Research Article | | Peer-Reviewed

Carbon Emission Reduction Potentials of Improved Biomass Cookstoves Used in Gambella Refugee Camps, Southwest Ethiopia

Received: 21 November 2025     Accepted: 13 January 2026     Published: 6 February 2026
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Abstract

In many countries of the world, households burn firewood or biomass to fulfill their cooking and heating needs. The excessive reliance on biomass fuels by inefficient traditional cookstove produces and emits substantial amount of smoke which brings effects associated with high indoor air pollution, deforestation, climate change and losses productivity. Therefore, this study focused on carbon emission reduction potentials of improved biomass cookstoves used in Gambella refugee camps and compares it with traditional open-fire stove. For this study, Water Boiling Test (WBT) was carried out at laboratory level. The most commonly used improved biomass cookstoves and the three stone traditional cook stove were selected for the assessment and comparison. The emission of greenhouse gasses (carbon monoxide, carbon dioxide and particulate matters) was used as indicators to compare the emissions of each stove. The results indicated that, three-stone open-fire traditional stove, Clay (User Centered Design-UCD), Flexy and Tikikil stoves were found to be the preferred mode of biomass cooking stove used by most refugees. From the experimental test results, the performance model showed a significant reduction in greenhouse gasses and/or pollutant (CO2, CO, and PM2.5) concentrations. The use of one Flexy stove could avoid the emission of 1.21 tons, Clay 1.15 tons, and Tikikil 0.96 tons of CO2e per stove per year. The average amount of CO emission from the three-stone stove was 1105ppm and from ICS was 370.3 ppm. Particulate matter (PM2.5) emissions of Flexy, Clay, Tikikil and Traditional cookstoves were recorded as 329, 339, 337, 614 mg respectively. Therefore, it can be conclude that improved biomass cook stoves can produce less smoke and reduce greenhouse gas emissions and health effects. Thus, concerned organizations should disseminate and monitor improved biomass cooking stoves for the refugees so as to protect individuals from negative impact of traditional three-stone cookstoves.

Published in Journal of Energy, Environmental & Chemical Engineering (Volume 11, Issue 1)
DOI 10.11648/j.jeece.20261101.11
Page(s) 1-11
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2026. Published by Science Publishing Group

Keywords

Emission Reduction, Gambella, Improved Biomass Cookstoves, Refugee, Water Boiling Test

1. Introduction
Globally, more than one-third (over 2.8 billion) of peoples lack access to modern energy and relies on combustion of traditional solid biomass through inefficient cookstoves to fulfill their primary energy needs . Cutting of trees and traditional fuelwood consumption for cooking purposes result in adverse effects on the environment. This in turn traps heat and warms the Earth, leading to climate change and its associated devastating consequences . Worldwide, approximately around 1–2.4 Gt CO2e of greenhouse gasses (GHGs) are emitted annually due to the production and use of fuelwood and charcoal by inefficient cookstoves, which are 2–7% of the global anthropogenic emissions . In addition, burning biomass fuels in traditional cookstoves or open fires emit large quantities of fine particulate matter (PM2.5) and carbon monoxide (CO) . Cooking with solid-fuels contributes to 12% of the global ambient PM2.5 burden and to 25% of ambient black carbon . This brings significant health disorders such as respiratory , blood pressure, and cardiovascular disorders mostly among women , as well as 3.2 million premature deaths per annum as of 2020 . Without any major change in policy, the number of people relying on traditional biomass fuels in 2030 is expected to remain roughly the same as now, about 40% of the current world population . Better strategies like improved cook stoves (ICSs) to reduce carbon emissions have the potential of simultaneously mitigating climate change, conserving forests and improving human livelihoods .
Over 80% of the populations in Africa rely on solid biomass or firewood in meeting their cooking energy needs and from this only 11% of the population makes use of clean cookstoves and fuels. This has undoubtedly contributed to deforestation and the current climate change crisis . In the 1990s, largely from developing countries, forests released about 5.8 Gt per year, which was more than all forms of transport combined . Recent estimates show that over 890 million people in sub-Saharan Africa depend on traditional fuels as their primary energy sources . The incomplete combustion of biomass fuels in traditional cookstoves also has an adverse effect on human health and climate due to the formation of black carbon . Indoor air pollution from traditional biomass fuels has a disproportionate impact on women and is listed among the top three causes of death in most countries of Sub-Saharan Africa . IEA estimates that Sub-saharan Africa depends on biomass for upwards of three-quarters of its energy, and that without major policy changes the vast majority of people will continue to rely on biomass fuels for the foreseeable future. Efficient biomass-based combustion devices and densified solid biofuel technology for energy production is promising to reduced greenhouse gas (GHG) emissions . The fuel in improved cookstoves is burned more efficiently, releasing reduced amounts of CO2 into the atmosphere. Energy-efficient cookstoves therefore offer many health, community and environmental benefits .
Ethiopia, like many African countries, is heavily reliant on biomass-based energy sources. The largest energy supply comes from waste and biomass covering the highest share of the total primary energy . This excessive reliance on biomass fuels and traditional open-fire cookstoves produces and emits substantial amount of smoke which affects human health associated with high indoor air pollution, high deforestation, climate change and losses of production opportunity . In Ethiopia, ~72,400 peoples die every year due to indoor air pollution from biomass fuel and kerosene . The government of Ethiopia (GoE) is striving to enhance energy access across the country by 2030, with an increasing rate of access by 1.7% annually from 2010–2019 to reduce CO2 emissions . There is a continued wide-spread of fuel saving improved cookstove technologies to reduce pressure on forests and the adverse impact of indoor air pollution for the last decades. Now a day, 1.2 million people of low-income households in Ethiopia have sustainable access to improved cooking technologies that use less biomass fuel . Thus, the promotion of such clean cookstoves is an important measure to improve the health and environmental conditions of people who are still relying on solid fuel burning for daily domestic energy supply .
The Moving Energy Initiative (MEI) estimates that forcibly displaced families living in camps are burning 64,700 acres of forest (equivalent to 49,000 football pitches) each year contributes to unsustainable wood harvesting, causing deforestation and reducing carbon uptake by forests . To address traditional use of fuels, significant and devoted efforts have been made on the advancement of cook-stoves over the last-to-recent decades . Currently, several prior strategies has been designed to reduce fuel-wood consumption and GHG emission which includes implementing ICSs, increasing fuel efficiency and changing the cooking behaviors . The main reason for distributing ICSs is to reduce forest degradation , reduce the GHGs emission , reduce indoor and outdoor pollution , improve the quality of health and enhance the socioeconomic benefit . ICSs can significantly reduce household exposure to indoor-air pollution resulting from burning of biomass fuels and abate emissions of CO2 by up to 75% compared to traditional stoves. Efficient stoves can save carbon, reduce women’s workload and improve air quality . Replacing traditional stoves with fuel‐efficient and lower‐emitting improved stoves can helps to mitigate those socio-economic and environmental problems . This study, therefore, evaluated the potential of improved biomass cooking stoves in greenhouse gas emission reduction at laboratory level more holistically by considering CO2, CO and PM2.5 and compares it with three-stone open-fire traditional cookstoves.
2. Materials and Methods
2.1. Materials
The following instruments were used for testing emissions of each identified biomass cookstoves.
1) Exhaust hood, including blower and collection duct with a variable ranges from 80-150 m3/h
2) CO2/CO analyzer with a variable ranges from 0–10,000/0–500 ppm
3) Bomb calorimeter
4) Flow grid
5) Scattering measurement with a variable ranges from 0-5000 g/m3
6) Carbon monoxide with a variable ranges from 0-2000 ppm
7) Carbon dioxide with a variable ranges from 0-5000 ppm
8) Filter-based particulate matter setup
2.2. Study Site Description and Sampling Technique
The study was carried out in selected refugee camps of Gambella region which is situated 766 km to the Southwest of Addis Ababa (capital of Ethiopia). Gambella is located at 7° 55' 19.087" N latitude and 34° 9' 11.501"E longitudes with an altitude of about 300-2300 m above sea level. For this study, three refugee camps i.e., Ngunyiel, Phignido and Jewi were selected purposively for the assessment due to the entirely dependence on biomass fuelwood for cooking and distribution of improved biomass cookstoves (IBCSs). The experimental test was carried out in Addis Ababa laboratory of the Ethiopian Ministry of Water, Irrigation and Energy (MoWIE) Center to evaluate performance of the stoves.
2.3. Description of Biomass Cookstoves
Source: Own survey data, 2022

Download: Download full-size image

Figure 1. Types of biomass cooking stoves used by the refugees.
Among the various available biomass cookstoves in each refugee camps; Flexy, Clay (UCD–User Center Design), Tikikil and Traditional open-fire cook stoves (TCS) was used for the study since they are the most common stoves adopted by a large proportion of the refugees (Figure 1).
2.4. Water Boiling Test (WBT)
The water boiling test (WBT version 4.2.3) was conducted in the Addis Ababa laboratory of the Ethiopian Ministry of Water Irrigation and Energy to determine emissions of GHGs by each identified stoves. The emissions of CO and CO2 by each biomass stove's were measured using IAQ-CALC meter while fine particulate matter (PM2.5) data were collected using an indoor air pollution meter. Both the IAQ-CALC meter and IAP Meter stored the data on data logger minute-by-minute over the entire measurement period. The test was done three times for each stove type and data on CO2, CO and PM2.5 emissions were collected three times following the standard WBT version 4.2.3 in a controlled laboratory setting . Background emissions were also accounted for by measuring concentrations of CO2, CO and PM2.5 before and during the test. The air temperature was 17.5–19°C and the local boiling point was 94°C. For this study, locally available and common type of biomass fuelwood (i.e., meth) was used to test the emission of each identified cookstoves. The wood sample was dried properly using sunlight and the average moisture content of the sample fuelwood was 8.32%.
2.5. Estimation GHG Emission Reduction
2.5.1. Estimation of the Carbon Dioxide (CO2) Emission Reduction
Estimate of the carbon dioxide (CO2) reduction is calculated using the AMS-II G methodology . Emission reduction from the use of efficient cooking stoves will be calculated as a product of the amount of woody biomass saved, i.e. fuel consumption, the fraction that is considered non-renewable biomass (fNRB), the emission factor for fossil fuel and the net calorific value (NCV) of biomass .
ERy, =By,×fNRB,×NCVBiomass×EF(1)
Where:
ERy=Emission reduction during year y in tCO2e
B_(y,)=Quantity of fuelwood saved (substitute or displayed) in tone
fNRB,= Fraction of non-renewable woody biomass saved by the project activity in year y (UNFCCC, default value for Ethiopia is 88%)
NCVBiomass= Net calorific value of the non-renewable woody biomass that is substituted (IPCC Change default for wood fuel is 0.015 TJ/ton or 15 MJ/kg)
EF= default emission factor (per unit of energy) which is 81.6 tCO2/TJ or 112 g CO2/MJ
By=Bold, cooking stove×(1-ƞoldƞnew ICS)(2)
Where,
ƞnew ICS=the efficiency of ICS in the study
ƞold= 10% [The default value of 10% will be applied as the systems to be replaced are three stone fires
Bold, cooking stove=By,deivce ×Ly(3)
Where,
Ly= The default net to gross adjustment factor of 0.95 was applied to account for leakages
By,deivce = Average annual consumption of woody biomass per appliance in tones per year
By,device=Bold, caption×Nresdent household×FWproportion(4)
Where,
FWproportion=Proportion of HH fuel wood consumed by cooking stove. Use 41.50% for cooking application
Bold, caption= Average baseline fuel wood consumption in tones per capita per year
Bold, capion=HCfuel wood,usage,yHCpopulation,y(5)
Where, HCfuel wood,usage,y=58,134,125t/year
HCpopulation,y=84,320,987
Bold,capion=0.689t/year for fuel wood
HCfuel wood,usage,y=fuel wood consumtion incubic meter ×wood density(6)
fuelwood consumption in cubic meter =80,185,000m3
wood density=0.727tm3
2.5.2. Measurement of PM2.5 and CO in the Hood
Figure 2. Setup for testing emissions.
The measurement of PM2.5 is conducted with portable air detector that put inside the hood (Figure 2). Hood system is widely used for testing the small cooking stove without a chimney. Hood method helps to capture all the exhaust in a hood, and measure the flow rate through the hood. The PM2.5 is collected using the detector that measure PM2.5 and the values were recorded manually. The measurement system includes two parts: a flue gas analyzer (testo330-2LL) that directly sampled gas and measured real-time concentrations of CO and GHGs.
Total Emission Test
To measure the total emission GHGs, the stove was kept inside a closed standard hood, Figure 2. The hood had an overall dimension of 1000 mm width × 750 mm length × 2820 mm height. It has gas mixing chamber with 330-2 LL model multi component gas analyzer. Readings of CO and CO2 were taken within 3 minutes interval .
2.6. Ethics Declarations
All procedures performed in studies involving human participants were in accordance with the ethical standards of Gambella University Institutional Research Committee. The study was approved by Institutional Review Board. Informed consent was obtained from all individual participants included in the study.
3. Results and Discussion
3.1. Greenhouse Gas (GHG) Emission Reduction Potentials of IBCS
3.1.1. Estimation of the Carbon Dioxide (CO2) Emission Reduction
The potential CO2e emissions avoided by each stove was calculated assuming the net calorific value of fuel-wood (air-dried) at 15 MJ/kg (Hall et al., 1994) and emission intensity of 109.7 g CO2e/MJ of fuelwood burned in traditional stoves . The total CO2 emission reduction per stove per year was significantly different between the traditional and improved stoves. CO2 emission reduction potential from ICSs were shown in Figure 3 which was taken from the estimate of CO2 reduction calculated using the AMS-II G methodology . The emission reduction potential of each IBCSs in terms of carbon credit saving was calculated as by using equation (1).
Figure 3. CO2 emission reduction potential of improved biomass cooking stoves.
The result indicated that Flexy, Clay and Tikikil reduced the carbon emissions by 1.21 tCO2/stove/year, 1.15 tCO2/stove/year and 0.96 tCO2/stove/year respectively (Figure 3). These mean that, ICSs reduced carbon emissions by an average of 1.1 tCO2/stove/year. Flexy stove reduced carbon emissions by 36.44% than Clay stove (34.64%) and Tikikil stove (28.92%). The amount of CO2e reduction using ICSs was found with in the range of CRGE strategy document, which is the abatement potential of 0.6–1.4 t CO2e per stove per year, depending on the stove type. If we extrapolate the result of CO2 emission reduction from the Ethiopian target to disseminate 31 million ICSs by 2030 (considering 50% each Flexy, Clay and Tikikil), around 17.05 million CO2e per year will be reduced. The result is in line with other similar studies . Additionally, the result is most approximately consistent with the finding of World Vision Ethiopia who reports ICSs emit 1.14t CO2/stove/year. The CO2 emission reduction potential of IBCS stove was within the range of the CRGE strategy documents which is the abatement potential of 0.6 – 1.4 t CO2e/stove/year, depending on the stove type . Furthermore, the result is also in line with DGB Group who founds that energy-efficient cookstove reduces CO2 emissions by 2.85 tonnes annually compared to traditional open-fire cooking.
The results suggest that compared to the traditional stove, the three ICSs can reduce household CO2e emissions substantially. Furthermore, this finding suggest that beyond fuel-wood savings, ICSs can have substantial potential for abating CO2 emissions, thereby assisting Ethiopia’s low-carbon economic development path and the global GHGs emissions reduction effort. Moreover, the large CO2 emission savings from improved stoves indicates to generate revenue from carbon credits for emission reductions under the United Nations Clean Development Mechanism (CDM) and other international Green Climate Funds by expanding ICSs programs in different parts of Ethiopia.
3.1.2. Measurement of Carbon Monoxide (CO)
Carbon-monoxide was chosen as indoor air pollutants to be measured since it has been associated with respiratory and cardiovascular health effects. Wood-burning produced extremely high emissions of CO and other gasses. CO concentrations during the water boiling experimental test of Flexy, Clay, Tikikil and TCS were measured separately (Table 1). From the finding it can be indicated that the CO emission from the three-stone stove was higher than that of the ICSs. The average amount of CO emission from the three-stone stove was 1105 ppm and from ICS was 370.3 ppm (Figure 4). Uncontrolled situations in the three-stone cookstove are the main contributor for higher CO concentrations. Flexy and Clay stove emitted significantly lower CO than the traditional cookstove. IBCSs reduced CO concentrations by 66.48% over the TCS. Less controlled combustion in the TCS is the main contributor to higher CO concentration. Even though each stove has its exclusive behavior, fuel feeding has two direct effects i.e., decreasing the flame temperature and at the same time increasing CO. Adding solid fuel during the stove operation makes a sharp increase in CO emission. On the other hand, air supply in the IBCSs through the fuel magazine and ash grate assured higher combustion efficiency and lower pollutant emissions. However, the emission levels of CO during burning biomass are significantly impacted by fuel moisture content and stove design. Solid fuels with inefficient TCS are an important source of severe Household Air Pollution (HAP) linked to many adverse health problems.
Figure 4. CO in ppm of biomass cooking stoves.
According to international standard for the Determination of Toxicity of Gases , CO will not be considered as toxic if its concentration in the atmospheric air doesn’t exceed 4,947 ppm. However, a person near the stove felt health problems like headache, nausea and dizziness. Thus, IBCSs can significantly reduce household exposure to indoor-air pollution resulting from the burning of biomass fuels compared to traditional stoves. Although Flexy, Clay and Tikikil stoves emitted relatively less CO than the traditional stove, the emissions from these ICS were above the proposed benchmark value of 20 g . The result is supported by studies . Similarly, Mamuye F. et al. reported that ICSs emit less amounts of CO as compared to traditional stove.
Table 1. Emission of Carbon Monoxide (CO).

Parameter

Type of biomass cookstoves

Flexy

Clay (UCD)

Tikikil

TCS

Emission of CO in ppm

517

547

679

1187

692

697

554

1876

704

619

479

1834

532

548

483

1621

471

374

421

1460

372

329

313

1345

231

268

294

1213

143

163

208

205

54

96

142

168

24

59

97

141

Average

374

370

367

1105

Source: Lab. Experiment result, 2022
3.2. PM2.5 Emissions from Biomass Cooking Stoves
The PM2.5 of each biomass cooking stoves was taken the average emitted in one hour by the interval of 5 minutes. From the result the PM2.5 emissions of Flexy, Clay, Tikikil and TCS were recorded 327, 341, 338, 614 mg respectively (Figure 5). The fine PM emissions from both improved stoves and the traditional stove were quite below the proposed benchmark value of 1500 mg . The same to CO, the emission levels of PM2.5 during burning biomass are significantly impacted by fuel moisture content and stove design. From this finding, PM2.5 emission reduction by Flexy, Clay, and Tikikil stoves were 34.33, 32.66 and 33.01%, respectively as compared with traditional cookstoves. Three stone stove releases high amount of PM2.5 than ICS which pollutes the environment more seriously. On the other hand, Flexy has a less impact on surrounding environment in terms of emitting PM followed by Clay and Tikikil cookstoves. Thus, it is better to use Flexy stoves for the refugees to have safe environment in terms of particulate matter or it is advisable to avoid using TCS to keep the surrounding environment clean from any particulate matter. The result is in line with other findings by Mamuye et al. and Mekonnen who reports PM2.5 concentration from the TCS was significantly higher than that of the IBCSs.
Figure 5. The PM2.5 emissions of biomass cooking stove.
The use of biomass, in fact, also produces emissions that are potentially harmful to health in the form of CO and PM2.5. The smaller the size of the PM2.5 is the higher the potential impact on health. Thus, from the result, we can conclude that households will be exposed more to toxins that cause respiratory diseases due to inhaling smoke if they still use TCS. Clean cookstoves which burn fuels efficiently can reduce smoke emissions (PM2.5), so that can significantly reduce the health risks of women and children.
4. Conclusion
The study was aimed to evaluate the potentials of improved biomass cookstoves in greenhouse gas emission reduction and compare them with three stone traditional cookstove based on experimental analyses through water boiling test (WBT) at laboratory level. The results indicated a significant reduction in greenhouse gasses and/or pollutants (CO2, CO and PM2.5) concentrations by the use of improved biomass cookstoves. Based on comparisons, the use of one Flexy stove could avoid the emission of 1.21 tons, Clay 1.15 tons, and Tikikil 0.96 tons of CO2e per stove per year. The average amount of CO emission from the three-stone stove was 1105ppm and from ICS was 370.3 ppm in average. Particulate matter (PM2.5) emissions of Flexy, Clay, Tikikil and Traditional cookstoves were recorded as 329, 339, 337, 614 mg respectively. The results indicated that shifting from traditional to improved cookstoves could mitigate CO2, CO and PM2.5 emissions. From the result, it is concluded that improved biomass cookstoves significantly reduce carbon emissions, whereas traditional cookstoves have high emissions that lead to climate change. Thus, it is advisable to promote and advertise for widely distribution of these improved biomass cooking stoves. Distributing energy-saving cooking stoves as a sustainable, eco-friendly energy solution for households in Gambella refugee camps and to Gambella town communities as well is also very crucial.
Abbreviations

CDM

Clean Development Mechanism

CO

Carbon Monoxide

CO2

Carbon Dioxide

CO2e

Carbon Dioxide Equivalents

CRGE

Climate Resilient Green Economy

GHG

Greenhouse Gas

GoE

Government of Ethiopia

IBCS

Improved Biomass Cook Stoves

ICS

Improved Cook Stoves

MEI

Moving Energy Initiative

MoWIE

Ministry of Water, Irrigation and Energy

PM2.5

Fine Particulate Matter

TCS

Traditional Cookstoves

UCD

User Center Design

WBT

Water Boiling Test

Acknowledgments
The authors acknowledge Gambella University for the financial support of this study.
Author Contributions
Fikre Destaw: Conceptualization, Data curation, Formal analysis, Funding acquisition, Investigation, Methodology, Project administration, Resources, Software, Supervision, Validation, Visualization, Writing – original draft, Writing – review & editing
Alemayehu Gurmessa: Data curation, Investigation, Supervision, Validation, Writing – original draft, Writing – review & editing
Amansisa Birhanu: Data curation, Investigation, Supervision, Validation, Writing – original draft, Writing – review & editing
Nyagoa Biel: Data curation, Investigation, Supervision, Validation, Writing – original draft, Writing – review & editing
Girma Tadesse: Data curation, Investigation, Supervision, Validation, Writing – original draft, Writing – review & editing
Kuey Peter: Data curation, Investigation, Supervision, Validation, Writing – original draft, Writing – review & editing
Data Availability Statement
The datasets used and/or analyzed during the study are available from the corresponding author upon reasonable request.
Conflicts of Interest
The authors declare no conflicts of interest.
References
[1] Adem KD, Ambie DA. (2017). Performance and emission reduction potential of micro-gasifier improved through better design. AIMS Energy. 1; 5(1): 63-76.
[2] Agbro EB, Ogie NA. (2012). A comprehensive review of biomass resources and biofuel production potential in Nigeria. Research journal in engineering and applied sciences. 1(3): 149-55.
[3] Anenberg SC, Balakrishnan K, Jetter J, Masera O, Mehta S, Moss J, Ramanathan V. (2013). Cleaner cooking solutions to achieve health, climate, and economic cobenefits. Environmental Science and Technology, 47(9), 3944-3952.
[4] Bailis R., Drigo R., Ghilardi A. and Masera O. (2015). The carbon footprint of traditional woodfuels. Nature Climate Change, 5(3), pp. 266-272.
[5] Barbour M., Udesen D., Bentson S., Pundle A., Tackman C., Evitt D., Means P., Scott P., Still D., Kramlich J. and Posner J. D., (2021). Development of wood-burning rocket cookstove with forced air-injection. Energy for Sustainable Development, 65, pp. 12-24.
[6] Barpatragohain R., Bharali N. and Dutta P. P. (2021). Thermal performance evaluation of an improved biomass cookstove for domestic applications. In Proceedings of International Conference on Thermofluids: KIIT Thermo 2020 (pp. 579-590). Springer Singapore.
[7] Bensch G. and Peters J. (2013). Alleviating deforestation pressures? Impacts of improved stove dissemination on charcoal consumption in urban Senegal. Land Economics, 89(4), pp. 676-698.
[8] Beyene A., Bluffstone R. A., Gebreegzhiaber Z., Martinsson P., Mekonnen A. and Vieider F. (2015). Do improved biomass cookstoves reduce fuelwood consumption and carbon emissions? Evidence from rural Ethiopia using a randomized treatment trial with electronic monitoring. Evidence from Rural Ethiopia Using a Randomized Treatment Trial with Electronic Monitoring (June 22, 2015). World Bank Policy Research Working Paper, (7324).
[9] Boafo-Mensah G., Darkwa K. M. and Laryea G. (2020). Effect of combustion chamber material on the performance of an improved biomass cookstove. Case Studies in Thermal Engineering, 21, p. 100688.
[10] Bond T. C., Doherty S. J., Fahey D. W., Forster P. M., Berntsen T., DeAngelo B. J., Flanner M. G., Ghan S., Kärcher B., Koch D. and Kinne S. (2013). Bounding the role of black carbon in the climate system: A scientific assessment. Journal of geophysical research: Atmospheres, 118(11), pp. 5380-5552.
[11] Chafe Z. A., Brauer M., Klimont Z., Van Dingenen R., Mehta S., Rao S., Riahi K., Dentener F. and Smith K. R. (2014). Household cooking with solid fuels contributes to ambient PM2.5 air pollution and the burden of disease. Environmental health perspectives, 122(12), pp. 1314-1320.
[12] Dam J. V. (2017). The charcoal transition: greening the charcoal value chain to mitigate climate change and improve local livelihoods.
[13] DGB Group (2022). Cookstoves for carbon reduction. Sustainability simplified: Carbon footprinting for beginners.
[14] Dresen E., DeVries B., Herold M., Verchot L. and Müller R. (2014). Fuelwood savings and carbon emission reductions by the use of improved cooking stoves in an Afromontane Forest, Ethiopia. Land, 3(3), pp. 1137-1157.
[15] Duguma L. A., Minang P. A., Freeman O. E. and Hager H. (2014). System wide impacts of fuel usage patterns in the Ethiopian highlands: Potentials for breaking the negative reinforcing feedback cycles. Energy for Sustainable Development, 20, pp. 77-85.
[16] EnDev (2014). Energising Development (EnDev) Ethiopia. Improved Cook Stoves (ICS).
[17] Ethiopia CSA (2012). Population Statistics Abstract.
[18] FDRE (2011). Ethiopia’s climate-resilient green Economy (CRGE). Federal Democratic Republic of Ethiopia, Addis Ababa, Ethiopia, 188.
[19] FDRE (2014). Ethiopia’s Climate-Resilient Green Economy Climate Resilience Strategy: Water and Energy, Ministry of Water, Irrigation and Energy, Federal Democratic Republic of Ethiopia (FDRE).
[20] Global Alliance for Clean Cookstoves (GACC) (2014). The Water Boiling Test Version 4.2.3 Cookstove Emissions and Efficiency in a Controlled Laboratory Setting,
[21] Gebreegziabher Z., Beyene A. D., Bluffstone R., Martinsson P., Mekonnen A. and Toman M. A. (2018). Fuel savings, cooking time and user satisfaction with improved biomass cookstoves: Evidence from controlled cooking tests in Ethiopia. Resource and Energy Economics, 52, pp. 173-185.
[22] Getahun E., Tessema D. and Gabbiye N. (2019). Design and development of household gasifier cooking stoves: natural versus forced draft. In Advances of Science and Technology: 6th EAI International Conference, ICAST 2018, Bahir Dar, Ethiopia, October 5-7, 2018, Proceedings 6 (pp. 298-314). Springer International Publishing.
[23] IEA,(2012). World Energy Outlook. International Energy Agency, Paris.
[24] IEA (2018a). World Energy Outlook. International Energy Agency, IEA, Paris.
[25] IPCC (2006). IPCC guidelines for national greenhouse gas inventories. Institute for Global Environmental Strategies, Hayama, Kanagawa, Japan.
[26] IS-Indian Standards (2013). BIS IS 13152-1 Portable Solid Biomass Cookstove (Chulha) Specificaition.
[27] Islam R., Sheba N. H., Siddique R. F., Hannan J. M. A. and Hossain S. (2023). Association of household fuel use with hypertension and blood pressure among adult women in rural Bangladesh: A cross‐sectional study. American Journal of Human Biology, 35(8), p. e23899.
[28] Lahn G. and Grafham O. (2015). Heat, light and power for refugees: saving lives, reducing costs.
[29] Lambe F., Jürisoo M., Wanjiru H. and Senyagwa J. (2015). Bringing clean, safe, affordable cooking energy to households across Africa: an agenda for action. Prepared by the Stockholm Environment Institute, Stockholm and Nairobi, for the new climate economy, 32.
[30] Lee C. M., Chandler C., Lazarus M. and Johnson F. X. (2013). Assessing the climate impacts of cookstove projects: issues in emissions accounting. Challenges in Sustainability, 1(2), pp. 53-71.
[31] MacCarty N., Still D. and Ogle D. (2010). Fuel use and emissions performance of fifty cooking stoves in the laboratory and related benchmarks of performance. Energy for sustainable development, 14(3), pp. 161-171.
[32] Mamuye F., Lemma B. and Woldeamanuel T. (2018). Emissions and fuel use performance of two improved stoves and determinants of their adoption in Dodola, southeastern Ethiopia. Sustainable Environment Research, 28(1), pp. 32-38.
[33] Manaye A., Amaha S., Gufi Y., Tesfamariam B., Worku A. and Abrha H. (2022). Fuelwood use and carbon emission reduction of improved biomass cookstoves: evidence from kitchen performance tests in Tigray, Ethiopia. Energy, Sustainability and Society, 12(1), p. 28.
[34] Mekonnen B. A., Liyew K. W. and Tigabu M. T. (2020). Solar cooking in Ethiopia: Experimental testing and performance evaluation of SK14 solar cooker. Case Studies in Thermal Engineering, 22, p. 100766.
[35] Mekonnen B. A. (2022). Thermal efficiency improvement and emission reduction potential by adopting improved biomass cookstoves for sauce-cooking process in rural Ethiopia. Case Studies in Thermal Engineering, 38, p. 102315.
[36] Mercy Corps (2010). Basic Guide to Fuel Effcient Stoves and Emission Testing, Portland OR 97204, USA; Edinburgh, EH9 1NJ, UK.
[37] Mondal M. A. H., Bryan E., Ringler C., Mekonnen D. and Rosegrant M. (2018). Ethiopian energy status and demand scenarios: prospects to improve energy efficiency and mitigate GHG emissions. Energy, 149, pp. 161-172.
[38] Mopoung S. and Udeye V. (2017). Characterization and evaluation of charcoal briquettes using banana peel and banana bunch waste for household heating. Am. J. Eng. Appl. Sci, 10(2), pp. 353-365.
[39] MoWIE-Ethiopia (2017). Energy Balance and Statistics for Years 2010/11–2016/17. Available online:
[40] Mulu Getachew Mengistu M. G. M., Belay Simane B. S., Getachew Eshete G. E. and Workneh, T. S. (2016). The environmental benefits of domestic biogas technology in rural Ethiopia.
[41] Onyeneke R. U., Nwajiuba C. U., Mmagu C. J., Aligbe J. O., Uwadoka C. O., Igberi C. O. and Amadi M. U. (2018). Impact of adoption of improved cook‐stove on different components of household welfare in rural communities in Nigeria: The case of Save80 cook‐stove in Kaduna. Environmental Progress & Sustainable Energy, 37(4), pp. 1327-1338.
[42] Rasoulkhani M., Ebrahimi-Nik M., Abbaspour-Fard M. H. and Rohani A. (2018). Comparative evaluation of the performance of an improved biomass cook stove and the traditional stoves of Iran. Sustainable Environment Research, 28(6), pp. 438-443.
[43] Roden C. A., Bond T. C., Conway S. and Pinel A. B. O. (2006). Emission factors and real-time optical properties of particles emitted from traditional wood burning cookstoves. Environmental science & technology, 40(21), pp. 6750-6757.
[44] Saatchi S. S., Harris N. L., Brown S., Lefsky M., Mitchard E. T., Salas W., Zutta B. R., Buermann W., Lewis S. L., Hagen S. and Petrova S. (2011). Benchmark map of forest carbon stocks in tropical regions across three continents. Proceedings of the national academy of sciences, 108(24), pp. 9899-9904.
[45] Sharma D. and Jain S. (2019). Impact of intervention of biomass cookstove technologies and kitchen characteristics on indoor air quality and human exposure in rural settings of India. Environment international, 123, pp. 240-255.
[46] Sutar K. B. (2022). Energy Efficiency, Emissions and Adoption of Biomass Cookstoves. In. Alternative Energies and Efficiency Evaluation. IntechOpen.
[47] Teka K., Welday Y. and Haftu M., (2018). Analysis of household's energy consumption, forest degradation and plantation requirements in Eastern Tigray, Northern Ethiopia. African journal of ecology, 56(3), pp. 499-506.
[48] Thomas E., Wickramasinghe K., Mendis S., Roberts N. and Foster C., (2015). Improved stove interventions to reduce household air pollution in low and middle income countries: a descriptive systematic review. BMC public health, 15, pp. 1-15.
[49] Tigabu A. (2014). Factors Affecting Adoption of Improved Cookstoves in Rural Areas: Evidence from ‘Mirt’ Injera Baking Stove (The Survey of Dembecha Woreda, Amhara Regional State, Ethiopia) (Doctoral dissertation, Mekelle University).
[50] UNFCCC (2012). CDM, Small-Scale Methodology: Energy Efficiency Measures in Thermal Applications of non-renewable biomass (AMS-II.G).
[51] UNSD (2013). Energy Statistics Yearbook.
[52] Van der Werf G. R., Morton D. C., DeFries R. S., Olivier J. G., Kasibhatla P. S., Jackson R. B., Collatz G. J. and Randerson J. T. (2009). CO2 emissions from forest loss. Nature geoscience, 2(11), pp. 737-738.
[53] Wassie Y. T. and Adaramola M. S. (2021). Analysis of potential fuel savings, economic and environmental effects of improved biomass cookstoves in rural Ethiopia. Journal of cleaner production, 280, p. 124700.
[54] Wathore R., Mortimer K. and Grieshop A. P. (2017). In-use emissions and estimated impacts of traditional, natural-and forced-draft cookstoves in rural Malawi. Environmental science & technology, 51(3), pp. 1929-1938.
[55] WHO (2016). Household air pollution and health – Fact Sheet N292. World Health Organization.
[56] WHO (2022). Household air pollution.
[57] World Vison Ethiopia (2013). Energy Efficient Stoves Program, CDM Program of Activities Design Document.
[58] Ye W., Thangavel G., Pillarisetti A., Steenland K., Peel J. L., Balakrishnan K., Jabbarzadeh S., Checkley W., Clasen T. and Hapin Investigators (2022). Association between personal exposure to household air pollution and gestational blood pressure among women using solid cooking fuels in rural Tamil Nadu, India. Environmental research, 208, p. 112756.
[59] Yip F., Christensen B., Sircar K., Naeher L., Bruce N., Pennise D., Lozier M., Pilishvili T., Farrar J. L., Stanistreet D. and Nyagol R. (2017). Assessment of traditional and improved stove use on household air pollution and personal exposures in rural western Kenya. Environment international, 99, pp. 185-191.
[60] Zhou Y., Zhang Z., Zhang Y., Wang Y., Yu Y., Ji F., Ahmad R. and Dong R. (2016). A comprehensive review on densified solid biofuel industry in China. Renewable and Sustainable Energy Reviews, 54, pp. 1412-1428.
[61] IEA (2020). Energy policy review. International Energy Agency
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    Destaw, F., Gurmessa, A., Birhanu, A., Biel, N., Tadesse, G., et al. (2026). Carbon Emission Reduction Potentials of Improved Biomass Cookstoves Used in Gambella Refugee Camps, Southwest Ethiopia. Journal of Energy, Environmental & Chemical Engineering, 11(1), 1-11. https://doi.org/10.11648/j.jeece.20261101.11

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    Destaw, F.; Gurmessa, A.; Birhanu, A.; Biel, N.; Tadesse, G., et al. Carbon Emission Reduction Potentials of Improved Biomass Cookstoves Used in Gambella Refugee Camps, Southwest Ethiopia. J. Energy Environ. Chem. Eng. 2026, 11(1), 1-11. doi: 10.11648/j.jeece.20261101.11

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    AMA Style

    Destaw F, Gurmessa A, Birhanu A, Biel N, Tadesse G, et al. Carbon Emission Reduction Potentials of Improved Biomass Cookstoves Used in Gambella Refugee Camps, Southwest Ethiopia. J Energy Environ Chem Eng. 2026;11(1):1-11. doi: 10.11648/j.jeece.20261101.11

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  • @article{10.11648/j.jeece.20261101.11,
      author = {Fikre Destaw and Alemayehu Gurmessa and Amansisa Birhanu and Nyagoa Biel and Girma Tadesse and Kuey Peter},
      title = {Carbon Emission Reduction Potentials of Improved Biomass Cookstoves Used in Gambella Refugee Camps, Southwest Ethiopia},
      journal = {Journal of Energy, Environmental & Chemical Engineering},
      volume = {11},
      number = {1},
      pages = {1-11},
      doi = {10.11648/j.jeece.20261101.11},
      url = {https://doi.org/10.11648/j.jeece.20261101.11},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.jeece.20261101.11},
      abstract = {In many countries of the world, households burn firewood or biomass to fulfill their cooking and heating needs. The excessive reliance on biomass fuels by inefficient traditional cookstove produces and emits substantial amount of smoke which brings effects associated with high indoor air pollution, deforestation, climate change and losses productivity. Therefore, this study focused on carbon emission reduction potentials of improved biomass cookstoves used in Gambella refugee camps and compares it with traditional open-fire stove. For this study, Water Boiling Test (WBT) was carried out at laboratory level. The most commonly used improved biomass cookstoves and the three stone traditional cook stove were selected for the assessment and comparison. The emission of greenhouse gasses (carbon monoxide, carbon dioxide and particulate matters) was used as indicators to compare the emissions of each stove. The results indicated that, three-stone open-fire traditional stove, Clay (User Centered Design-UCD), Flexy and Tikikil stoves were found to be the preferred mode of biomass cooking stove used by most refugees. From the experimental test results, the performance model showed a significant reduction in greenhouse gasses and/or pollutant (CO2, CO, and PM2.5) concentrations. The use of one Flexy stove could avoid the emission of 1.21 tons, Clay 1.15 tons, and Tikikil 0.96 tons of CO2e per stove per year. The average amount of CO emission from the three-stone stove was 1105ppm and from ICS was 370.3 ppm. Particulate matter (PM2.5) emissions of Flexy, Clay, Tikikil and Traditional cookstoves were recorded as 329, 339, 337, 614 mg respectively. Therefore, it can be conclude that improved biomass cook stoves can produce less smoke and reduce greenhouse gas emissions and health effects. Thus, concerned organizations should disseminate and monitor improved biomass cooking stoves for the refugees so as to protect individuals from negative impact of traditional three-stone cookstoves.},
     year = {2026}
    }
    

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  • TY  - JOUR
    T1  - Carbon Emission Reduction Potentials of Improved Biomass Cookstoves Used in Gambella Refugee Camps, Southwest Ethiopia
    AU  - Fikre Destaw
    AU  - Alemayehu Gurmessa
    AU  - Amansisa Birhanu
    AU  - Nyagoa Biel
    AU  - Girma Tadesse
    AU  - Kuey Peter
    Y1  - 2026/02/06
    PY  - 2026
    N1  - https://doi.org/10.11648/j.jeece.20261101.11
    DO  - 10.11648/j.jeece.20261101.11
    T2  - Journal of Energy, Environmental & Chemical Engineering
    JF  - Journal of Energy, Environmental & Chemical Engineering
    JO  - Journal of Energy, Environmental & Chemical Engineering
    SP  - 1
    EP  - 11
    PB  - Science Publishing Group
    SN  - 2637-434X
    UR  - https://doi.org/10.11648/j.jeece.20261101.11
    AB  - In many countries of the world, households burn firewood or biomass to fulfill their cooking and heating needs. The excessive reliance on biomass fuels by inefficient traditional cookstove produces and emits substantial amount of smoke which brings effects associated with high indoor air pollution, deforestation, climate change and losses productivity. Therefore, this study focused on carbon emission reduction potentials of improved biomass cookstoves used in Gambella refugee camps and compares it with traditional open-fire stove. For this study, Water Boiling Test (WBT) was carried out at laboratory level. The most commonly used improved biomass cookstoves and the three stone traditional cook stove were selected for the assessment and comparison. The emission of greenhouse gasses (carbon monoxide, carbon dioxide and particulate matters) was used as indicators to compare the emissions of each stove. The results indicated that, three-stone open-fire traditional stove, Clay (User Centered Design-UCD), Flexy and Tikikil stoves were found to be the preferred mode of biomass cooking stove used by most refugees. From the experimental test results, the performance model showed a significant reduction in greenhouse gasses and/or pollutant (CO2, CO, and PM2.5) concentrations. The use of one Flexy stove could avoid the emission of 1.21 tons, Clay 1.15 tons, and Tikikil 0.96 tons of CO2e per stove per year. The average amount of CO emission from the three-stone stove was 1105ppm and from ICS was 370.3 ppm. Particulate matter (PM2.5) emissions of Flexy, Clay, Tikikil and Traditional cookstoves were recorded as 329, 339, 337, 614 mg respectively. Therefore, it can be conclude that improved biomass cook stoves can produce less smoke and reduce greenhouse gas emissions and health effects. Thus, concerned organizations should disseminate and monitor improved biomass cooking stoves for the refugees so as to protect individuals from negative impact of traditional three-stone cookstoves.
    VL  - 11
    IS  - 1
    ER  - 

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Author Information
  • College of Agriculture and Natural Resource, Gambella University, Gambella, Ethiopia

  • College of Agriculture and Natural Resource, Gambella University, Gambella, Ethiopia

  • College of Agriculture and Natural Resource, Gambella University, Gambella, Ethiopia

  • College of Agriculture and Natural Resource, Gambella University, Gambella, Ethiopia

  • College of Engineering and Technology, Gambella University, Gambella, Ethiopia

  • College of Natural and Computational Science, Gambella University, Gambella, Ethiopia