3.4 Consumption of wood energy

National energy statistics seldom include information about traditional energy consumption with comparable level of details as those for commercial or conventional energy sources. Because of the difficulties associated with wood energy data collection and the decentralized nature of wood energy systems (Bhatia, 1985 and Ramani et al., 1995), wood energy consumption is not regularly monitored in the same way as that of conventional or commercial energy sources. But the large proportion of rural population and the significant contribution of agriculture in the economies of the countries under study (coupled with the low national income) indicate a still important role for traditional energy sources (fuelwood and charcoal, agricultural residues, and animal dung).

 

Figure 3.1

 

Figure 3.2

 

Reliable statistical data on wood energy have been obtained only from household energy consumption surveys and wood energy studies. However, most of these surveys and studies are necessarily limited in scope both in terms of the area and type of information covered. Few household energy consumption surveys are national in scope and produce comprehensive detailed information. But national household energy consumption surveys could not be conducted on a more frequent or regular basis because of the time and money involved.

Published national energy balance tables are also useful in getting an overall picture of the role of wood energy in national energy systems and in making cross-country comparisons. The latter, however, has to be done with a lot of caution because of differences in wood energy definitions and measurements among countries. For example, not all countries use the same energy unit and care should be exercised from converting from one unit to another because each country could be using different conversion factors. Some countries, moreover, may deliberately lump all biomass fuels under fuelwood because the other biomass fuels may be taking up a small portion of total energy. In addition, available data may not coincide in timing preventing more precise comparisons.

Table 3.4: Energy Indicators

 

 

Per Capita Energy
Consumption (kgoe)

Per Capita Electricity Consumption (kWh)

Population access to
electricity (%)

1975

1985

1992

1975

1985

1992

1992

Bangladesh

28

43

57

11

28

51

13

Bhutan

2

19

53

10

9

844

11

Cambodia

2

19

28

21

9

6

33

China

342

513

855

210

338

567

67

India

136

191

283

100

164

285

82

Indonesia

108

232

344

21

77

187

26

Lao PDR

29

23

40

61

35

53

13

Malaysia

555

802

1,389

365

763

1,384

84

Maldives

15

114

193

7

49

90

78

Myanmar

 

57

58

  

39

41

6

Nepal

10

18

31

6

17

35

10

Pakistan

137

208

251

95

180

284

38

Philippines

242

201

267

202

268

337

63

Sri Lanka

89

114

129

71

130

165

30

Thailand

215

315

622

180

383

853

80

Vietnam

131

90

127

51

65

100

15

Source: ADB (1994)

 

Household energy consumption surveys that are national in scope have been conducted for India (NCAER, 1979), Pakistan (UNDP, 1993), and the Philippines (UNDP, 1992).

India. According to the survey conducted in India in 1978-79, biomass fuels accounted for 97% of rural household energy use. Of this, fuelwood contributed 42%. It is estimated that after more than 15 years, with the expected increase in total energy consumption, the share of fuelwood in total biomass energy consumption may have actually increased with the likely decline in contributions from agricultural residues and animal dung (Natarajan, 1995). More recent survey (on the use of improved cookstoves, NCAER , 1993) shows that the share of biomass fuels in rural households energy consumption has declined to 94%, but that of fuelwood has increased to 47% (see Figure 3.3). The consumption of fuelwood rose to 130 million tonnes (mt) in 1992-93 from 80 mt in 1978-79. Similarly, total rural energy consumption climbed to 3,499 from 2,368 petajoules (PJ).

It was also found out that the proportion of households using firewood logs increased to about 56% from 35%, while those using firewood twigs slightly declined to 63% from 68% (Figure 3.4).

While total fuelwood consumption in rural areas increased both in relative and absolute terms, urban fuelwood consumption declined from 16.5 million tonnes in 1978-79 to 9.5 million tonnes in 1985. The decrease is explained by the shift to modern fuels, in particular LPG and kerosene, which had steady growth in sales during this period.

Pakistan. The household energy consumption survey in Pakistan (UNDP, 1993) show that households accounted for 53%, equivalent to almost 994.2 petajoules (PJ), of total final energy consumption in 1991. Seventy-nine percent (79%) of all households used fuelwood which accounted for around 53% of total household energy use (Table 3.5). All biomass fuels contributed a total of 86%. The average annual fuelwood consumption per household was estimated at 2,324.4 kilograms (kg).

Figure 3.3
Rural Household Energy Consumption in India

 

 

Note: "Others" include coal/softcoke, kerosene, and other unspecified fuels. Coal and kerosene are converted to PJ from physical units, while the other unspecified fuels which are expressed in tons of coal replacement are converted to PJ using the conversion factor for hard coal.

Source of basic data: Natarajan (1995)

 

Figure 3.4

 

Charcoal was used by only 9.2% of households in Pakistan and accounted for less than one percent of total household energy consumption.

The contribution of fuelwood in rural household energy consumption at 58% was significantly higher than in urban areas where the figure dropped to 38%. Around 30% of household energy requirements in urban Pakistan were met by natural gas. In rural areas, animal dung and agricultural residues accounted for 37% of household energy consumption.

Philippines. Based on a similar survey conducted in 1989 (UNDP, 1992), fuelwood and charcoal accounted for 68% and 11%, respectively, of total household fuel consumption in the Philippines that was just half that of Pakistan, or 497.7 PJ (Table 3.6).

The share of fuelwood in household energy consumption was higher in rural areas (82%) which accounted for 72% of total household energy consumption.

Table 3.5: Pakistan Household Energy Consumption by Fuel and by Area (in PJ)

 

Urban

%

Rural

%

Pakistan

%

Firewood

71.57

37.94

374.00

57.87

445.69

53.22

Dung

21.41

11.35

130.02

20.12

151.38

18.08

Crop Residues

11.98

6.35

105.97

16.40

117.99

14.09

Charcoal

0.71

0.38

4.27

0.66

4.99

0.60

Subtotal Biofuels

105.71

56.04

614.25

95.04

720.05

85.98

 

Natural Gas

56.90

30.16

0.00

0.00

59.33

7.08

Electricity

19.90

10.55

15.75

2.44

35.70

4.26

Kerosene

3.77

2.00

14.79

2.29

17.68

2.11

LPG

2.39

1.27

1.51

0.23

3.85

0.46

Subtotal Modern

82.96

43.98

32.05

4.96

117.40

14.02

 

Total

188.63

100.00

646.31

100.00

837.50

100.00

Note: Sum may not add up to totals due to rounding off.

Source of basic data: Ouerghi and Heaps (1993)

 

Table 3.7 also shows the proportion of households using each fuel. The data indicate that most households were using more than one type of fuel, particularly electricity, kerosene, fuelwood, and, to some extent, crop residues. Data also show that kerosene and electricity were the closest substitutes of fuelwood nationwide. In fact, in rural areas almost the same number of households was using kerosene and fuelwood. In urban areas, most households were using electricity, kerosene, and LPG.

Table 3.6: Estimated Household Fuel Consumption, 1989, Philippines

 

Electricity
(GWH)

LPG
(‘000 tons)

Kerosene
(‘000 m3)

Charcoal
(‘000 tons)

Fuelwood
(‘000 tons)

Crop Residues
(‘000 tons)

MBFOE
(%)

NCR

2,867.36

133.42

83.11

120.93

131.61

18.70

5.8%

Other Urban

2,185.21

109.78

131.87

716.33

3,126.82

414.05

21.9%

All Urban

5,052.57

243.20

214.98

837.26

3,258.43

432.75

27.7%

Rural

1,792.53

77.93

281.20

727.67

15,058.47

2,137.70

72.3%

Philippines

  

  

  

  

  

  

  

Original Units

6,845.10

321.13

496.18

1,564.93

18,316.90

2,570.45

  

MBFOE

3.943

2.322

2.707

7.512

46.891

5.963

69.338

Terajoules

23.86

14.05

16.38

45.45

283.71

36.08

419.52

MBFOE (%)

5.7

3.4

3.9

10.8

67.6

8.6

100

Source: UNDP (1992)

 

Table 3.7: Percent of Households Using Each Fuel, Philippines

 

Electricity

LPG

Kerosene

Charcoal

Fuelwood

Crop
Residues

NCR

98.5

59.4

36.7

23.4

7.5

1.8

Other Urban

83.3

32.8

68.0

42.8

54.0

26.1

All Urban

88.7

42.2

56.9

35.9

37.5

17.5

Rural

49.5

9.0

85.7

29.6

85.9

64.7

Philippines

64.7

21.9

74.5

32.1

67.1

46.4

Source: UNDP ( 1992), Annex

 

Wood energy consumption data are also scattered in energy studies conducted mostly for or by national and international agencies. The results of some of these studies are as follows:

While the above-mentioned household energy consumption surveys and studies reveal many data gaps and lack of uniformity in the available information, some patterns can be observed:

Fuelwood appears in the national energy balance tables of all countries except China and India (see Table 3.8). The information derived from national energy balance tables give broad but reasonable indications as to the significance of fuelwood in meeting national energy requirements. To summarize, Table 3.8 shows that:


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