install the biodigester is by folding the plastic in an organized way and then
extending it along the floor of the trench (Figure 7).
The water tube is fitted following the same procedure as for the inlet tube.
The polyethylene tube must be placed in the trench with care. The ceramic tubes should be
set at a 45� angle and fixed temporarily with clay.
The safety valve is made from a transparent plastic bottle, a PVC "T" and three
pieces of tubular PVC (one of 30 cm and the other two of 5 cm). Water is poured into the
bottle and maintained at a depth of 5 cm above the mouth of the tube (Figure 8).
The biodigester tube is three-quarters filled with water or water and manure, moving up
and down the outlet (as indicator of the water level inside the tube). The air trapped
inside the tube escapes from the safety valve as the volume of water increases.
When fitting the gas pipe to the kitchen stove, it must not be placed underground because
moisture will condense in the lowest part and may block the gas flow. The safety valve
should be at the lowest point in the gas line.
The gas reservoir is made from a 3 to 4 m piece of the same polyethylene tube used for the
biodigester and is joined to the gas line with a PVC "T". It can be suspended
horizontally or vertically but should be shaded from the sun. To increase the pressure as
the reservoir begins to empty, a weight (a brick or stone) is suspended from the bottom
(vertical suspension) (Photo 6) or a cord is placed around the central part and tightened
(horizontal suspension) (Photo 7).
It is important to handle the polyethylene tubular film with care, as it is easily
punctured, and to cut the gas outlet neatly, taking care not to cut too large a hole in
the tube.
FIGURE/FIGURA 4
Farmers' participation in the installation of biodigesters
Participation des agriculteurs � l'installation de biodigesteurs
Participaci�n de los agricultores en la instalaci�n de biodigestores
FIGURE/FIGURA 5
Plastic biodigester
Biodigesteur en plastique
Biodigestor de pl�stico
PHOTO/FOTO 2
Cooking stoves: (left) classical burner; (right) a burner made from a beer can
Fourneaux: (� gauche) un br�leur de type traditionnel; (� droite) un br�leur
r�alis� au moyen d'une cannette m�tallique
Estufas de cocinar: (izquierda) quemador cl�sico; (derecha) uno hecho con una lata
de cerveza
Photo/Foto: Lylian Rodr�guez
PHOTO/FOTO 3
The width of the trench varies according to the size of the tube
La largeur de la tranch�e varie selon les dimensions du tube
El ancho de la zanja var�a de acuerdo con las dimensiones de la tuber�a
Photo/Foto: Lylian Rodr�guez
PHOTO/FOTO 4
Fitting the inlet pipe
Installation du conduit d'admission
Ajuste de la tuber�a de entrada
Photo/Foto: Veronika Brezki
PHOTO/FOTO 5
A plastic tube ready for installation
Tube plastique pr�t � �tre install�
Tubo de pl�stico listo para su instalaci�n
Photo/Foto: Lylian Rodr�guez
PHOTO/FOTO 6
A vertical biogas storage bag
Sac vertical de stockage du biogaz
Bolsa vertical para almacenar el biog�s
Photo/Foto: Lylian Rodr�guez
PHOTO/FOTO 7
A horizontal biogas storage bag
Sac horizontal de stockage du biogaz
Bolsa horizontal para almacenar el biog�s
Photo/Foto: Lylian Rodr�guez
An innovative feature of using tubular polyethylene is that the biodigester can be located so as to float on any water surface. It floats half submerged, with only the inlet and outlet tubes being fixed to bamboo stakes. In places where the water level rises and falls, the inlet should be fixed firmly, with its mouth located above the highest water level, while the outlet should be fixed to a floating object, such as a dried coconut or a plastic container). In Viet Nam more than 5 percent of biodigesters float in ponds, which greatly facilitates their installation since space on farms is often very limited (Photo 8).
It is possible to use any type of excreta, but gas production is higher
with pig manure and mixtures of poultry droppings and cattle manure. The amount required
depends on the length of the digester, but is generally about 5 kg of fresh manure (1 kg
solid matter) for every 1 m. To this should be added 15 litres of water so that the solids
content represents approximately 5 percent. It is not advisable to use less water since
this can lead to the formation of solid scum on the surface of the digesting material;
there is no risk in adding more. As a rule of thumb, four to five pigs (assumed live
weight of 70 kg) will provide enough manure to produce the gas required for a family of
four to five people.
Linking latrines to the plastic biodigester was pioneered in Cambodia (Soeurn Than, 1994).
It is also quite common in Viet Nam, while it is only a recent development in Colombia.
Apart from the increase in gas production, recycling human excrement through biodigesters
is an effective way of reducing disease transmission (Photo 9).
FIGURE/FIGURA 6
Fixing the gas outlet
Installation de la sortie de gaz
Ajuste de la salida del gas
FIGURE/FIGURA 7
Colombian method of installing biodigester by folding the plastic
M�thode de pliage du plastique utilis�e en Colombie pour l'installation des
biodigesteurs
Sistema colombiano de instalaci�n del biodigestor doblando el pl�stico
FIGURE/FIGURA 8
Fitting the safety valve
Installation de la valve de s�curit�
Ajuste de la v�lvula de seguridad
In Viet Nam, the cost of materials to construct a 5 m3
biodigester was US$37.00 and two person days were needed for digging the trench and
installing the digester. The time from installing the first demonstration unit to the
first unit paid for by a farmer was four months.
During the past three years, more than 800 units have been installed by extensionists and
farmers in Viet Nam. Less than 12 percent of the digesters have had technical problems,
often because of damage caused by stray animals. Most of the repairs have been carried out
by the farmers themselves.
The process of fermentation in biodigesters results in the transformation of organically bound carbon into gaseous carbon dioxide and methane. The anaerobic environment and extended retention time inhibit the growth of most pathogenic organisms and prevent the survival of intestinal parasites. Both the chemical and biological parameters of livestock excreta are therefore improved by passage through biodigesters (Table 1).
1
Differences between waste water and slurry of biodigesters
Diff�rences entre les eaux us�es et les effluents des biodigesteurs
Diferencias entre las aguas residuales y el esti�rcol l�quido de los biodigestores
Input |
Output |
|
COD (mg/litre) |
2 998 |
978 |
Escherichia coli (103/cell/ml) |
52 890 |
75 |
Coliforms (103/cell/ml) |
266 780 |
236 |
pH |
6.8 |
7.2 |
Note: COD = chemical oxygen demand (the amount of oxygen consumed for
the oxidation of the reductive substances contained in 1 litre sample of liquid waste by a
strong oxidizer). ,
Source: Bui Xuan An and Preston (1995).
Bui Xuan An, Preston and Dolberg (1996) found that biodigestion decreased chemical oxygen demand (COD) from 35 610 mg/litre in the inlet to 13 470 mg/litre in the effluent, indicating a process efficiency of 62 percent (COD removal rate). The volume of gas per caput per day, enough for cooking three meals, was about 200 litres. The loading rates were low and gas production could be improved by increasing the amount of manure fed to the digesters. However, five farmers reported that, in addition to cooking meals, they were also able to cook animal feeds; three farmers made wine; one made cakes; and two prepared tea and coffee in their cafeterias. This demonstrates that there is a high justification for adopting the technology, as discussed by Dolberg (1993) (Table 2).
2
Input and output of 31 digesters working on small farms around Ho Chi Minh City, Viet
Nam
Param�tres de production de 31 digesteurs utilis�s dans de petites exploitations
pr�s de H� Chi Minh-Ville, Viet Nam
Entrada y salida de 31 digestores que funcionan en peque�as explotaciones
alrededor de la Ciudad de Ho Chi Minh, Viet Nam
Mean |
Range |
|
Size of family5.9 |
3-12 |
|
Manure loading (kg/day) |
16 |
2-27 |
Water/manure ratio |
5.1 |
2.9-8.1 |
Loading rates (kg DM/m3) |
0.7 |
0.1-1.2 |
Temperature of loading (�C) |
26.4 |
25.7-28.5 |
Temperature of effluent (�C) |
27.0 |
26.0-29.1 |
pH of loading |
6.7 |
6.4-7.1 |
pH of effluent |
7.2 |
6.8-7.5 |
Gas production (litres/unit/day) |
1 235 |
689-2 237 |
Volume gas/caput (litres/person/day) |
223 |
68-377 |
Methane ratio (%)1 |
56 |
45-62 |
COD of loading (g/litre) |
35.6 |
22.4-46.0 |
COD of effluent (mg/litre) |
13.5 |
8.8-23.9 |
COD removal rate (%) |
62 |
42-79 |
1 From nine digesters.
Note: COD = chemical oxygen demand (the amount of oxygen consumed for the oxidation
of the reductive substances contained in 1 litre sample of liquid waste by a strong
oxidizer).
The main problems identified in a farmers' survey (Bui Xuan An, Preston and Dolberg, 1996) were:
Biodigesters can play a vital role in integrated farming systems by
contributing to the control of pollution and at the same time adding value to livestock
excreta.
The impact of the low-cost biodigester is variable. Adoption of the technique and
successful results depend on aspects such as location (availability of traditional fuel)
and the way in which the technology is introduced, adapted and improved according to local
conditions and technicians' attitudes.
The polyethylene tubular film biodigester technology is a cheap and simple way to produce
gas. It is appealing to small farmers because of its low installation cost and also
because of its environmental advantages. It can be applied in rural or urban areas.
The technology has been developed sufficiently to justify large-scale implementation in
countries where socio-economic conditions facilitate its rapid adoption, such as in Viet
Nam and Cambodia. Nevertheless, research should continue in close consultation with users
so that the technology continues to improve.
PHOTO/FOTO 8
A floating polyethylene biodigester
Biodigesteur flottant en poly�thyl�ne
Biodigestor flotante de polietileno
PHOTO/FOTO 9
A latrine linked to the biodigester
Latrines reli�es au biodigesteur
Letrina conectada al biodigestor
Photo/Foto: Lylian Rodr�guez
In view of the high potential of the technology, the following recommendations can be made:
Botero, R. & Preston, T.R. 1987. Low-cost biodigester for
production of fuel and fertilizer from manure, p. 1-20. Cali, Colombia, CIPAV.
(unpublished manuscript, in Spanish)
Bui Xuan An & Preston, T.R. 1995. Low-cost polyethylene tube biodigesters on
small-scale farms in Vietnam. Electronic Proceedings, Second Int. Conf. on Increasing
Animal Production with Local Resources, p. 11. Zhanjiang, China.
Bui Xuan An, Preston, T.R. & Dolberg, F. 1996. The introduction of low-cost
plastic polyethylene tube biodigesters on small-scale farms in Vietnam. Livestock Res.
Rur. Dev., 8(3).
Bui Xuan An, Ngo an Man, Duong Nguyen Khang, Nguyen Duc Anh & Preston, T.R.
1994. Installation and performance of low-cost polyethylene tube biodigesters on
small-scale farms in Vietnam. In T.R. Preston, Le Viet Ly, Luu Trong Hieu & B.
Ogle, eds. Proceedings of National Seminar-workshop on Sustainable Livestock Production
on Local Feed Resources. p. 81-90. Ho Chi Minh City, Viet Nam, 22-27 November 1993.
Chater, S. 1986. New biogas digester for African small holders. ILCA Newsl.,
1986(5): 4.
Dolberg, F. 1993. Transfer of sustainable technologies in Vietnam. Development of
Sustainable Livestock Technologies for Ecologically Fragile Zones in the Tropics. SIDA
M.Sc. course in sustainable livestock production systems. (report)
FAO. 1992. Biogas processes for sustainable development. FAO Agricultural
Services Bulletin No 95. Rome
Khan, S.R. 1996. Low cost biodigesters. Programme for Research on Poverty
Alleviation, Grameen Trust Report, February 1996.
Pound, B., Bordas, F. & Preston, T.R. 1981. Characteristics of production and
function of a 15 cubic metre Red-Mud PVC biogas digester. Trop. Anim. Prod., 6:
146-153
Rodr�guez, L., Preston, T.R. & Dolberg, F. 1996. Participatory rural
development: experiences in Binh Dien and Xuan Loc villages in central Vietnam. Livestock
Res. Rur. Dev., 8(2): 1-39.
Sarwatt, S.V., Lekule, F.P. & Preston, T.R. 1995. Biodigesters as means for
introducing appropriate technologies to poor farmers in Tanzania. Electronic
Proceedings, p. 6. Second Int. Conf. on Increasing Animal Production with Local Resources,
Zhanjiang, China.
Soeurn Than. 1994. Low cost biodigesters in Cambodia. In T.R. Preston, Le
Viet Ly, Luu Trong Hieu & B. Ogle, eds. Proceedings of National Seminar-workshop on
Sustainable Livestock Production on Local Feed Resources. Ho Chi Minh City, Viet Nam,
22-27 November 1993.
Solarte, A. 1995. Sustainable livestock systems based on local resources:
CIPAV's experiences. Electronic Proceedings, p. 2. Second Int. Conf. on Increasing
Animal Production with Local Resources, Zhanjiang, China.