# Blog

## Web Development Modelling of supply and demand-side determinants of liquefied petroleum gas consumption in peri-urban Cameroon, Ghana and Kenya – Nature.com

Thank you for visiting nature.com. You are using a browser version with limited support for CSS. To obtain the best experience, we recommend you use a more up to date browser (or turn off compatibility mode in Internet Explorer). In the meantime, to ensure continued support, we are displaying the site without styles and JavaScript.
Nature Energy volume 6pages 1198–1210 (2021)
1613 Accesses
1 Citations
50 Altmetric
Metrics details
Household transitions to cleaner cooking fuels (for example, liquefied petroleum gas (LPG)) have historically been studied from a demand perspective, with clean energy usage expected to increase with improvements in household socio-economic status. Although recent studies demonstrate the importance of supply-side determinants in increasing clean cooking, few large-scale studies have assessed their importance quantitatively, relative to demand-related factors. Here, as part of the CLEAN-Air(Africa) study, we examine a population-based survey (n = 5,638) of cooking practices in peri-urban communities within Cameroon, Kenya and Ghana. Multilevel logistic and log-linear regression assessed the demand and supply-side determinants of LPG usage (primary versus secondary fuel) and consumption (kilograms per capita per year), respectively. Supply-side factors (for example, cylinder refill and transportation costs) and the use of single versus multiburner stoves were better predictors than household socio-economic status for both the probability of primarily cooking with LPG and the annual LPG consumption. These results highlight the need for policies that promote LPG supply and stove equipment to meet household needs.
Polluting fuels, which include biomass (for example, wood and charcoal), coal and kerosene, are used by approximately 3.8 billion individuals worldwide for cooking, heating and lighting1. Household air pollution generated from incomplete combustion of these fuels results in levels of 2.5 μm fine particulate matter (PM2.5) typically well above World Health Organization (WHO) guidelines2. Exposure to PM2.5 in household air pollution is causally associated with many adverse health outcomes, which include cardiopulmonary and respiratory diseases3,4,5,6. Although fuels such as coal and charcoal generally emit lower levels of PM2.5 than other polluting fuels7, their combustion also generates high levels of carbon monoxide, which has been linked to increased blood pressure8 and adverse pregnancy outcomes9. Additionally, household air pollution contains short-term climate-forcing pollutants, which include black carbon, which is also associated with negative health impacts10. It is estimated that 25% of global anthropogenic black-carbon emissions are produced from household biomass combustion11,12. The use of polluting cooking fuel further leads to deforestation in certain locations, particularly in East Africa11. Women, typically the primary cook, may travel long distances to gather polluting fuels in some settings, which negatively impacts their livelihoods13,14.
In Sub-Saharan Africa (SSA), approximately 900 million people cook with polluting fuels15. Governments in SSA, which include Cameroon, Ghana and Kenya, plan to expand the population-level use of liquefied petroleum gas (LPG) as a clean cooking solution to an aspirational target of 35–58% over the next decade16,17,18. LPG, although a fossil fuel, does not emit black carbon and has much lower PM2.5 emissions than polluting fuels7,16,19. Using LPG for cooking can also decrease localized deforestation and reduce the time spent gathering and cooking with polluting fuels7,20.
Historically, studies focused on the determinants of clean cooking fuel use have emphasized the ‘household energy ladder’ model, by which improvements in socio-economic status (SES) lead households to transition to modern energy sources21,22,23. In reality, higher income usually does not lead to a complete transition to clean cooking fuels in low- and middle-income countries, as households will probably continue using polluting fuels alongside clean fuels (fuel ‘stacking’) to meet all cooking needs24. For example, studies in India found that resource-poor rural households provided with LPG cooking equipment under the Pradhan Mantri Ujjwala Yojana (PMUY) programme continued to use polluting fuels, which led to less frequent LPG use compared with that of more affluent urban households25,26. There are numerous potential causes of fuel stacking, which include taste preferences, high or unstable fuel costs, convenience and cultural norms27,28,29. In SSA, studies carried out in Cameroon30,31, Tanzania32 and Ethiopia33 also found supply-related issues to be important determinants of fuel stacking. Multinational modelling studies conducted in SSA found that community-level effects explained a higher amount of variability in cooking fuel choice than household SES characteristics, which suggests that cooking decisions may be largely driven by fuel availability and other supply-related factors that occur at a broader level34,35. Although these studies assessed the impact of specific supply and demand-side factors on primary cooking fuel type used, few large-scale studies quantitatively assessed determinants of a higher LPG consumption in SSA. To understand the important drivers of increased LPG consumption, rather than a binary indictor of whether LPG is used, may help uncover strategies that reduce fuel stacking and facilitate a full transition to LPG.
In this study, survey data on cooking behaviours, which include the primary and secondary cooking fuels used and the average annual per capita LPG consumption, were collected in three peri-urban communities in Cameroon, Kenya and Ghana. These countries were specifically chosen as all are implementing policies to scale-up the adoption of LPG for cooking to decrease the negative impacts of polluting cooking fuels on health and the environment (Methods). Multilevel modelling of over 5,500 households from the three countries was conducted in a quantitative assessment of the supply and demand-related impacts on LPG fuel usage in the rapidly urbanising communities of SSA. The modelling results show a significant, positive relationship between increased per capita LPG consumption and lower LPG refill cost, shorter travel time to access the fuel and a higher number of LPG stove burners. Households that indicated a consistent availability of LPG refills at retailers had a significantly higher probability of using LPG as a primary cooking fuel (defined as the fuel used most often (Methods)) than those that reported an inconsistent supply, irrespective of education level and income. This empirical evidence suggests that to enhance LPG accessibility and availability, which includes via expansion of the number of retail points and promotion of multiburner LPG stoves, can be effective short-term interventions to increase the LPG consumption among peri-urban households in SSA.
This study presents findings from the Global Health Research Group on clean energy access for the prevention of non-communicable disease in Africa through clean air (CLEAN-Air(Africa)) programme36, which involves a randomly administered cross-sectional survey via door-to-door sampling. Surveys were completed by the main cook of the household and included questions on cooking fuel use from a WHO harmonized survey for monitoring Sustainable Development Goal 7 indicators37. The full questionnaire is available in the Supplementary Information. The final analytical sample included 5,638 households (Obuasi, Ghana, 1,987 (35%); Mbalmayo, Cameroon, 1,811 (32%) and Eldoret, Kenya, 1,840 (33%)).
The proportion of individuals who primarily cooked with LPG varied substantially by community (Obuasi 38% (n = 757), Mbalmayo 28% (n = 468) and Eldoret 5% (n = 35)) (Fig. 1). Of the households, 60% (n = 2,772) ‘stacked’ at least two cooking fuels. Fuel stacking was 30% higher among households that primarily used LPG (82%) compared with households that primarily used polluting fuels (53%). Fuel-stacking prevalence among households that primarily cooked with polluting fuels was approximately 20% higher in Eldoret (~60%) and Mbalmayo (~60%) compared with Obuasi (~40%) (Supplementary Table 2).
Cooking fuel percentages (n = 4,555) are presented among 757 households in Eldoret, rather than the full sample of 1,840 households because random sampling was switched to purposive sampling midway through the data collection. This was done to ensure a higher sample of LPG households available for subsequent phases of the CLEAN-Air(Africa) study in Eldoret.
A higher percentage of households that primarily cooked with LPG contained a member with a university degree (22%) and were in the highest income quartile (23%), compared with households that primarily used polluting cooking fuels (5% with a university degree and 8% in the highest income quartile) (Supplementary Table 2). In Eldoret and Mbalmayo, the proportion of households cooking primarily with polluting fuels and reported seasonal changes in income (72 and 75%, respectively) was 20–30% higher than those that primarily cooked with LPG (42 and 58%, respectively). Among households that primarily cooked with LPG, 59% had fewer than five family members, compared with 38% of those that primarily cooked with polluting fuels (Supplementary Table 2).
Over half (55%, n = 1,567) of the 2,830 households cooking with LPG used it as a primary fuel; very few (4%, n = 109) exclusively cooked with LPG and 44% (n = 1,263) used LPG as a secondary fuel (Table 1). In Obuasi, two-thirds of households reported using LPG as a primary fuel (67%, n = 679) compared with one-third (37%, n = 316) of households in Eldoret; in Mbalmayo, LPG was used roughly equally as a primary and secondary fuel (48%, n = 463). LPG was most frequently stacked with wood in Mbalmayo, and with charcoal in Eldoret and Obuasi (Fig. 2).
For brevity, only the most common fuel combinations (>35 households) were included. Among the study households, there were nearly 200 different cooking fuel combinations.
Nearly half (47%) of households that primarily cooked with LPG said it was not always available for purchase (Table 1), more than double that for those exclusively cooking with LPG (21%)). LPG consumption varied substantially from 0.8 to 67.0 kg capita–1 yr–1. Median LPG consumption was 14.4 kg capita–1 yr–1 (interquartile range (IQR) 10.4, 24.0) in Eldoret, 20.0 kg capita–1 yr–1 (IQR 15.0, 30.0) in Mbalmayo and 23.2 kg capita–1 yr–1 (IQR 14.5, 36.0) in Obuasi. The mean cost of cylinder refills was lowest among households exclusively cooking with LPG (US$0.99 kg–1 (s.d. 0.50)) and highest among households using LPG as a secondary fuel (US$1.27 kg–1 (s.d. 0.67)).
In Eldoret, 72% of the participants cooking exclusively with LPG were ten minutes or less from a retailer compared with 47 and 36% of households using LPG as a primary or secondary fuel, respectively. Electing to walk to an LPG retailer to obtain cylinder refills was six times more common among participants in Eldoret using LPG exclusively (61%) than among those using LPG as a secondary fuel (11%).
The final multivariable model modestly characterized (pseudo (R_{{rm{marginal}}}^2) = 0.42, receiver operating characteristic = 0.82) primary versus secondary use of LPG for cooking (Supplementary Table 4). Demographics ((R_{{rm{marginal}}}^2) = 0.11) and LPG supply-related factors ((R_{{rm{marginal}}}^2) = 0.10) explained a higher proportion of model variability than SES ((R_{{rm{marginal}}}^2) = 0.03) (Supplementary Table 4). Households with 1–2 members had more than twice the predicted probability (84% (95% CI, 68, 93)) of primarily using LPG than households with 7–8 family members (35% (95% CI, 17, 58)) (Table 2). Lower availability of LPG and higher refill costs were associated with a lower predicted probability of primary use of the fuel in a monotonically decreasing manner (Fig. 3). Specifically, 69% (95% CI, 47, 85) of households that report a refill cost of <US$0.86 kg–1 were predicted to use LPG as a primary fuel, compared with 60% (95% CI, 40, 80), 52% (95% CI, 30, 73) and 40% (95% CI, 20, 64) of households that reported a cylinder refill cost of US$0.86–1.00 kg–1, US$1.01–1.10 kg–1 and >US$1.10 kg–1, respectively. As the number of family members living in the household increased, a higher number of LPG stove burners was associated with a greater proportion of households that reported the use of LPG as a primary fuel; nearly 60% of households with a large family size (≥7 members) using LPG as a primary cooking fuel owned a 3–4 burner stove, compared with less than 30% of smaller households (1–2 members) that primarily cooked with LPG (Supplementary Fig. 1).
Mean predicted probability of using LPG as a primary fuel along with error bars that represent 95% confidence intervals (CIs). Primary LPG households were those that indicated LPG as their main cooking fuel, whereas secondary LPG users were those that stated LPG was another fuel they used aside from their main cooking fuel. All probabilities account for quantitative covariates centred at their mean.
Half ((R_{{rm{marginal}}}^2) = 0.49; cross-validation R2 = 0.39) of the variability in LPG consumption was explained by covariates included in the final model (root mean square error = 0.52 kg capita–1 yr–1; cross-validation root mean square error = 0.54 kg capita–1 yr–1) (Supplementary Table 5). Household demographics ((R_{{rm{marginal}}}^2) = 0.31) explained substantially more of this variability than household SES ((R_{{rm{marginal}}}^2) = 0.0). Households with 3–4 members consumed an average of 13.7 kg capita–1 yr–1 (95% CI, –17.2, –9.4), less than households with 1–2 individuals (Table 3).
Households that used a double-burner or triple-burner LPG stove consumed an average of 8.1 (95% CI, 3.6, 13.8) or 6.7 (95% CI, 2.4, 11.7) kg capita–1 yr–1, respectively, more LPG than households with single-burner stoves, irrespective of SES and family size (Table 3). Households that exclusively cooked with LPG consumed 2.5 kg capita–1 yr–1 (95% CI, 0.4, 4.3) more than households that stacked LPG with another fuel (Table 3).
Participants that required 11–20 minutes, 21–30 minutes or >30 minutes to travel to LPG retailers consumed an average of 0.9 (95% CI, –3.9, 2.9), 1.2 (95% CI, –4.2, 2.7) and 1.3 (95% CI, –4.2, 2.4) kg capita–1 yr–1 less than those who could reach an LPG retailer in 10 minutes or less (Table 3). In addition, households that reported a lowest cost of LPG cylinder refills (<US$0.86 kg–1) consumed 3.2 (95% CI, –6.4, 0.8), 3.9 (95% CI, –7.2, 0.1) and 6.0 (95% CI, –9.0, –2.2) kg capita–1 yr–1 more than participants who reported higher refill costs of US$0.86–1.00 kg–1, US$1.01–1.10 kg–1 and >US$1.10 kg–1, respectively. A similar monotonically decreasing relationship was found between a higher transportation cost to reach the LPG retailer and an average per capita LPG consumption (Fig. 4).
Mean LPG consumption along with error bars that represent 95% CIs. Annual per capita consumption was obtained by dividing 12 months by the self-reported average duration (months) until a typical cylinder refill runs empty, multiplying that quantity by the LPG cylinder size and dividing by the number of household members. Per capita consumption is presented with covariates centred at their mean.
Among households that exclusively cook with polluting fuels (n = 2,685), nearly half (47%, n = 1,248) reported they had previously cooked with LPG (Supplementary Table 6); the proportion varied nearly threefold by community (Obuasi 63% (n = 612), Mbalmayo 48% (n = 399) and Eldoret 24% (n = 237)). Only 10% (n = 272) of households that cooked exclusively with polluting fuels indicated being satisfied with their current cooking fuel.
Inability to afford the upfront costs of purchasing LPG stoves and/or equipment was the dominant reason (70%, n = 1,889) reported for not currently cooking with LPG (Fig. 5). High refill costs were cited as a barrier for LPG use by twice as many households that previously cooked with LPG (37%) as those that had not (19%) (Supplementary Table 6). LPG safety concerns were reported by 18% (n = 470) of households not currently using LPG; this concern was highest in Obuasi (30%, n = 292); the proportion was twice as high as that in Mbalmayo (14%, n = 117) and five times higher than that in Eldoret (6%, n = 61).
n = 2,685.
By quantitatively modelling the impact of demand and supply-side indicators on LPG usage, this multinational study demonstrates that both types of factors influence rates of LPG consumption in peri-urban communities in SSA. Although the prevalence of exclusive LPG users in the study sample was minimal (4%), a 20% higher prevalence of a consistent availability of LPG reported among exclusive LPG users in Obuasi and Eldoret compared with that for households that stacked LPG with a polluting fuel (Supplementary Table 3) indicates that an unreliable supply of LPG is a critical deterrent to a full transition to clean cooking. Additionally, cooking with LPG exclusively rather than stacking with a polluting fuel was associated with a significantly (20%) higher annual LPG consumption (average increase from 13.3 to 15.8 kg capita–1 yr–1) (Table 3). This importantly indicates that a higher per capita consumption among our study sample was not only due to households that cooked more on both LPG and traditional stoves (for example, due to a larger family size), but also that stacked fuels at a lower rate.
Households indicating that LPG was always available at retailers had a 25% higher predicted probability of using LPG as a primary fuel than those that reported that it was unavailable for purchase at least once per month, irrespective of household SES (Table 2). Households reporting the lowest LPG cylinder refill costs also had a 30% higher probability of primarily using LPG (Table 2) and consumed 6.0 kg capita–1 yr–1 (95% CI, 2.2, 9.0) more than households that reported the highest refill costs (Table 3). Unaffordable LPG cylinder refill costs were commonly reported by households that cooked exclusively with polluting fuels, particularly in Obuasi (50%) and Mbalmayo (40%). This is possibly indicative of customers who use smaller cylinders (6 kg) in Eldoret being less sensitive to changes in the refill price compared with those using >12 kg cylinders in Cameroon and Ghana. As an increasing LPG cylinder refill cost (per kilogram) was negatively associated with consumption in a monotonically decreasing manner (Fig. 4), and 37% of previous LPG users cited LPG cylinder refill costs as their main reason for the discontinued use of the fuel (Fig. 5), the cost of LPG cylinder refills emerged as a critical barrier among both current and former LPG users.
Moreover, using a double-burner LPG stove was associated with a 8.1 kg capita–1 yr–1 (95% CI, 3.6, 13.8) higher LPG consumption compared with use of a single-burner stove (Table 3). Further, using a multiburner LPG stove was linked to a greater probability of households that primarily used LPG, particularly those with five members or more (Supplementary Fig. 2). These findings probably reflect the greater time and fuel savings multiburner stoves offer to larger families due to the ability to use multiple pots or pans simultaneously38. The ability to cook two meals simultaneously on double-burner stoves was an advantage of LPG over kerosene reported by households in Nairobi39, and participants in another Kenyan study stated they had ‘no need to stack’ when using double-burner stoves40. This study adds to the growing body of evidence that, once the barrier of initial LPG access is overcome, families value the practicalities of cooking (for example. time and fuel savings), which can be influenced by supply-related factors aside from fuel price alone. Governments should promote multiburner stoves (as in India with the PMUY programme)26 as a potentially highly effective intervention to scale-up the more exclusive use of clean cooking.
Higher transportation cost and longer time to obtain an LPG refill were associated with lower LPG consumption in a monotonically decreasing manner (Table 3). This finding matches that of previous cooking fuel choice research conducted in rural communities in Ghana41,42,43. Policies that improve the proliferation of last-mile LPG distributors and retailers are probably needed in these peri-urban communities to decrease the travel time and costs associated with acquiring cylinder refills. Other LPG supply-chain enhancements, such as increased cylinder inventory, bulk storage and filling facilities, may ultimately lead to a greater population-level consumption of LPG29. These supply-related policies were identified as a priority by the governments of all three countries17,44,45.
Additionally, consumer finance mechanisms, which includes unconditional cash transfers46, microfinance47 and pay-as-you-go LPG were shown to increase or sustain the use of LPG. Pay-as-you-go LPG, which removes transportation times and costs via the direct home delivery of LPG cylinders, has been successfully rolled out in urban settings, but will be more logistically challenging to implement in peri-urban areas due to the higher transportation costs and enhanced distribution networks needed to ensure timely home deliveries17.
In India, the PMUY programme rapidly expanded LPG access among the poorest, but did not lead to a higher usage among rural households25,48. A study among 8,000 PMUY programme beneficiaries similarly proposed that long travel times from rural Indian villages to refill points was a likely driver of a 30% lower LPG consumption26. Although the Indian study proposed that LPG access is important at a village level, we found that accessibility may play a role at smaller scales in an African context; a 10-minute-longer travel time to a retailer within a community was a deterrent to LPG usage (Fig. 4). These results contribute to growing evidence that accessibility, in addition to affordability, of LPG refills should be targeted by policymakers to expand LPG use.
Younger households and smaller families were more likely to primarily use LPG and had higher consumption rates (Fig. 5), which is similar to findings from a study of PMUY beneficiaries in India26. As household size increases, there is generally a demand for a greater amount of fuel and stove surface area to prepare larger meals to feed the entire family. Thus, open fires that accommodate larger pots can be more practical for substantive cooking than a single-burner LPG stove38,49. Moreover, it is typically easier for families with more children to collect biomass as there are more hands available to attend to other household chores50; one-fifth (21%) of households with 7 or more family members in our sample obtained free fuelwood for cooking compared with only 8% of households with 1–2 inhabitants (Supplementary Table 10).
In contrast to a study in India25, years spent cooking with LPG was not significantly associated with consumption, which potentially highlights the importance of LPG fuel costs remaining price competitive in the long term to prevent reversion to polluting cooking fuels. This finding is further supported by households previously cooking with LPG being more likely than households with no prior LPG experience to cite high cylinder refill costs as a reason for not cooking with LPG (Supplementary Table 6). Household income was not significantly associated with use of LPG as a primary fuel (Table 2), which demonstrates that usage does not necessarily intensify in a linear manner with increasing SES, but may follow a complicated trajectory due to various supply-related and contextual factors51,52.
The estimated median annual LPG per capita consumptions in Mbalmayo, Eldoret and Obuasi were relatively similar (40% higher, 13% higher and 8% lower, respectively) to national rates as last estimated in National Feasibility Assessments conducted by the Global LPG Partnership in 2017/2018 (14.2 kg capita–1 yr–1 in Cameroon, 12.8 kg capita–1 yr–1 in Kenya and 25.0 kg capita–1 yr–1 in Ghana)44,45,53. It is unclear if the differences result from geographical variation within countries, population-level changes in consumption from 2017 to 2019 or bias in the self-reporting of consumption (Supplementary Table 7), which has occurred in previous studies54. Nonetheless, the self-reported consumption rates are about half those of households in more developed countries (for example, Brazil, Indonesia and Peru) with well-established LPG supply chains18. The communities of Mbalmayo (27%) and Obuasi (39%) had a substantially higher prevalence of households that primarily cooked with LPG than those of Eldoret (5%); the prevalence of households using LPG in Eldoret is consistent with the proportion of rural households using LPG in Kenya (6%) reported in the 2019 Kenya Census55.
A lower prevalence and per capita LPG consumption in Eldoret compared with those in Obuasi and Mbalmayo are partially due to differences in national LPG policies between the three countries. In Cameroon, regulations regarding the storage and distribution of LPG have been in place since the 1970s53. Despite instances of cylinder shortages over the past couple of decades, new foreign-owned companies entered the Cameroonian market in the mid-2000s, which increased the number of cylinders in circulation and raised population-level LPG consumption. The Ghana LPG promotion programme started in 1990 to encourage households to adopt LPG44. The Ghanaian government has subsidized LPG over the past several decades (although subsidies were phased out in 2013) and Ghana partially produced LPG from a local refinery and offshore natural gas extraction, which spurred a higher population use of LPG (including as a transport fuel). Ghana was the first country in SSA to endorse a Sustainable Energy for All Action Plan in 2012 under the United Nations. In Kenya, a lack of proper enforcement rules has led to the diffusion of illegal refilling practices, which makes it difficult for legitimate companies to operate sustainably. A lack of LPG pricing regulation in Kenya contributed to a higher price (per kilogram) of LPG in Eldoret than those in Obuasi and Mbalmayo (Supplementary Table 3).
LPG safety concerns were prevalent among households that cooked with polluting fuels, particularly in Obuasi (30%) (Fig. 5). A higher proportion in Obuasi compared with those in the other communities is probably attributable to the ‘customer-owned’ cylinder model currently implemented in Ghana, which places customers in charge of cylinder maintenance and replacement, and thus contributes to more frequent serious LPG accidents45. The Ghanaian government is transitioning the population to the ‘branded cylinder recirculation model’, which ensures proper refilling practices and the correct disposal of cylinders, as LPG marketers are responsible for cylinder maintenance and safety56.
Participants in Eldoret who gathered firewood at no cost (42% of households compared with 5% in Obuasi and 22% in Mbalmayo (Supplementary Table 9)) were substantially less likely to purchase LPG for cooking (Supplementary Table 2). Further, households that purchased all their cooking fuels had nearly twice the probability (69%) of using LPG as the primary cooking fuel compared with households that gathered free fuelwood (37%) (Table 2). The ability to collect free firewood, assessed via forest cover as a proxy in some studies57, is a well-documented deterrent to LPG consumption16 and can lead to the discontinuation of LPG use among households in SSA58.
The reversion from clean to polluting cooking fuels is reported in longitudinal studies35, with a prevalence as high as 35% (China)59. Likewise, this study uncovered that 47% of households that exclusively cooked with polluting fuels had formerly cooked with LPG (Supplementary Table 6). Although unable to ascertain whether these households previously used LPG as their primary fuel, and whether participants have completely stopped using it or routinely switch between fuels (for example, due to periodic income fluctuations), unaffordable LPG refill costs played a key role in 37% of household decisions to discontinue their use of LPG (Supplementary Table 6). Nonetheless, there was high aspiration to cook with clean fuels among households that reverted to cooking with biomass, with only 7% reporting satisfaction with their current polluting fuel.
This study was statistically powered to examine supply- and demand-related determinants of LPG consumption in SSA. Although the calculation of self-reported annual LPG consumption via two different survey questions showed disagreement (Supplementary Fig. 3), sensitivity analyses revealed that this discrepancy did not substantially impact the modelling results (Supplementary Table 8). As the direction of misclassification between the self-reported LPG consumption variables was similar across all three communities (Supplementary Fig. 3) (consumption using self-reported number of annual refills was higher than that calculated via the average cylinder lifetime among 75% of households), we expect that this misclassification was non-differential and therefore biased towards a null finding. We recommend that future studies that collect self-reported data on LPG consumption phrase survey questions in terms of ‘average cylinder lifetime’ in addition to number of annual cylinder refills to help protect against overreporting. As other studies have found low agreement between self-reported and objective measures54, we further recommend that the absolute measures of LPG consumption and cylinder refill costs reported in this study be interpreted with caution.
This study examined household energy decisions in a unique peri-urban context. As the extent of fuel stacking and availability of free biomass typically varies between rural and peri-urban households31,43,57, and research has shown differences in LPG consumption in urban, rural and peri-urban settings44,45,53, the study results may not hold outside peri-urban communities. We further point out that primary cooking fuels can vary seasonally due to fluctuations in income or changes in cooking needs24. As cooking patterns can also fluctuate over the course of the year, the per capita LPG consumption rates derived from this cross-sectional study may not reflect long-term LPG usage. Further, as household energy decisions are complex, additional participatory research methods (for example, focus group discussions and visual participatory methods) are important to place the findings from the modelling in context and understand the perspectives of individuals who use the cooking fuels60. These qualitative research methods have been employed by CLEAN-Air(Africa) and the results will be shared in the future36.
This study presents empirical evidence of the critical role of supply-side determinants in increasing LPG consumption among peri-urban households in three SSA countries, even at small scales (for example, 10 minute travel intervals). Although a lower cylinder price of an LPG refill will undoubtedly increase its consumption, other amenable factors, such as shortening the distance to LPG retail points and improving access to multiburner stoves, represent short-term, palpable interventions that may be crucial to minimize fuel stacking and accelerate growth of the clean cooking market in peri-urban SSA.
This study, conducted as part of the CLEAN-Air(Africa) programme36, received ethical approval from the University of Liverpool, United Kingdom, and local ethics committees in each study country: Central Regional Ethics Committee for Human Health Research (Cameroon), Institutional Research and Ethics Committee for Moi Teaching and Referral Hospital and Moi University (Kenya) and Kintampo Health Research Centre (Ghana). Informed written consent was obtained from all the participants prior to conducting the study. No compensation was provided to participants for agreeing to take part in the survey.
The CLEAN-Air(Africa) programme consisted of applied research and capacity building within peri-urban communities in three SSA countries: Mbalmayo, an agricultural town in central Cameroon with 60,000 residents that is an hour drive away from Yaoundé, the country’s capital; Obuasi, a gold-mining community in southern Ashanti, Ghana, with a population of almost 200,000 that is an hour drive away from Kumasi (capital city of the Ashanti region); Eldoret, a town surrounded by agricultural land, located at an elevation of over 2,000 m in Western Kenya with a population of nearly 500,000 and currently the fastest growing town in Kenya according to the 2019 National Census. In each location, approximately 2,000 households were surveyed to ensure a sufficient sampling frame for comparative research between households cooking primarily with LPG and exclusively with polluting fuels in later phases of CLEAN-Air(Africa). Across all three study settings, a total of 6,424 households were asked to participate and 97% (n = 6,245) consented. Participants that did not typically cook at home and ate their meals primarily at local eateries (n = 607, 9%) were excluded, left a final study sample of 5,638 households.
Survey data were collected using secure web technology (Mobenzi Researcher in Cameroon and Kenya, and REDCap (Research Electronic Data Capture) in Ghana) from April to November 2019. Mobenzi is a data collection software system (data encrypted at source) whereby data from predefined surveys are collected by smartphone application and automatically uploaded via the phone’s SIM (subscriber identification module) card and synced to the Mobenzi cloud (or when the phone is connected to a wireless network if there is no mobile signal)61. REDCap is an encrypted web application to create and manage online surveys and databases; data are wirelessly imported directly to the database servers. Completion took approximately 20 min. Owing to a switch from random to purposive sampling (by primary cooking fuel type) midway through the data collection in Eldoret (to ensure a sufficient sample of households using LPG for future phases of CLEAN-Air(Africa) research), population-based results are reported among a subset of 757 households for this location.
The first outcome of interest was the use of LPG as a primary or secondary cooking fuel among all households that cooked with LPG at the time of the survey administration. Participants’ primary cooking fuel was determined from the question ‘What does this household use for cooking most of the time, including cooking food, making tea/coffee, boiling drinking water?’. Use of secondary cooking fuels was gauged from the question ‘What other fuels and energy sources does this household use for cooking food, making tea/coffee, boiling drinking water and/or starting the fire?’. No distinction was made between secondary and tertiary cooking fuels among households that reported three or more cooking fuels; hence, all the fuels that were not stated as the main cooking fuel are considered secondary fuels in this analysis.
The second outcome of interest was annual per capita consumption of LPG among all the households that used LPG as a primary or secondary fuel. The annual per capita LPG consumption (kg capita–1 yr–1) was estimated in two ways: (1) multiplying the self-reported LPG cylinder size by the number of annual refills and dividing by the number of household members and (2) dividing 12 months by the self-reported average duration (months) of a cylinder refill to obtain a second estimate of the self-reported number of annual refills and multiplying that quantity by cylinder size and dividing by the number of household members. Sensitivity analyses examined the effects of using both metrics as the outcome on modelling results. The distribution of annual per capita LPG consumption was right-skewed so data were natural log-transformed before modelling.
A two multilevel (households nested within communities) models were built: (1) use of LPG as a primary or secondary cooking fuel (logistic regression) and (2) self-reported quantity (kg) of LPG consumed per capita (log-linear regression). Variables were considered for both models based on a priori knowledge or previous literature, which suggested a potential association with household cooking fuel decisions. Individual variables were added or removed from the models based on their significance in the model and their effect on the coefficient of determination (R2) when added to the model, with consideration given to selection of parsimonious models. The list of variables included in the modelling are described in Supplementary Table 1. Results from logistic regression modelling are depicted as the average-adjusted predicted probability of using LPG as a primary cooking fuel. Findings from log-linear regression are portrayed as the average-adjusted annual LPG per capita consumption (kg capita–1 yr–1):
Model 1: LPG cooking fuel (primary/secondary)ik = β0 + β1 + bi + eik (logistic regression).
Model 2: ln(kg LPG capita–1 yr–1)ik = β0 + β1 + bi + eik (log-linear regression).
In Model 1, LPG cooking fuel (primary/secondary)ik represents whether the kth participant in community i uses LPG as a primary or secondary cooking fuel. In Model 2, ln(kg LPG capita–1 yr–1)ik represents the natural log transformed annual per capita consumption of the kth participant in community i. In both models, β0 is the overall intercept, β1 represents fixed effects, bi is the community-level random effect and eik is the residual error.
Model fit was assessed via a combination of the R2, Akaike information criterion and tenfold cross-validation (training and test datasets are split at the community level to ensure a more accurate evaluation of the model performance). The cross-validated R2 is reported for the linear model62 and the area under the receiver operating characteristic curve is reported for the logistic model63. All the data analysis was conducted in R (version 3.5.1)64.
Household SES was assessed via household income and highest level of education among household members, which have been shown to be associated with greater use of clean cooking fuels21,22,23. Additionally, a principal components analysis was run on household assets across all three communities combined to generate a measure of household SES additional to household income and education65. The first principal component was grouped into quartiles and tested as a predictor in both regression models. The full list of household assets included in the principal components analysis is provided in Supplementary Table 1.
Supply-side characteristics included participants’ perceptions about the availability of LPG at the retail point. Participants were asked how frequently LPG was unavailable at the retailer and could select from preset categories of (1) always available, (2) 4 times per year, (3) 4–12 times per year or (4) >12 times per year. Participants were asked to provide the current cost of the LPG cylinder they purchase. The cost provided by the participant was divided by the cylinder size used by the household to generate the per kilogram price. All per capita fuel prices in each country were converted to US dollars and grouped into quartiles (see Supplementary Table 1 for the price cutoff points). Participants were asked about the typical amount of time required to reach the LPG retailer (one-way) using their usual mode of transportation. Travel times were grouped into 10 min intervals. Participants were also asked about their usual mode of transport to obtain the LPG cylinder refill: (1) walking, (2) motorbike, (3) public transportation, (4) car or (5) home delivery. Lastly, a binary variable of whether the participant currently pays for all their cooking fuels or gathers biomass locally for free was considered in both models.
Cooking behaviours were characterized by the self-reported frequency of LPG use during the previous week (that is 1–7 days) and the number of years the participant has been cooking with LPG. Whether or not the participant used LPG exclusively or stacked with other fuels was included in the model of LPG annual per capita consumption. The number of LPG stove burners was also asked to determine if this may increase usage. Household demographics were accounted for by quantifying the number of individuals who lived in the household and the number of children under five years old. Marital status and sex of the fuel decision maker were also considered in all regression models.
The two outcomes assessed in this study, using LPG as a primary or secondary fuel and kilograms of LPG consumed per capita per year, do not account for the extent of polluting fuel displacement, and therefore may not directly correlate with health or climate benefits. Further studies that quantify LPG consumption alongside the quantity of polluting fuels used can improve how LPG supply-related factors contribute to potential health gains among households.
Additionally, self-reported quantitative data, which include LPG cylinder refill costs and transportation costs, may partially reflect user perceptions and thus be higher or lower than the actual value in some instances. To minimize the potential for bias to impact the results, quantitative predictors were grouped into quartiles before being added to the regression models (Supplementary Table 1); the resulting monotonically decreasing relationship between increasing transportation and the fuel cost ‘quartile’ and lower LPG per capita consumption is therefore likely to be a true association.
Despite these limitations, this modelling study incorporates a diverse set of household energy supply and demand-related variables and identifies new-found factors (for example, number of stove burners) that influence cooking fuel decisions. Thus, the findings highlight that the ability of LPG to meet households’ cooking needs (for example, the ability to cook multiple dishes simultaneously on multiple burners) may increase its consumption. End-user preferences should therefore be factored into future clean-energy scale-up efforts, particularly as larger family sizes in SSA typically have a much lower LPG consumption.
As all data in this study were self-reported, information on availability of LPG at retailers and fuel prices may be skewed by participants’ positive or negative views regarding LPG supply and cost. Future research that collects data on user perceptions on various aspects of cooking with and obtaining LPG cylinder refills, alongside objective supply-related measurements, is warranted. Nonetheless, the large sample size of this study is likely to minimize any meaningful effects of response bias on the statistically significant relationships found between several supply-side characteristics and LPG usage found in the modelling results.
Further information on research design is available in the Nature Research Reporting Summary linked to this article.
Data is still under use by CLEAN-Air(Africa) for future work, but can be made available to researchers upon reasonable request directed to the corresponding author.
The source code used in this study can be accessed through Figshare at https://doi.org/10.6084/m9.figshare.16699492.
State of Global Air 2020 (Health Effects Institute, 2020).
Bruce, N. et al. WHO indoor air quality guidelines on household fuel combustion: strategy implications of new evidence on interventions and exposure-risk functions. Atmos. Environ. 106, 451–457 (2015).
Po, J. Y., FitzGerald, J. M. & Carlsten, C. Respiratory disease associated with solid biomass fuel exposure in rural women and children: systematic review and meta-analysis. Thorax 66, 232–239 (2011).
Li, L. et al. Indoor air pollution from solid fuels and hypertension: a systematic review and meta-analysis. Environ. Pollut. 259, 113914 (2020).
Yu, K. et al. Association of solid fuel use with risk of cardiovascular and all-cause mortality in rural China. J. Am. Med. Assoc. 319, 1351–1361 (2018).
Sumpter, C. & Chandramohan, D. Systematic review and meta-analysis of the associations between indoor air pollution and tuberculosis. Tropical Med. Int. Health 18, 101–108 (2013).
Shupler, M. et al. Household and personal air pollution exposure measurements from 120 communities in eight countries: results from the PURE-AIR study. Lancet Planet. Health 4, e451–e462 (2020).
Quinn, A. K. et al. Association of carbon monoxide exposure with blood pressure among pregnant women in rural Ghana: Evidence from GRAPHS. Int. J. Hyg. Environ. Health 219, 176–183 (2016).
Agrawal, S. & Yamamoto, S. Effect of indoor air pollution from biomass and solid fuel combustion on symptoms of preeclampsia/eclampsia in Indian women. Indoor Air 25, 341–352 (2015).
Baumgartner, J. et al. Highway proximity and black carbon from cookstoves as a risk factor for higher blood pressure in rural China. Proc. Natl Acad. Sci. USA 111, 13229–13234 (2014).
Bailis, R., Drigo, R., Ghilardi, A. & Masera, O. The carbon footprint of traditional woodfuels. Nat. Clim. Change 5, 266–272 (2015).
Bond, T. C. & Sun, H. Can reducing black carbon emissions counteract global warming? Environ. Sci. Technol. 39, 5921–5926 (2005).
Kumar, P. & Mehta, S. Poverty, gender, and empowerment in sustained adoption of cleaner cooking systems: making the case for refined measurement. Energy Res. Soc. Sci. 19, 48–52 (2016).
Burning Opportunity: Clean Household Energy for Health, Sustainable Development, and Wellbeing of Women and Children (WHO, 2016); http://www.who.int/indoorair/publications/burning-opportunities/en/
World Energy Outlook 2020 (International Energy Agency, 2020); https://www.iea.org/reports/world-energy-outlook-2020
Bruce N. G., Aunan K., Rehfuess E. A. Liquefied Petroleum Gas as a Clean Cooking Fuel for Developing Countries: Implications for Climate, Forests, and Affordability (KfW Development Bank, 2017); https://static1.squarespace.com/static/53856e1ee4b00c6f1fc1f602/t/5b16ec08352f538a85f57d7c/1528228877332/2017_Liquid-Petroleum-Clean-Cooking_KfW.pdf
Bruce, N. et al. The Government-led initiative for LPG scale-up in Cameroon: programme development and initial evaluation. Energy Sustain. Dev. 46, 103–110 (2018).
Van Leeuwen V., Evans A. & Hyseni B. Increasing the Use of Liquefied Petroleum Gas in Cooking in Developing Countries Report no. 114846 (The World Bank, 2017); http://documents.worldbank.org/curated/en/707321494347176314/Increasing-the-use-of-liquefied-petroleum-gas-in-cooking-in-developing-countries
Shen, G. et al. Evaluating the performance of household liquefied petroleum gas cookstoves. Environ. Sci. Technol. 52, 904–915 (2018).
Simkovich, S. M. et al. A systematic review to evaluate the association between clean cooking technologies and time use in low- and middle-income countries. Int. J. Environ. Res. Public Health 16, 2277 (2019).
Heltberg, R. Fuel switching: evidence from eight developing countries. Energy Econ. 26, 869–887 (2004).
Leach, G. The energy transition. Energy Policy 20, 116–123 (1992).
Masera, O. R., Saatkamp, B. D. & Kammen, D. M. From linear fuel switching to multiple cooking strategies: a critique and alternative to the energy ladder model. World Dev. 28, 2083–2103 (2000).
Shankar, A. V. et al. Everybody stacks: lessons from household energy case studies to inform design principles for clean energy transitions. Energy Policy 141, 111468 (2020).
Mani, S., Jain, A., Tripathi, S. & Gould, C. F. The drivers of sustained use of liquified petroleum gas in India. Nat. Energy 5, 450–457 (2020).
Gould, C. F., Hou, X., Richmond, J., Sharma, A. & Urpelainen, J. Jointly modeling the adoption and use of clean cooking fuels in rural India. Environ. Res. Commun. 2, 085004 (2020).
Puzzolo, E., Pope, D., Stanistreet, D., Rehfuess, E. A. & Bruce, N. G. Clean fuels for resource-poor settings: a systematic review of barriers and enablers to adoption and sustained use. Environ. Res. 146, 218–234 (2016).
Lewis, J. J. & Pattanayak, S. K. Who adopts improved fuels and cookstoves? A systematic review. Environ. Health Perspect. 120, 637–645 (2012).
Puzzolo, E. et al. Supply considerations for scaling up clean cooking fuels for household energy in low- and middle-income countries. GeoHealth 3, 370–390 (2019).
Pope, D. et al. Household determinants of liquified petroleum gas (LPG) as a cooking fuel in SW Cameroon. EcoHealth 15, 729–743 (2018).
Stanistreet, D. et al. Barriers and facilitators to the adoption and sustained use of cleaner fuels in Southwest Cameroon: situating ‘lay’ knowledge within evidence-based policy and practice. Int. J. Environ. Res. Public Health 16, 4702 (2019).
Choumert-Nkolo, J., Combes Motel, P. & Le Roux, L. Stacking up the ladder: a panel data analysis of Tanzanian household energy choices. World Dev. 115, 222–235 (2019).
Alem, Y., Beyene, A. D., Köhlin, G. & Mekonnen, A. Modeling household cooking fuel choice: a panel multinomial logit approach. Energy Econ. 59, 129–137 (2016).
Rehfuess, E. A., Briggs, D. J., Joffe, M. & Best, N. Bayesian modelling of household solid fuel use: insights towards designing effective interventions to promote fuel switching in Africa. Environ. Res. 110, 725–732 (2010).
Shupler, M. et al. Household, community, sub-national and country-level predictors of primary cooking fuel switching in nine countries from the PURE study. Environ. Res. Lett. 14, 085006 (2019).
Puzzolo, E. et al. Clean energy access for the prevention of non-communicable disease in Africa: the NIHR CLEAN-Air (Africa) Global Health Research Group. Environ. Epidemiol. 3, 319 (2019).
Harmonized Survey Questions for Monitoring Household Energy Use and SDG Indicators 7.1.1 and 7.1.2 (WHO, 2018); https://www.who.int/airpollution/household/1_Harmonized_household_energy_survey_questions-list_format_final_Nov2019.pdf?ua=1
Campbell, C. A. et al. Investigating cooking activity patterns and perceptions of air quality interventions among women in urban Rwanda. Int. J. Environ. Res. Public Health 18, 5984 (2021).
Shupler, M. et al. Pay-as-you-go LPG supports sustainable clean cooking in Kenyan informal urban settlement, including during a period of COVID-19 lockdown. Appl. Energy 292(116769).
Ochieng, C. A., Zhang, Y., Nyabwa, J. K., Otieno, D. I. & Spillane, C. Household perspectives on cookstove and fuel stacking: a qualitative study in urban and rural Kenya. Energy Sustain. Dev. 59, 151–159 (2020).
Asante, K. P. et al. Ghana’s rural liquefied petroleum gas program scale up: a case study. Energy Sustain. Dev. 46, 94–102 (2018).
Rahut, D. B., Behera, B. & Ali, A. Factors determining household use of clean and renewable energy sources for lighting in Sub-Saharan Africa. Renew. Sustain. Energy Rev. 72, 661–672 (2017).
Wiedinmyer, C. et al. Rural–urban differences in cooking practices and exposures in Northern Ghana. Environ. Res. Lett. 12, 065009 (2017).
National Feasibility Study: LPG for Clean Cooking in Kenya (The Global LPG Partnership, 2018).
National Feasibility Assessment: LPG for Clean Cooking in Ghana (The Global LPG Partnership, 2018).
Aung, T. et al. Energy access and the ultra-poor: do unconditional social cash transfers close the energy access gap in Malawi? Energy Sustain. Dev. 60, 102–112 (2021).
Hsu, E. et al. Microfinance for clean cooking: what lessons can be learned for scaling up LPG adoption in Kenya through managed loans? Energy Policy 154, 112263 (2021).
Kar, A., Pachauri, S., Bailis, R. & Zerriffi, H. Using sales data to assess cooking gas adoption and the impact of India’s Ujjwala programme in rural Karnataka. Nat. Energy 4, 806–814 (2019).
Ngui, D., Mutua, J., Osiolo, H. & Aligula, E. Household energy demand in Kenya: an application of the linear approximate almost ideal demand system (LA-AIDS). Energy Policy 39, 7084–7094 (2011).
van der Kroon, B., Brouwer, R. & van Beukering, P. J. H. The energy ladder: theoretical myth or empirical truth? Results from a meta-analysis. Renew. Sustain. Energy Rev. 20(C), 504–513 (2013).
Bisaga, I. & Parikh, P. To climb or not to climb? Investigating energy use behaviour among Solar Home System adopters through energy ladder and social practice lens. Energy Res. Soc. Sci. 44, 293–303 (2018).
Neto-Bradley, A. P., Choudhary, R. & Bazaz, A. Slipping through the net: can data science approaches help target clean cooking policy interventions? Energy Policy 144, 111650 (2020).
National Feasibility Assessment: LPG for Clean Cooking in Cameroon (The Global LPG Partnership, 2019).
Kar, A., Brauer, M., Bailis, R. & Zerriffi, H. The risk of survey bias in self-reports vs. actual consumption of clean cooking fuels. World Dev. Perspect. 18, 100199 (2020).
2019 Kenya Population and Housing Census (Kenya National Bureau of Statistics, 2019); https://open.africa/dataset/2019-kenya-population-and-housing-census
Scaling LPG for Cooking in Developing Markets: Insights from Tanzania (Clean Cooking Alliance. 2019); https://www.enea-consulting.com/en/scaling-lpg-for-cooking-in-developing-markets/
Jagger, P. & Perez-Heydrich, C. Land use and household energy dynamics in Malawi. Environ. Res. Lett. 11, 125004 (2016).
Carrión, D. et al. Using longitudinal survey and sensor data to understand the social and ecological determinants of clean fuels use and discontinuance in rural Ghana. Environ. Res. Commun. 2, 095003 (2020).
Carter, E. et al. Household transitions to clean energy in a multiprovincial cohort study in China. Nat. Sustainability. 3, 42–50 (2020).
Ronzi, S. et al. Using photovoice methods as a community-based participatory research tool to advance uptake of clean cooking and improve health: the LPG adoption in Cameroon evaluation studies. Soc. Sci. Med 228, 30–40 (2019).
van Heerden, A., Norris, S., Tollman, S., Richter, L. & Rotheram-Borus, M. J. Collecting maternal health information from HIV-positive pregnant women using mobile phone-assisted face-to-face interviews in Southern Africa. J. Med. Internet Res. 15, e116 (2013).
Yuchi, W. et al. Evaluation of random forest regression and multiple linear regression for predicting indoor fine particulate matter concentrations in a highly polluted city. Environ. Pollut. 245, 746–753 (2019).
Maroco, J. et al. Data mining methods in the prediction of dementia: a real-data comparison of the accuracy, sensitivity and specificity of linear discriminant analysis, logistic regression, neural networks, support vector machines, classification trees and random forests. BMC Res. Notes 4, 299 (2011).
R Core Team R: a Language and Environment for Statistical Computing (R Foundation for Statistical Computing, 2017). http://www.R-project.org/
Vyas, S. & Kumaranayake, L. Constructing socio-economic status indices: how to use principal components analysis. Health Policy Plan 21, 459–468 (2006).
We express gratitude to the field staff at each of the three research institutions (Douala General Hospital, Moi University and Kintampo Health Research Centre) for their dedication and efficient effort in administering thousands of household surveys in a timely manner. This research was funded as part of the CLEAN-Air(Africa) Global Health Research Group by the National Institute for Health Research (NIHR) (ref. 17/63/155) (grant awarded to D.P.) using UK aid from the UK government to support global health research. All the authors are members of the CLEAN-Air(Africa) programme.
Department of Public Health, Policy and Systems, University of Liverpool, Liverpool, UK
Matthew Shupler, Rachel Anderson de Cuevas, Emily Nix, Elisa Puzzolo & Daniel Pope
School of Public Health, Moi University, Eldoret, Kenya
Judith Mangeni, Edna Sang & Diana Menya
Kintampo Health Research Centre, Kintampo, Ghana
Theresa Tawiah, Jason Saah, Mieks Twumasi, Seeba Amenga-Etego & Kwaku Poku Asante
Douala General Hospital, Douala, Cameroon
Miranda Baame, Emmanuel Betang & Bertrand Mbatchou
School of Public Health, University of Ghana, Accra, Ghana
Reginald Quansah
Global LPG Partnership (GLPGP), New York, USA
Elisa Puzzolo
You can also search for this author in
You can also search for this author in
You can also search for this author in
You can also search for this author in
You can also search for this author in
You can also search for this author in
You can also search for this author in
You can also search for this author in
You can also search for this author in
You can also search for this author in
You can also search for this author in
You can also search for this author in
You can also search for this author in
You can also search for this author in
You can also search for this author in
You can also search for this author in
You can also search for this author in
M.S. assisted with the survey design, supervised the data collection, managed, cleaned and analysed all the data, and wrote the first and final drafts of the paper. E.P. and D.P. designed and supervised the conduct of the CLEAN-Air(Africa) study and supervised the interpretation of the data. E.N. assisted with data cleaning, management and interpretation. M.B., E.B., J.M., E.S., T.T. and J.S. led the data collection and study logistics in their respective study countries. D.M., B.M. K.P.A. and R.Q. designed and supervised the conduct of the CLEAN-Air(Africa) study, directed the study implementation and supervised the data collection in their respective countries. D.P., E.P., R.A.d.C., M.T. and S.A.-E. helped oversee the data management in the CLEAN-Air(Africa) study. All the co-authors reviewed and commented on the final manuscript.
Correspondence to Matthew Shupler.
The authors declare no competing interests.
Peer review information Nature Energy thanks Abhishek Kar, Pamela Jagger and Caroline Ochieng for their contribution to the peer review of this work.
Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Supplementary Figs. 1–3, Tables 1–10 and questionnaire used.
Reprints and Permissions
Shupler, M., Mangeni, J., Tawiah, T. et al. Modelling of supply and demand-side determinants of liquefied petroleum gas consumption in peri-urban Cameroon, Ghana and Kenya. Nat Energy 6, 1198–1210 (2021). https://doi.org/10.1038/s41560-021-00933-3
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1038/s41560-021-00933-3
Anyone you share the following link with will be able to read this content:

Provided by the Springer Nature SharedIt content-sharing initiative
Nature Energy (2021)