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Comparing forestry wood species for the charcoal supply of Antananarivo city, Madagascar


Table of Contents

Boiling Point
Front cover of Boiling Point issue 40
Issue 40 (1998) Household energy and health

ArticleComparing forestry wood species for the charcoal supply of Antananarivo city, Madagascar
AuthorP. Girard, P. Rousset, A. M. Vergnet, A. Rasamindisa


[top] [end]Introduction

The city of Antananarivo city relies on charcoal from eucalyptus trees (eucalyptus robusta) for its energy supplies. However, undue pressure on these trees has caused degradation of the eucalyptus plantations, and research has been done to find other suitable sources of charcoal.

The study compared the energy output seven local species: Harungana madagascariensis,
Leucaena leucocephala,
Melia azedarach,
Tephrosia vogelii,
Acacia mangium,
Acacia dealbata,
Pinus kesiya. It also looked at the emissions, especially of greenhouse gases, which were produced in producing and using the charcoal.

[top] [end]Carbonization process

Figure 1 shows the temperatures to which the wood was subjected to produce charcoal during several tests.

The results were analysed for quantities of ash, greenhouse gases and carbon. All the output gases were collected in order to assess the quantity of greenhouse gases produced per kilogram of charcoal.
Figure 1: Temperature development within the reactor
Figure 1: Temperature development within the reactor


[top] [end]Energy output tests

The purpose of these tests was to compare how different charcoals would behave in actual households using an improved stove.

A stove was enclosed in a container from which a chimney carried the exhaust gases past a set of laboratory measuring instruments (see Figure 2). Each sample of charcoal was lit using ethanol and a fixed quantity of water was brought to the boil and boiled for 30 minutes.

For each phase - ignition, bringing to the boil, and boiling -the weight of charcoal used and the quantity of water which evaporated was measured, as well as the time needed to bring the sample to boiling point. Throughout the test, the temperatures of the fireplace, the water and the chimney were recorded continuously, and the volume of gases emitted was recorded.

Figure 2: Test rig for measuring charcoal combustion behaviour
Figure 2: Test rig for measuring charcoal combustion behaviour


[top] [end]Results

Two charcoal samples were produced from each type of wood. Four stove tests were performed for each charcoal type. Table 1 presents the average results. It can be seen that charcoal yields were between 31% and 37% and volatile gases were between 20% and 25%. The only major difference between the woods tested and eucalyptus was the low heat output rate when charcoal made from leucaena was used.

[top] [end]Conclusions

[top] [end]Greenhouse gas production

Compared to eucalyptus, the emissions resulting from charcoal-making and in cooking turned out to be very similar for 3 of the woods; the four other species produced less greenhouse gases. The quality of the charcoal did not appear to affect the quantity of greenhouse gas emissions very much, although the poorer quality charcoal yielded slightly less greenhouse gases.

[top] [end]Charcoal usability

The studied varieties of wood have been classified by density, charcoal quality produced and performance in cooking, and their overall performance graded on a 0-7 scale. This is shown in Figure 3.

Figure 3: Classification of the Malagasy species
Figure 3: Classification of the Malagasy species


[top] [end]Overall conclusions

None of the factors alone can provide the ideal choice. However, using the criteria described above, the following woods appear to be the most favourable:

Acacia mangium, Pinus kesiya, Tephrosia vogelii.

These results show that, where choice of fuel is available, an integrated approach provides a useful tool in selecting suitable woods to grow for charcoal production for household energy.

Table 1: Charcoal production and stove test results
Eucal robusta Acacia dealbata Acacia mangium Harungana madacar Leucaena leucce Melia azedar Pinus kesiya Tephrosia vogelli
Density 0.43 0.29 0.47 0.21 0.44 0.27 0.53 0.32
Yield (%) 33.1 30.8 34.6 34.3 33.6 34.1 36.8 31.8
Volatile gases 20.0 18.3 19.1 20.9 19.4 19.5 25.8 21.7
Greenhouse gases produced in making charcoal (a) 2.9 3.4 2.7 3.2 3.5 3.3 2.4 2.9
Boiling time (min) 17 15 14 12 30 15 19 16
Specific boiling time (min/l) 8.3 7.2 6.7 6.0 14.5 7.3 8.5 7.6
Specific consumption to reach boiling point g/l 43.6 43.3 39.2 44.4 48.2 46.3 47.4 39.0
Specific consumption to evaporate 1 litre of water g/l 156 153 148 152 157 152 151 134
Evaporated water whilst reaching boilingpoint (ml) 371 356 362 369 312 390 279 366
Greenhouse effect when charcoal is used for cooking (a) 2.7 3.0 2.5 3.4 2.5 2.9 2.4 2.4
Total greenhouse effect (a) 5.2 6.4 5.1 6.7 6.0 6.2 4.8 5.2

(a) kg equivalent CO2 / kg of charcoal

[top] [end]Contents: Boiling Point 40: Household energy and health

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Household energy, smoke and health - Smoke from biomass and its effects on infants - Health risk caused by domestic smoke - Emissions from high altitude stoves - a case study in Nepal - Biomass smoke and ill-health in India - preliminary results from a national survey - Global network for the health effects of environmental air pollution - Fuels, stoves and indoor air pollution in Jaracuaro, Mexico - Redesign of liquified petroleum gas stove for the blind - How many of these improvements are in your stoves programme - Participatory Technology Development in stove manufacture - a case study - Renewable energy sources in Nigeria- Efficient household energy use in Uttara Kannada District, Karnataka - Research into cooking and heating applications of down-draught stoves - Comparing forestry wood species for the charcoal supply of Antananarivo city, Madagascar

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