Acadlore takes over the publication of IJEPM from 2025 Vol. 10, No. 3. The preceding volumes were published under a CC BY 4.0 license by the previous owner, and displayed here as agreed between Acadlore and the previous owner. ✯ : This issue/volume is not published by Acadlore.
Review of Empirical Evidence on Households’ Energy Choices, Consumption, Behavioral Tendencies and Patterns Across 32 Countries
Abstract:
Many households have restricted access to various energy types and, as a result, are faced with a daily challenge of having to make appropriate energy choices to meet their energy requirements. This paper aimed to review empirical studies on the households’ energy choices and consumption patterns to establish local, regional and global trends. Our findings revealed that fuelwood, electricity, kerosene, liquified petroleum gas (LPG), charcoal, dung cakes and crop residues are the most common fuel type options available to households. Fuelwood was the most common fuel type available to the majority of the households. Our paper indicates that a significant majority of the households tend to practice energy-stacking consumption patterns. Households mostly consume fuelwood, electricity, kerosene, LPG and charcoal for cooking, lighting, water and space heating. The use of fuelwood as a major fuel by the majority of households in relation to intermediate and cleaner fuels is associated with the demo- graphic characteristics of the households, economic status of the household, the biophysical condition of the area where the household is located and the energy supply characteristics. However, the relative importance of these factors in household energy choices varies across the globe, among regions and rural, urban and mixed settings. Our results seem to suggest that the majority of households that rely on fuelwood to meet their energy needs and requirements may relatively earn less income to afford cleaner fuels, are located closer to fuelwood resources, have larger family sizes, low level of education and pos- sibly do not have adequate access to cleaner fuels. Our study indicates that there are weak correlations between the identified 12 factors, except in a few cases where there are moderate positive and negative and mostly significant linear relationships between some factors. The findings of this study have major implications for household energy use policies, plans and strategies.
1. Introduction
Varieties of energy sources are vital in maintaining people’s livelihoods and these include traditional energy sources (e.g. fuelwood, crop residues), intermediate energy sources (e.g. kerosene, charcoal) and cleaner energy sources (e.g. electricity, liquid petroleum gas) [1, 2]. Of these energy types, fuelwood, electricity, kerosene, liquefied petroleum gas (LPG), char- coal, dung cakes and biogas are the most commonly consumed fuels by households in communities globally [3–5].
However, the ultimate decision to consume any or a set of these energy resources is highly linked to the demographic characteristics and economic status of the households, the bio- physical conditions of the area where the household is located, the energy supply and other behavioral characteristics [6–8]. Despite a plethora of studies that demonstrated the strong and direct links between these driving forces and the ultimate energy choices of and con- sumption by households, there is no consensus in the literature as to which of the driving forces are most important [4, 9, 10].
The literature available on this topic cites many different factors as important, but all seem to concur that no factor single-handedly drives the choice and consumption of certain fuel types by households [10–12]. This could be attributed to differences in socio-economic development of the study countries and/or between some urban and rural areas [7, 13–15]. It is accepted that fuel type availability and accessibility could be the most important factor driving household energy choices in poorer communities of less economically developed countries, while fuel type reliability is a crucial driving force in poorer communities from much more economically developed countries [15–18].
Yet, the most common factors known to influence the household’s energy choices have been aggregated from studies undertaken in countries at various socio-economic develop- ment stages and with somewhat different biophysical conditions [3], [4], [19]. For example, Semenya and Machete [3] reviewed 70 authoritative papers and articles from 27 different countries at varying socio-economic development levels to establish the global trends on factors that influence the selection and consumption of fuelwood energy. This has been done with little emphasis on study sites with relatively similar social, economic and energy supply characteristics, despite the importance of these aspects in energy choices.
To date, reviews on local and regional trends in factors driving households’ energy choices and consumption are generally lacking in the literature. This is apart from the attempt by Akther et al. [14], who investigated the households’ energy choices and their driving forces in South Asia, Northeast Asia, Africa, and Latin and Central America. Moreover, most of the studies also come short of establishing the interrelationships between the most common fac- tors influencing household energy selection and consumption [3, 14], despite the importance of these in sustainable energy management plans [4, 20]. The interrelationships between the socio-economic factors that drive household fuel choices and consumption remain unclear.
The aim of this paper is, therefore, to review the empirical studies on the household’s energy choices and consumption behavioral tendencies and patterns to establish local, regional and global trends. By so doing, this paper seeks to document (1) the energy types consumed by the households, the various uses of these fuel types and the households’ con- sumption patterns; (2) a set of factors influencing the households’ energy choices; (3) the relative importance of the factors influencing the households’ energy choices and (4) the interrelationships between the factors that influence household’s energy choices. This was done with the view of documenting the socio-economic profile of the users of the most con- sumed fuel type or types.
2. Methods
A total of 80 empirical studies on households’ energy choices and consumption behavioral tendencies and patterns were reviewed and the retrieved information analyzed. The analysis was restricted to the 32 different countries covered by the 80 studies. The table in the Annex- ure summarizes the collected information. It lists the study countries, study countries’ economic development and electrification levels, the most common fuels available to house- holds and the most common statistically significant factors influencing household energy choice as specified in each reviewed literature source. As can be seen in the Annexure, of the studies analyzed, 55% (n = 44) were from Africa, 42% (n = 34) from Asia and the remaining 5% (n = 4) were from North and South America. These included studies undertaken at local- ized, national, regional and inter-regional scales. The economic development level of the study countries varied as follows: low income (12), lower middle income (13), upper middle income (6) and high income (01) countries. Accordingly, 50% (n = 40), 19% (n = 15) and 31% (n = 25) of the literature items utilized were undertaken in rural, urban and mixed setting areas (urban and rural – national household surveys), respectively. It is worth noting that different studies utilized in this review seem to have adopted different methodologies for categorizing the study areas as rural or urban, as none of the studies defined what separates an urban from a rural area. Studies said to have been undertaken in mixed settings are those that undertook country-wide studies, where both rural and urban households were sampled. Data sources were randomly selected through an online search, using a content analysis method where a selected range of keywords, based on their frequency of appearance in com- prehensive literature, were used as a selection criterion. Microsoft Excel 2011 software was used to analyze and determine global, regional and local scale trends on households’ energy choices and consumption behavioral tendencies and patterns. Data analyses were descriptive and presented through quantitative figures, bar charts and tables.
Fuels’ availability to households was calculated by extracting all the fuels cited as available for household consumption in the existing literature. The most common fuel type options available to households were determined by aggregating the observations of each fuel type cited in the reviewed paper. The top seven fuel types, as ranked by the total number of obser- vations, were classified as the most common fuel type options available to households. The ‘common’ and the ‘least common’ fuel type options were those ranked eighth and below. It is worth mentioning that, apart from the seven most common fuels mentioned in the Annexure, 10 more fuel types were identified in the reviewed literature and were included in the subse- quent calculations.
A set of fuel types consumed by the households was determined by identifying all the energy types consumed by the households for at least one domestic purpose, while the commonly consumed fuel types were measured by ranking the number of times that each fuel type was cited as the most consumed fuel type in the reviewed paper, for either household’s cooking, water heating, space heating or lighting purposes.
This was measured by counting the number of observations where a particular fuel type was cited as a carrier of choice for either cooking, water heating, space heating or lighting. It was then possible to determine and rank the fuel type mostly consumed by the households for each of the domestic purposes based on the sum.
The factors influencing household energy choices were aggregated by registering all the fac- tors cited as statistically significant (5% and 10% confidence level) in influencing the household energy choices and consumption in the reviewed literature. A total of 12 such factors were identified; however, only the top six ranked factors are included in the table of the Annexure. The relative importance of the factors influencing households’ energy choices was measured by ranking factors in terms of the number of times a driving factor was cited as significantly influencing a household’s energy consumption decisions across 80 reviewed studies. The top six ranked factors were identified and classified as the most important factors driving the global households’ energy choices and consumption. These top six ranked socio-economic factors are included in the table of the Annexure.
The interrelationships between factors were measured by applying multiple regression analysis and calculating the correlation coefficients on Microsoft Excel 2011. The relation- ship between two variables was considered weak when the R value was below −0.2 or 0.2, moderate when the R value was between negative or positive 0.2 and 0.4 and stronger when the R value was greater than negative or positive 0.7. If the correlation coefficient of a pair of variables equals or is closer to 0.0, it means there is no linear relationship between vari- ables. The negative and positive signs of a correlation coefficient indicate the direction of the relationship between variables. A negative correlation coefficient implies that as the value of one variable increases, the value of other variable decreases. Positive correlation coefficient implies that the values of both variables either increase or decrease together. The output of the multiple regression analysis provided the correlation coefficient (R value) and the p-value for each pair of the 12 factors known to influence the household’s energy choices (variables). The significance of the p-value was tested at 95% confidence interval. The correlation coefficient for these two variables was taken as significant when the p-value was £0.05.
The Gross Domestic Product (GDP) comparisons using the purchasing power parity (PPP) is a good indicator of countries’ economic health. This study utilized the GDP-PPP comparison to rank and classify the economic development level of the study countries. Data on the GDP- PPP of the study countries was obtained from the International Monetary Fund (IMF) website. Countries with relatively higher GDP-PPP were ranked as economically healthier than those with relatively lesser GDP–PPP. The economies of the study countries were further classified as low (L), lower middle (LM), upper middle (UM) and high (H) economies based on their respective Gross National Income (GNI) per capita. Following the methodology proposed by the World Bank, countries with US$ £10,025 billion GNI per capita were categorized as low-income economies, and those with GNI per capita of between 1026 and 3995 were clas- sified as lower middle-income economies. The nations whose GNI per capita was between 3996 and 12,375 were classified as upper middle-income economies, while those with ³12,375 GNI per capita were classified as high-income economies. Data on the rate of elec-trification across countries was downloaded from the World Bank website. The 2018 data on the countries’ electrification rate and the GDP-PPP was used to calculate the correlation coefficient on Microsoft Excel 2011. The output of the multiple regression analysis provided the correlation coefficient (R value) and the p-value of these two variables. These outputs of the multiple regression analysis were interpreted as explained in Section 2.5.
3. Results
It is pointed out that all figures and tables presented in this section are based on data retrieved from the literature sources listed in the first column of the table given in the Annexure. The same table also mentions the year of publication of as well as the area (country and setting) covered by each reviewed study.
As mentioned in Section 2, the analysis revealed that 17 different fuel types are available for selection and consumption by the households globally. The number of fuel type occurrences is presented in Fig. 1 and also listed in Table 1, where they are classified as traditional (23%), intermediate (41%) and cleaner energy sources (35%). As can be seen in Fig. 1, fuelwood is the most common fuel type option available to households globally (96%), followed by elec- tricity (71%), kerosene (69%), LPG (64%), charcoal (39%), dung cakes (30%) and crop residues (26%) across the globe.
Figure 2 shows the global number of observations of each fuel type in the reviewed literature broken down to each region, namely Africa, Asia and America. According to this figure, the majority of households in African, Asian and American regions have access to fuelwood, LPG, electricity, charcoal, kerosene, charcoal and dung cakes, among other fuels, while fuelwood remains the most common fuel type available for household consumption in these regions.
Traditional energy sources | Intermediate energy sources |
Cleaner energy sources |
A. Fuelwood | A. Kerosene | A. Electricity |
B. Dung cakes | B. Charcoal | B. LPG |
C. Non-woody plant materials | C. Coal | C. Natural gas |
D. Crop residues | D. Candle | D. Battery |
| E. Paraffin | E. Bio-gas |
| F. Diesel | F. Solar |
| G. Petrol |
|


Figure 3 shows the global number of occurrences of each fuel type in the reviewed litera- ture broken down to each type of household setting, namely urban, rural or mixed. According to this figure, fuelwood, electricity, kerosene, LPG, charcoal, dung cakes and crop residues remain the most common fuel type options available to households in rural, urban and mixed settings, while fuelwood is again the most common fuel type available for household con- sumption in either rural, urban or mixed settings.

Fuel type | Cooking | Heating (space) | Heating (water) | Lighting |
Fuelwood | Ö | Ö | Ö | Ö |
LPG | Ö | Ö | Ö | Ö |
Kerosene | Ö | Ö | Ö | Ö |
Charcoal | Ö | Ö | Ö | X |
Electricity | Ö | Ö | Ö | Ö |
Dung cakes | Ö | Ö | Ö | X |
Crop residue | X | Ö | Ö | X |
Paraffin | X | X | X | Ö |
Solar | X | Ö | Ö | Ö |
The descriptive analysis of the previous section showed that fuelwood, electricity, kerosene, LPG and charcoal are the most consumed fuels globally. Based on data retrieved from the literature sources listed in the Annexure, it was possible to produce Table 2 and Fig. 4, which indicate that these energy carriers are preferred for various domestic purposes including cooking, water heating, space heating and lighting. Figure 4, in particular, provides the fre- quency of each fuel use corresponding to each domestic energy purpose. It is seen in that figure that fuelwood is preferred by the majority of the households for cooking, water heat- ing, space heating purposes and it is an alternative source of energy for lighting, while electricity is the preferred energy carrier for lighting within the global households, followed by kerosene.
As indicated in Table 3, it was also observed that a significant majority of the households tend to practice energy-stacking consumption patterns where more than one fuel is consumed. Results plotted in Figs 5 and 6 for Africa and Asia, respectively, indicate that households in these regions mostly use fuelwood for cooking, space heating and water heat- ing, while electricity and kerosene are preferred for lighting households. This is also clearly seen in Fig. 7, where the frequency of fuel use for cooking alone has been plotted.

Household energy consumption patterns | |
Utilization method | Rating (%) |
A. Energy stacking | 87.5 |
B. Single energy | 12.5 |
The frequency of fuel use for cooking per household setting (urban, rural or mixed) is described by the bar charts of Fig. 8. These findings indicate that fuelwood is the most favored energy carrier for cooking by households in rural areas relative to households in urban areas and those in mixed settings, while reliance on fuelwood for cooking is much less in house- holds located in urban areas than those in rural and mixed settings.




The classification of the 12 identified factors is presented in Table 4 and the number of their occurrences in Fig. 9. It is seen in Table 4 that these factors are distributed across four broad categories, namely, demographic characteristics of the households, economic status of the household, the biophysical condition of the area where the household is located and the energy supply characteristics. However, the relative importance of these factors in influenc- ing household energy choices varies across the globe and among regions and rural, urban and mixed settings. The data from the reviewed studies, as plotted in Fig. 9, demonstrate that household wealth status (87%) is the most important factor driving the global household’s energy choices and consumption, followed by fuel availability and accessibility (57%), household size (52%), fuel cost/affordability (51%), education level of the household head (50%) and the household location (42%).
Economic | Fuel supply | Demographic | Biophysical condition |
A. House- hold wealth status | A. Fuel availability and accessibility | A. Household size | A. Household location |
| B. Fuel cost | B. Household head educa- tional level | B. Household dwell- ing type |
| C. Fuel type im- pact or benefit | C. Household head gender |
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| D. Household head age |
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| E. Household head marital status |
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| F. Household culture |
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Figure 10 shows again the number of observations for each factor broken down to the con- tributions from the three regions: Africa, Asia and America. Expressed in terms of percentages for each region, the results show that the household’s wealth status (84%), education level (61%), family size (54%), fuel cost (50%), fuel availability and accessibility (47%) and loca- tion (40%) are largely important in influencing the energy choices by households located in the Africa region; while within the Asian households, the households’ wealth status (85%), fuel availability and accessibility (64%), education level (50%), family size (50%), fuel cost (44%) and location (44%) are the critical driving forces.
The number of observations for each factor influencing the fuel type choice and consump- tion is plotted in Fig. 11 for each location setting: urban, rural and mixed. In terms of percentages per setting, this chart reveals that factors such as household wealth status (87%), fuel availability and accessibility (60%), family size (47%), fuel cost (45%), education level (40%) and location (37%) are the major determinants of energy choices in households located in rural areas. The roles of households’ wealth status, family size, fuel cost, culture (35%) and fuel availability and accessibility seem to be more pronounced in rural areas than in urban areas and mixed settings. The household’s wealth status (92%), educational level (76%), location (64%), gender (56%), family size (52%), age (52%) and dwelling type (44%) play a major role in households located in mixed settings.


The results of the multiple regression analysis are presented in Table 5, which provides the correlation coefficient R and the p-value (strength of the relationship) for each pair of varia- bles. These results indicate that there are generally weak correlations between the identified 12 factors, except for a few cases where there are moderate positive and negative and mostly significant linear relationships between two factors. In particular, positive, moderate and sig- nificant linear relationships between household location and wealth status, household head’s education level and household wealth status, and household head education level and household size were found. A negative, moderate and significant linear relationship was also found between fuel cost and household head gender, and household size and fuel availability and accessibility.
| Household location
| Household head education level
| Household wealth status | Household head age
| Household head gender
| Househol size
| Household head marital status
| Household dwelling type | Fuel cost | Fuel availability and accessi- bility
| Household culture
| Fuel health and bene-fits | ||||||||||||
| R | p | R | p | R | p | R | p | R | p | R | p | R | p | R | p | R | p | R | p | R | p | R | p |
A. House- hold loca- tion |
1.00 |
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B. House- hold head education level | 0.22 | 0.051 | 1.00 |
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C. House- hold wealth status | 0.31 | 0.006 | 0.31 | 0.005 | 1.00 |
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D. House- hold head age | 0.15 | 0.171 | 0.37 | 0.001 | 0.23 | 0.037 | 1.00 |
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E. House- hold head gender | 0.24 | 0.031 | 0.38 | 0.001 | 0.25 | 0.023 | 0.40 | 0.000 | 1.00 |
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F. House- hold size | 0.10 | 0.336 | 0.36 | 0.002 | 0.22 | 0.054 | 0.12 | 0.246 | 0.09 | 0.394 | 1.00 |
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G. House- hold head marital status | −0.12 | 0.299 | 0.13 | 0.251 | 0.09 | 0.417 | 0.06 | 0.620 | 0.14 | 0.205 | 0.04 | 0.733 | 1.00 |
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H. House- hold dwell- ing type | 0.40 | 0.000 | 0.30 | 0.007 | 0.23 | 0.044 | 0.25 | 0.027 | 0.13 | 0.248 | 0.21 | 0.053 | −0.16 | 0.146 | 1.00 |
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I. Fuel cost | −0.17 | 0.124 | −0.23 | 0.041 | −0.11 | 0.332 | −0.18 | 0.110 | −0.31 | 0.005 | −0.11 | 0.264 | −0.06 | 0.609 | −0.15 | 0.173 | 1.00 |
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J. Fuel availability and acces- sibility | 0.07 | 0.513 | −0.22 | 0.051 | −0.07 | 0.561 | −0.26 | 0.018 | −0.08 | 0.472 | −0.25 | 0.019 | −0.20 | 0.082 | −0.01 | 0.912 | 0.17 | 0.124 | 1.00 | |||||
K. Household culture | −0.04 | 0.703 | 0.02 | 0.864 | 0.05 | 0.651 | 0.13 | 0.263 | 0.19 | 0.093 | 0.15 | 0.152 | −0.05 | 0.660 | 0.08 | 0.455 | 0.12 | 0.280 | 0.10 0.381 1.00 | |||||
L. Fuel health and benefits | −0.14 | 0.223 | −0.18 | 0.116 | −0.20 | 0.081 | −0.10 | 0.355 | 0.06 | 0.628 | −0.17 | 0.136 | −0.04 | 0.716 | −0.10 | 0.369 | 0.00 | 0.972 | 0.14 0.223 0.08 0.507 1.00 | |||||
The results of the multiple regression analysis are presented in Fig. 12, which provides the correlation coefficient R and the p-value of the relationship between the countries’ economic development and rate of electrification. As seen in Fig. 12, multiple regression analysis revealed that there is a positive and moderate linear relationship between the country’s eco- nomic development level and the rate of electrification. The respective correlation coefficient is significant at 0.03. Countries with relatively higher GDP-PPP (>1322 trillion), including China, USA, India, Indonesia, Brazil, Mexico and Thailand, have relatively higher electrifi- cation rate, while those nations that recorded lower GDP-PPP had lower electrification level. However, there have been some instances where relatively higher ranked nations had lower electrification rate (e.g. India – 95% and Nigeria – 57%) relative to lowly ranked nations (e.g. Timor-Leste – 86% and Bhutan – 100%).
Lower-income economies also exhibited lower electrification rates. Approximately <50% of the population in poorer countries such as Burundi, Burkina Faso, Malawi, Ethiopia, Tan- zania, Lesotho, Uganda, Zimbabwe, Zambia and Malawi have access to electricity. However, other low-income economies like Tajikistan (99%), Nepal (94%) and Timor-Leste (86%) have relatively higher electrification rate when compared to fellow economies. The electrifi- cation rate for lower middle-income economies is ³57% and as high as 99%, except for Angola which has an electrification rate of 43%. The entire population (100%) of the upper middle-income economies, apart from Botswana (65%) and Namibia (54%), have access to electricity. USA was the only nation classified as high-income economy, and similar to most upper middle-income economies, has a 100% electrification rate.
This paper aimed to review the empirical studies on the households’ energy choices and con- sumption behavioral tendencies and patterns to establish regional and global trends. The main findings of this study reveal that global households in communities have access to 17 fuels. Fuelwood, a traditional fuel, was the most readily available fuel type for the majority of the households and this was well ahead of clean (electricity and LPG), intermediate (char- coal, kerosene) and other traditional dirty fuels (dung cakes and crop residues). The paper revealed that the majority of the households do practice multiple fuel stacking techniques, where dirty, intermediate and clean fuels are consumed simultaneously. It was found that fuelwood, electricity, kerosene, LPG, charcoal, dung cakes and crop residues were the fuels most utilized by the households for cooking, water heating, space heating and lighting. The present study also revealed that a vast majority of global households rely on fuelwood for cooking, water heating and space heating purposes. Results show that the use of fuelwood as a major source by the majority of households in relation to intermediate and cleaner fuels is largely associated with the household wealth status, fuel availability and accessibility, family size, fuel cost, household head’s education level, household location, household head’s age, household head’s marital status, household culture and dwelling type. However, the relative importance of these factors in influencing household energy choices varied across the globe, among regions and rural, urban and mixed settings. Yet, the fuel choices of the vast majority of households were largely driven by their wealth status. The present study indicated that there are weak correlations between the identified 12 factors except for a few cases where there are moderate positive and negative and mostly significant linear relationships between two factors. Results also showed that higher income economies have higher electrification rate, while poorer nations have lower electrification level.
4. Conclusions
The findings from this review study reveal that the largest proportions of the households have access to fuelwood, electricity, LPG, kerosene, charcoal, dung cakes and crop residues and these were the fuels most utilized by the households for cooking, water heating, space heating and lighting through multiple fuel stacking patterns. The utilization of cleaner and traditional fuels concurrently could be linked to the inability of one fuel to meet all the households’ energy needs and requirements. However, the vast majority of households rely on fuelwood for cooking, water heating and space heating purposes. The results show that the use of fuel- wood as a major source by the majority of households in relation to intermediate and cleaner fuels is associated with the 12 socio-economic factors. However, the relative importance of these factors in influencing household energy choices varied across the globe, among regions and rural, urban and mixed settings. Yet, the factors (drivers) with the largest impact in house- holds’ energy choices largely remain common across the globe, regions and local levels, except in mixed settings where household age, gender and dwelling type play a much central role. Thus, the reliance on fuelwood is largely associated with the household’s wealth status, location, size, educational level, fuel cost and fuel availability and accessibility. These factors also happen to be the poverty-defining variables, while the fuel choices of the vast majority of households were largely driven by the households’ wealth status and other socio-economic variables. Results also revealed that higher-income economies have higher electrification rate, while poorer nations have lower electrification level as measured by the percentage of populations with access to electricity.
The presented results seem to suggest that the majority of the households globally that rely on fuelwood to meet their energy needs and requirements may earn relatively less income to afford cleaner fuels, located closer to fuelwood resources, have larger family sizes, low level of education and possible do not have access to cleaner fuels amongst other characteristics. This could also be associated with the fact that fuelwood is readily available and accessible to households from nearby woodlands, affordable, efficient and does not require specialized installation and appliances, while intermediate and clean fuels are often relatively inaccessi- ble and expensive and are thus restricted to affluent households. The variation in the relative importance of the factors influencing household energy choices across the globe, among regions and rural, urban and mixed settings implies that scale-based specific sets of determi- nants should be prioritized in attempts to understand the households’ energy choices and consumption behavioral tendencies and patterns.
The findings of this study have major implications for household energy use policies including future energy plans and strategies. Households that have access to other fuels and yet still primarily rely on fuelwood could be encouraged, through awareness raising pro- grams, to adopt cleaner fuels to lessen their high dependence on fuelwood. Where a complete switch from fuelwood to cleaner fuels is not economically feasible, major efforts should be geared toward improving the fuelwood use efficiency in kitchens and increasing the supply of fuelwood resources to reduce the overexploitation of fuelwood resources. Reducing or subsidizing the prices of alternative fuels as part of a broader poverty reduction program would also empower economically marginalized households to afford fuelwood substitutes. The use of fuelwood substitutes could also be enhanced by investing in vigorous programs aimed at increasing the supply and access to cleaner fuels.
The data used to support the findings of this study are available from the corresponding author upon request.
The authors declare that they have no conflicts of interest.
Authors | Study area | Most common fuels available to households | Statistically significant factors influencing the choice | |||||||||||
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| Fuel- LPG wood | Elec- tricity | Ker- osene | Char- coal | Dung cakes | Crop residues | Loca- tion | Edu- cation | Wealth status | Size | Fuel cost | Fuel avail- ability and access | |
1. Akther et al. 2010 | Bangladesh Urban and rural | 1 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | |
2. Lhendup et al. 2010 | Bhutan Urban | 1 1 | 1 | 1 |
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| 1 | 1 | |
3. Jaiswal and Bhattacharya 2013 | India Rural | 1 1 |
| 1 |
| 1 | 1 | 1 |
| 1 | 1 |
| 1 | |
4. Malik et al. 2014 | India Rural | 1 1 |
| 1 |
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| 1 |
| 1 | 1 | 1 | 1 | |
5. Pan et al. 2012 | China Rural | 1 1 | 1 |
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| 1 | 1 | 1 |
| 1 |
| 1 | 1 | |
6. Ramachandra et al. 2000 | India Rural | 1 1 | 1 | 1 |
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| 1 | 1 |
| 1 | 1 |
| 1 | |
7. Mukul et al. 2014 | Bangladesh Rural | 1 |
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| 1 | 1 |
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| 1 |
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| 1 | |
8. Kuunibe et al. 2013 | Ghana Urban | 1 1 | 1 |
| 1 |
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| 1 | 1 | 1 | 1 |
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9. Abdul-Hanan et al. 2014 | Ghana Urban and rural | 1 | 1 |
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| 1 |
| 1 |
| 1 | 1 | |
10. Nnaji et al. 2012 | Nigeria Rural | 1 |
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| 1 | 1 | 1 |
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11. Rao and Reddy 2005 | India Urban and rural | 1 1 | 1 | 1 |
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| 1 | 1 | 1 | 1 |
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12. Punyu and Jamir 2018 | India Urban | 1 1 | 1 | 1 | 1 |
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| 1 | 1 |
| 1 | |
13. Bisu et al. 2016 | Nigeria Urban | 1 1 | 1 | 1 | 1 |
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| 1 | 1 | 1 | 1 | 1 | 1 | |
14. Dash et al. 2018 | India | Rural | 1 |
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| 1 |
| 1 |
| 1 | 1 | 1 | 1 | |
15. Nath et al. 2013 | Bangladesh | Rural | 1 |
| 1 | 1 |
| 1 | 1 |
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| 1 |
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16. Ateba et al. 2018 | South Africa | Urban and rural | 1 | 1 | 1 |
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| 1 | 1 | 1 | |
17. Ebe 2014 | Nigeria | Urban | 1 | 1 |
| 1 |
|
|
|
| 1 | 1 | 1 | |
18. Al-Subaiee 2016 | Saudi Arabia | Rural | 1 | 1 | 1 | 1 | 1 |
| 1 | 1 | 1 | 1 |
| |
19. Yuni et al. 2017 | Nigeria | Urban and rural | 1 |
| 1 | 1 |
|
|
| 1 | 1 | 1 | 1 | |
20. Buba et al. 2017 | Nigeria | Urban and rural | 1 | 1 |
| 1 | 1 |
|
| 1 | 1 | 1 | 1 | |
21. Imran et al. 2019 | Pakistan | Rural | 1 |
|
|
|
|
|
| 1 |
| 1 |
| |
22.Baiyegunhi and Hassan 2014 | Nigeria | Rural | 1 |
| 1 | 1 |
|
|
|
| 1 | 1 | 1 | |
23. Gioda 2019 | Brazil | Urban and rural | 1 | 1 | 1 | 1 | 1 |
|
|
|
| 1 |
| |
24. Wu et al. 2017 | China | Rural | 1 | 1 | 1 |
|
|
| 1 |
| 1 | 1 |
| |
25. Ranganath et al. 2016 | China | Rural |
| 1 | 1 | 1 |
|
|
|
|
|
|
| |
26. Rahut et al. 2016 | Ethiopia Malawi Tanzania | Urban and rural | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 |
| |
27. Assa et al. 2015 | Malawi | Urban and rural | 1 |
| 1 | 1 | 1 |
| 1 | 1 | 1 | 1 |
| |
28. Shrestha et al. 2008 | Thailand | Urban | 1 | 1 | 1 |
| 1 |
|
|
|
|
|
| |
29. Ali and Victor 2012 | Nigeria | Urban | 1 | 1 |
| 1 | 1 |
|
|
| 1 | 1 | 1 | |
30. Ping et al. 2017 | China | Rural | 1 | 1 | 1 |
|
|
|
|
| 1 | 1 | 1 | |
31. Maurice et al. 2015 | Nigeria | Rural | 1 |
|
| 1 |
|
|
|
|
| 1 |
| |
32. Rahut et al. 2017 | Ethiopia Malawi Tanzania Uganda | Urban and rural |
|
| 1 |
|
|
|
|
| 1 | 1 |
| |
33. Karakara 2018 | Ghana | Urban and rural | 1 | 1 | 1 | 1 | 1 |
|
| 1 | 1 | 1 | 1 | |
34. Rawat et al. 2009 | India | Rural | 1 | 1 | 1 | 1 |
| 1 |
|
|
|
|
| |
35. Song et al. 2012 | USA | Urban and rural | 1 |
|
|
|
|
|
| 1 |
| 1 | 1 | |
36. Israel- Akinbo et al. 2018 | South Africa | Urban and rural | 1 | 1 | 1 |
|
| 1 |
| 1 |
| 1 | 1 | |
37. Mislimshoe- va et al. 2019 | Tajikistan | Rural | 1 |
| 1 |
|
| 1 |
| 1 | 1 | 1 |
| |
38. Emagbetere et al. 2016 | Nigeria | Urban and rural | 1 | 1 | 1 | 1 | 1 |
|
|
| 1 | 1 |
| |
39. Roubik et al. 2018 | Indonesia | Rural | 1 | 1 | 1 |
|
|
|
|
|
| 1 |
| |
40. Nnaji et al. 2012 | Nigeria | Rural | 1 |
|
| 1 | 1 |
|
|
| 1 | 1 | 1 | |
41. Ahamed et al. 2013 | Bangladesh | Rural | 1 | 1 | 1 | 1 |
| 1 | 1 |
|
| 1 | 1 | |
42. Ouedraogo 2006 | Burkina Faso | Urban | 1 | 1 | 1 | 1 | 1 | 1 |
|
| 1 | 1 | 1 | |
43. Joshi and Bohara 2017 | Nepal | Urban and rural | 1 | 1 |
| 1 |
| 1 | 1 |
| 1 | 1 | 1 | |
44. Kwakwa et al. 2013 | Ghana | Urban and rural | 1 | 1 | 1 | 1 | 1 |
|
| 1 | 1 | 1 | 1 | |
45. Abebaw 2007 | Ethiopia | Urban | 1 |
| 1 | 1 | 1 | 1 | 1 |
| 1 | 1 | 1 | |
46. Malakasuka 2016 | Tanzania | Rural |
|
| 1 |
|
|
|
|
|
|
|
| |
47. Akpalu et al. 2011 | Ghana | Urban and rural | 1 | 1 |
| 1 | 1 |
|
| 1 |
| 1 |
| |
48. Foysal et al. 2012 | Bangladesh | Rural | 1 | 1 | 1 | 1 |
| 1 | 1 | 1 | 1 | 1 | 1 | |
49. Makonese et al. 2018 | Angola Lesotho Malawi Namibia Swaziland Zambia Zimbabwe | Urban and rural | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | |
50. Rahut et al. 2017 | Timor-Leste | Urban and rural | 1 |
| 1 | 1 |
|
|
| 1 | 1 | 1 | 1 | |
51. Link et al. 2012 | Nepal | Rural | 1 |
| 1 |
|
|
|
| 1 | 1 | 1 | 1 | |
52. Moeen et al. 2016 | Pakistan | Rural | 1 | 1 | 1 | 1 |
| 1 | 1 |
| 1 | 1 |
| |
53. Oteh et al. 2015 | Nigeria | Urban | 1 | 1 | 1 | 1 | 1 |
|
|
| 1 | 1 |
| |
54. Dorji and Singye 2017 | Bhutan | Urban and rural | 1 | 1 | 1 | 1 |
| 1 |
| 1 | 1 | 1 |
| |
55. Nyankone and Waithera 2016 | Kenya | Rural | 1 | 1 | 1 | 1 | 1 |
|
|
|
| 1 |
| |
56. Bhattarai 2013 | Nepal | Rural | 1 |
|
|
|
|
| 1 |
|
| 1 | 1 | |
57. Behera et al. 2015 | India Bangladesh Nepal | Urban and rural | 1 | 1 | 1 | 1 |
| 1 |
|
| 1 | 1 |
| |
58. Uhunamure et al. 2017 | South Africa | Rural | 1 |
| 1 |
|
|
|
| 1 | 1 | 1 | 1 | |
59. Asik and Masakazu 2017 | Bangladesh | Rural | 1 | 1 | 1 |
| 1 | 1 | 1 |
|
| 1 | 1 | |
60. Onoja and Idoko 2012 | Nigeria | Rural | 1 |
|
| 1 |
|
|
|
|
| 1 | 1 | |
61. Onyeneke et al. 2015 | Nigeria | Rural | 1 |
|
|
|
|
|
|
| 1 | 1 | 1 | |
62. Berhe et al. 2017 | Ethiopia | Rural | 1 |
|
|
| 1 | 1 |
| 1 |
| 1 |
| |
63. Deshmukh et al. 2014 | India | Rural | 1 | 1 |
| 1 |
| 1 | 1 |
| 1 | 1 | 1 | |
64. Rahut et al. 2014 | Bhutan | Urban and rural | 1 | 1 | 1 | 1 |
| 1 | 1 | 1 | 1 | 1 |
| |
65. Abd’razack et al. 2012 | Nigeria | Urban | 1 | 1 | 1 | 1 |
|
|
|
|
|
|
| |
66. Andadari et al. 2014 | Indonesia | Urban and rural | 1 | 1 | 1 | 1 | 1 |
|
|
| 1 | 1 | 1 | |
67. Prasad and Komala 2015 | India | Rural | 1 | 1 |
| 1 |
|
|
|
|
| 1 |
| |
68. Niyongabo and Makonese 2017 | Burundi | Urban | 1 |
|
| 1 | 1 |
|
|
|
| 1 |
| |
69. Ebe 2014 | Nigeria | Urban | 1 | 1 | 1 | 1 |
|
|
|
|
| 1 | 1 | |
70. Masera et al. 2000 | Mexico | Rural | 1 | 1 | 1 | 1 | 1 |
| 1 |
|
| 1 |
| |
71. Louw et al. 2008 | South Africa | Rural | 1 |
| 1 |
|
|
|
|
|
| 1 |
| |
72. Bravo et al. 2008 | Argentina | Urban | 1 | 1 | 1 | 1 | 1 |
|
|
|
| 1 |
| |
73. Masekoameng et al. 2005 | South Africa | Rural | 1 |
| 1 | 1 |
|
|
|
|
|
|
| |
74. Adepoju et al. 2012 | Nigeria | Rural | 1 |
|
|
| 1 |
| 1 | 1 | 1 | |||
75. Semenya and Machete 2019 | South Africa | Rural | 1 |
| 1 |
|
| 1 | 1 | 1 | 1 | 1 | ||
76. Nlom and Karimov 2015 | Cameroon | Urban and rural | 1 | 1 | 1 | 1 | 1 |
| 1 | 1 | 1 |
| ||
77. Megbowon et al. 2018 | Nigeria | Urban and rural | 1 |
|
| 1 |
|
|
| 1 |
| 1 | ||
78. Ado and Babayo 2016 | Nigeria | Urban | 1 | 1 | 1 | 1 | 1 |
| 1 | 1 | 1 | 1 | ||
79. Massawe et al. 2015 | Tanzania | Rural | 1 | 1 | 1 | 1 | 1 |
| 1 |
| 1 |
| ||
80. Kabir et al. 2018 | Nigeria | Rural | 1 | 1 | 1 | 1 |
|
|
|
|
| 1 | ||
