Research Article | | Peer-Reviewed

Analytical Hierarchy Process Applied to Clean Burning Cookstove Design Concept Selection

Received: 6 March 2025     Accepted: 26 March 2025     Published: 22 April 2025
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Abstract

This study used the Analytic Hierarchy Process (AHP), a multi-criteria decision making (MCDM) method to evaluate six clean-burning cookstove designs - the Natural Draft Sunken Pot Rocket Stove, the Kirk Harris TLUD Stove, the Side Feed Bottom Air Forced Draft Stove, the Top Lit Forced Draft Stove, the Charcoal Stove and the SSM Jet-Flame Stove -for mass production in Cameroon, addressing the dual priorities of thermal efficiency and emissions reduction under the ISO/IWA Tiers of Performance framework. Building on a prior quantitative survey of cookstove performance, eight criteria— thermal efficiency, specific consumption, high and low power emissions (CO, PM2.5), indoor emissions (CO, PM2.5). —were used to assess the designs. Pairwise comparisons showed the charcoal stove as optimal for combustion efficiency (24% priority score) and the Kirk Harris TLUD stove as superior for minimizing emissions (37% score), demonstrating that design suitability depends on context-specific energy and environmental goals. The AHP methodology was validated through sensitivity analysis and a consistency ratio below 10%, confirming its robustness for structured decision-making. By systematically balancing technical performance, user needs, and environmental impact, this study underscores AHP’s utility in guiding the selection of clean energy technologies. The findings provide policy makers and manufacturers with actionable insights to prioritise designs that meet regional priorities, whether fuel efficiency in resource-constrained environments or emissions reduction in health-sensitive areas. This approach supports scalable, evidence-based transitions to sustainable cooking solutions in Cameroon and similar contexts.

Published in Industrial Engineering (Volume 9, Issue 1)
DOI 10.11648/j.ie.20250901.12
Page(s) 9-19
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), 2025. Published by Science Publishing Group

Keywords

Stove Design Selection, Analytical Hierarchy Process, Multicriteria Decision Making, Clean Burning Cookstove

1. Introduction
Currently, approximately 2.7 billion people in developing nations rely on biomass, such as animal waste, agricultural residues, and charcoal, for cooking and heating . In Cameroon, this dependence on biomass as a primary energy source is particularly pronounced, especially in rural areas where access to modern energy services remains limited. Biomass accounts for nearly 74.22% of the total energy consumption in the country, with wood fuel and charcoal being the most widely used sources . In rural regions of Cameroon, over 90% of households depend on traditional biomass for cooking, highlighting the persistent energy poverty in these areas .
Even in urban centers, where alternative energy sources like electricity and liquefied petroleum gas (LPG) are more accessible, a significant portion of the population continues to use charcoal and wood due to affordability and cultural preferences. This reliance on biomass has significant environmental and health implications, including deforestation and respiratory diseases caused by indoor air pollution. Despite efforts to promote cleaner energy alternatives, the transition remains slow due to economic constraints and entrenched energy practices.
The adverse environmental and health impacts associated with traditional cooking stoves have driven the development of advanced, safe, and efficient biomass cookstoves. Numerous alternative cooking technologies have been designed to deliver improvements over traditional stoves in terms of fuel efficiency and emissions . Recent studies have demonstrated the importance of evaluating cookstove performance across multiple criteria, including fuel efficiency, emissions reduction, and user acceptability.
For instance, Still, Bentson, and Li tested 15 improved cookstove designs in accordance with the ISO/IWA Tiers of Performance, highlighting significant variability in performance across different designs and underscoring the need for a systematic approach to selection. Their study revealed that while some designs excelled in thermal efficiency, others performed better in reducing emissions, emphasizing the importance of context-specific solutions. Similarly, MacCarty, Still, and Ogle evaluated the fuel use and emissions performance of 50 cookstove models in laboratory settings, identifying key benchmarks for performance. Their findings demonstrated the trade-offs between fuel efficiency, emissions reduction, and user acceptability, further reinforcing the necessity of a structured framework for comparing and selecting cookstove designs.
Given the growing number of cookstove designs available, selecting the most suitable option for re-design and mass production requires a robust and structured decision-making framework. The shift toward advanced cooking technologies with high combustion efficiency and low emissions is critical for achieving multiple objectives, including improved public health, reduced deforestation, and climate change mitigation. However, the diversity of available designs and the complexity of performance trade-offs necessitate the use of MCDM methods like AHP to ensure the selection of preferred cookstove designs. Multicriteria decision-making (MCDM) methods, such as the Analytic Hierarchy Process (AHP) which has been used in design concept selection , have emerged over the years as one of the most popular MCDM tools for formulating and analyzing multicriteria decisions in wide range of application . The large number of applications of AHP as a standalone methodology shows that researchers consider AHP as a credible methodology in its own right.
The AHP method can be implemented using various techniques, including the geometric mean, arithmetic mean, row sum of the adjusted Saaty matrix, reverse sum of Saaty matrix columns, row sum of the saaty matrix, and the Saaty method . In comparison to the Saaty method which provides the most accurate results, the geometric mean method in previous studies showed the least deviation (CI = 0.00010), followed by the row sum of the adjusted Saaty matrix (CI = 0.00256), reverse sum of Saaty matrix columns (CI = 0.00852), and row sums of the Saaty matrix (CI = 0.01261) .
A survey conducted among managers (Figure 1) revealed that the respondents viewed the Saaty method as the most complex and difficult to apply. In contrast, the geometric mean and arithmetic mean methods were considered the simplest. The Geometric mean method, which produces results nearly identical to the Saaty method, was chosen for this study to identify the preferred design clean-burning cookstove design for mass production in Cameroon due to its accuracy, simplicity and the fact that it does not require specialized software.
Figure 1. Difficulty Levels of Methods in the AHP Process .
2. Materials and Methods
The Analytic Hierarchy Process (AHP), developed by Saaty, is a widely used multicriteria decision-making (MCDM) method that uses mathematics and psychology to make and analyse complex decisions. AHP decomposes complex problems into a structured hierarchy comprising the problem goal, criteria, and alternatives. This structured approach enables decision-makers to systematically evaluate and prioritize options to identify the preferred solution that aligns with the problem’s parameters.
The AHP method was applied in this study following these key steps: (1) establishing the hierarchical structure, (2) pairwise comparison of criteria, (3) computation of the weight vector using the geometric mean method, (4) conducting a consistency test to ensure the reliability of judgments, (5) data collection, (6) normalization of the decision matrix, and (7) final decision-making. The geometric mean method was employed to compute the weight vector, ensuring a robust and mathematically sound prioritization of criteria.
2.1. Setting up of the Hierarchical Structure
The hierarchy of the AHP method usually consists of the goal, the alternatives for achieving the goal and the criteria that apply to the individual alternatives of the goal. It is a so-called three-level hierarchy, whereby the peak is the goal (the 1 st level), followed by the criteria (the 2 nd level), and lastly, the alternative solutions to the problem (the 3 rd level). The hierarchical structure used in this study is as follows:
Goal: The overarching objective of the decision-making process. In this case, the goal is to select the best clean-burning cookstove design.
Criteria
Alternatives
The study assumes stable fuel (charcoal, wood pellets, dry wood, etc.) availability for the six stoves. For instance, charcoal availability in Cameroon, a premise based on its current dominance as a household energy source, particularly biomass accounted for 74.22% of the country's total energy consumption in 2018 . This assumption is consistent with Cameroon's national development strategy 2020-2030 , which recognises the entrenched role of biomass in the energy mix, despite efforts to promote alternatives such as LPG.
In this study, two scenarios (prioritising thermal efficiency vs. indoor emissions) were explicitly designed to reflect different, aggregated priorities derived from stakeholder interviews, World health organisation health policy and empirical adoption studies . While stakeholder interviews informed the weighting of criteria, the scenarios reflect dominant, policy-oriented priorities rather than exhaustive stakeholder segmentation.
Figure 2. AHP decision hierarchy of problem.
2.2. Criteria Comparison
The AHP compare alternatives pairwise with respect to each criterion. Let A=aij be the pairwise comparison matrix, equation (1), where aij is the element of row i column j of the Saaty's matrix, n is the number the evaluated criteria or alternatives; aij expresses the intensity of the preference of criterion over criterion j. It holds that if criterion i is more important than criterion j, then ajj  {1, 2, 3, 4, 5, 6, 7, 8, 9}, on the other hand aij=1/aji .
A=a11a1nan1ann=aij(1)
The relative importance between two criteria is evaluated on the basis of Saaty's scale, a numerical scale ranging from 1 to 9, as described in Table 1.
Table 1. AHP scale for criteria comparison .

Scale

Relative importance of factor i compared to factor j

1*

Equally important

3

Moderately more important

5

Strongly more important

7

Very strongly more important

9

Extremely more important

2, 4, 6, 8

Intermediate values

2.3. Weight Vector Using Geometric Mean
After building the matrix A, the geometric mean of each row in the pairwise comparison matrix is calculated using the geometric mean method. The geometric mean method is considered to be a simpler method that produces almost identical results, and for which specialized programs are not needed .
gi=j=1naij1n, i=1, 2, ,n(2)
Where the geometric gi determines the utility of individual alternatives. The geometric mean values is normalized to derive the weight vector w:
wi=gii=1ngi(3)
Vector w gives the relative weights of individual alternatives or criteria.
2.4. Consistency Test
In order to check the consistency of the comparisons made by decision-makers, namely, the matrix A, AHP suggests a technique based on testing the consistency ratio (CR) which is calculated using equation (6). The pair-wise comparisons in a judgment matrix are considered to be adequate if the corresponding CR is less than 10%. If CR>0.1, the judgment made by the decision maker is inconsistent, as a result, the evaluations must be revised.
The consistency index (CI) will be estimated by computing Awi, the i-th element of the matrix vector product Aw and approximating the maximum eigenvalue, λ max, using equation (4).
λmax=1n i=1nAwiwi (4)
Then, the CI and CR values are calculated by using the expressions:
CI=λmax-nn-1(5)
CR=CIRI(6)
RI is a random index changing according the order n of the matrix as shown in Table 2. For example, a value of 1.41 was set for 8 criteria.
Table 2. AHP scale for criteria comparison .

Attributes

RI

3

0.58

4

0.90

5

1.21

6

1.24

7

1.32

8

1.41

9

1.45

10

1.49

2.5. Data Collection
Quantitative data for each alternative stoves with respect to the eight criteria were collected from literature survey. These stoves were tested under the LEMS emissions hood with the WBT 4.2.3 and were rated for performance using the 2015 IWA Tier system. The data was organised into a decision matrix where rows represent alternatives and columns represent criteria.
2.6. Decision Matrix Normalisation
The decision matrix was normalized to eliminate units and enable comparability by dividing each element by the sum of its respective column values. For benefit attributes (where higher values are preferred), equation (7) was applied, while for cost attributes (where lower values are preferred), equation (8) was used.
rij=xijmaxxj(7)
rij=minxjxij(8)
Here, xij is the value of alternative i for criterion j, and rij is the normalized value.
2.7. Final Decision
The last step is the selection of the preferred alternative based on the value of total utility. The final score for each alternative is the weighted sum of the normalized values across all criteria. It is obtained by summing the weighted normalized values for each alternative Si. Rank the alternatives based on their aggregated scores Si, as in equation (9). The alternative with the highest score Si is the best choice.
The final step involves selecting the preferred alternative based on its total utility. The score for each alternative is the weighted sum of its normalized values across all criteria, calculated by summing the weighted normalized values for each alternative Si, as shown in equation (9). The alternatives are then ranked according to their aggregated scores Si, with the alternative having the highest score (Si) being selected as the best choice.
Si=j=1nwj× rij(9)
3. Result and Discussion
Two pairwise comparison matrices were developed using the scale in Table 1, reflecting preferences derived from stakeholder interviews, World health organisation policies, and empirical studies on cookstove adoption. These matrices evaluate criteria for selecting the preferred clean cookstove design under two scenarios: Scenario 1: prioritising thermal efficiency; Scenario 2: prioritising indoor emissions. These scenarios aimed to represent dominant policy-oriented objectives (e.g. energy efficiency to reduce deforestation) and health-oriented priorities (e.g. minimising indoor emissions) that emerged as common themes across stakeholder groups. For example, rural households and policy makers both emphasised fuel economy in surveys, albeit for different reasons (cost savings vs. environmental sustainability), while urban consumers and health advocates prioritised low emissions.
Scenario 1 prioritises high thermal output with very high importance over indoor emissions (CO and PM2.5), reflecting stakeholder priorities and empirical evidence. Surveys of end-users and policy makers in Cameroon highlighted fuel economy and stove performance as critical drivers for mass adoption, consistent with studies in similar resource-constrained settings. Cameroon's national energy policy emphasises energy efficiency to reduce deforestation, justifying the focus on thermal output and fuel economy. Previous research shows that thermal efficiency is strongly correlated with user satisfaction and adoption rates in sub-Saharan Africa.
In Table 3, high power thermal efficiency was rated moderately important over low power specific consumption, as both are critical, but thermal efficiency is slightly more influential for overall performance in many contexts. High power thermal efficiency was also rated strongly more important than emissions criteria (CO and PM2.5), as fuel economy directly impacts household costs and adoption scalability. It was also ranked very highly over indoor emissions (CO and PM2.5).
Low specific power consumption was rated moderately more important than emissions criteria, as fuel efficiency at low power levels remains important for user satisfaction. It was also rated as very important compared to indoor emissions (CO and PM2.5). The emission criteria (high power CO, low power CO, high power PM2.5, low power PM2.5) were considered to be of equal importance as they collectively address environmental and health impacts. However, they were considered of moderate importance compared to the indoor emissions (CO and PM2.5), which were considered of equal importance due to their direct impact on the health of users.
Scenario 2 emphasises indoor emissions (CO and PM2.5) over thermal efficiency, based on Health evidence: WHO guidelines on indoor air quality and studies linking PM2.5 exposure to respiratory disease justify the increased importance of emissions. WHO air quality guideline for healthy air prioritises the reduction of household air pollution, in line with this weighting. Rural end-users interviewed in this study expressed heightened concerns about indoor air quality, particularly for women and children. This is reflected in the pairwise comparison matrix (Table 4), which captures the preferences of the decision maker, with more important criteria receiving higher numerical values and less important criteria receiving their reciprocal values.
In Table 4, indoor emissions (CO and PM2.5) are given very high importance over high power thermal efficiency and strong importance over low power specific consumption. They are also rated as moderately important for the emission criteria (high power CO, low power CO, high power PM2.5, low power PM2.5). Meanwhile, high power thermal efficiency is given moderate importance over low power specific consumption, as both are critical, but thermal efficiency has a slightly greater impact on overall performance.
The pairwise comparison matrices in Table 3 and Table 4 were used to calculate the weight vector for each criterion, which guides the evaluation of the alternatives . The results obtained using equations (1) and (2) are presented in Table 5.
Table 3. Pairwise comparison matrix (scenario 1).

Attributes

HPT Eff

LPS Cons

HP CO

LP CO

HP PM2.5

LP PM2.5

IE CO

IE PM2.5

HPT Eff

1

3

5

5

5

5

7

7

LPS Cons

1/3

1

3

3

3

3

5

5

HP CO

1/5

1/3

1

1

1

1

3

3

LP CO

1/5

1/3

1

1

1

1

3

3

HP PM

1/5

1/3

1

1

1

1

3

3

LP PM

1/5

1/3

1

1

1

1

3

3

IE CO

1/7

1/5

1/3

1/3

1/3

1/3

1

1

IE PM

1/7

1/5

1/3

1/3

1/3

1/3

1

1

Table 4. Pairwise comparison matrix (scenario 2).

Attributes

HPT Eff

LPS Cons

HP CO

LP CO

HP PM2.5

LP PM2.5

IE CO

IE PM2.5

HPT Eff

1

3

5

5

5

5

1/5

1/5

LPS Cons

1/3

1

3

3

3

3

1/5

1/5

HP CO

1/5

1/3

1

1

1

1

1/3

1/3

LP CO

HP PM

1/5

1/3

1

1

1

1

1/3

1/3

LP PM

1/5

1/3

1

1

1

1

1/3

1/3

IE CO

1/5

1/3

1

1

1

1

1/3

1/3

IE PM

5

5

3

3

3

3

1

1

Table 5. Computed weights.

HPT Eff

LPS Cons

HP CO

LP CO

HP PM2.5

LP PM2.5

IE CO

IE PM2.5

Weights 1

0.382

0.207

0.086

0.086

0.086

0.086

0.034

0.034

Weights 1

0.170

0.100

0.054

0.054

0.054

0.054

0.257

0.257

In Scenario 1, high power thermal efficiency is the most important criterion with a weight of 0.382, followed by low specific power consumption (weight = 0.207). This ranking is based on the strong importance of high power thermal efficiency compared to indoor emissions (CO and PM2.5). In contrast, in Scenario 2, Indoor emissions (CO and PM2.5) is the most important criterion (weight = 0.266) and high power thermal efficiency is the second most important (weight = 0.155), reflecting the greater emphasis on indoor emissions over thermal efficiency.
The maximum eigenvalues (λmax) for Table 3 and Table 4 were calculated using equations (3) and (4) and yielded values of 8.157 and 9.003, respectively. Table 4 has a Consistency Ratio (CR) of 0.02 (2%), which is well below the threshold of 10% . This indicates that the pairwise comparison matrix in the first scenario is highly consistent, and the weights derived from it are reliable. Table 5 has a CR of 10%, which is considered acceptable according to . To assess robustness, a sensitivity analysis was performed by varying the criterion weights by ±20%. The results showed stable consistency ratio in both scenarios. Therefore, the calculated weights are consistent and can be used in the evaluation procedure to determine the most appropriate clean-burning cookstove.
Data from a survey of clean-burning stoves tested in the laboratory emissions monitoring system using the WBT 4.2.3 and rated for performance using the 2015 IWA Tier System for each of the six alternative stoves , as shown in Table 6, form the decision matrix. Since the values in the decision matrix are on different scales, normalisation is necessary. By applying equations (7) and (8) to the data in Table 6, we obtain the normalised decision matrix shown in Table 7.
Table 6. Cookstove selection decision matrix.

HPT Eff

LPS Cons

HP CO

LP CO

HP PM2.5

LP PM2.5

IE CO

IE PM2.5

NDSP Rocket Stove

49.7

0.02

2.22

0.05

152.2

1.73

0.25

11.8

KHND TLUD Stove

45.2

0.023

0.01

0.01

8

0.1

0.001

0.73

SFBA Forced Draft Stove

47.1

0.01

1.76

0.01

47.2

0.47

0.16

4.5

TL Forced Draft Stove

42.7

0.01

0.35

0.04

37.4

0.06

0.22

3.9

Charcoal Stove

47

0.002

6.35

0.01

28.2

0.01

0.41

1.8

SSMJ-Flame Stove

40.6

0.032

2.82

0.09

26.6

1.133

0.39

5

Table 7. Normalised decision matrix.

HPT Eff

LPS Cons

HP CO

LP CO

HP PM2.5

LP PM2.5

IE CO

IE PM2.5

NDSP Rocket Stove

1.00

0.10

0.00

0.20

0.05

0.01

0.00

0.06

KHND TLUD Stove

0.91

0.09

1.00

1.00

1.00

0.10

1.00

1.00

SFBA Forced Draft Stove

0.95

0.20

0.01

1.00

0.17

0.02

0.01

0.16

TL Forced Draft Stove

0.86

0.20

0.03

0.25

0.21

0.17

0.00

0.19

Charcoal Stove

0.95

1.00

0.00

1.00

0.28

1.00

0.00

0.41

SSMJ-Flame Stove

0.82

0.06

0.00

0.11

0.30

0.01

0.00

0.15

Table 8. Cookstoves ranking.

Scenario 1

Scenario 2

Overall Priority

Rank

Overall Priority

Rank

NDSP Rocket Stove

0.41

4

0.21

5

KHND TLUD Stove

0.55

2

0.84

1

SFBA Forced Draft Stove

0.43

3

0.29

3

TL Forced Draft Stove

0.41

5

0.25

4

Charcoal Stove

0.69

1

0.49

2

SSMJ-Flame Stove

0.36

6

0.21

6

The alternatives were ranked based on the sum of their weighted normalised scores and are presented in Table 8. If high thermal performance is prioritised over indoor emissions (CO and PM2.5), the charcoal stove ranks highest. Conversely, when indoor emissions (CO and PM2.5) are given higher priority, the Kirk Harris Natural Draft TLUD stove ranks first. These rankings are consistent with the 2015 IWA Tier System where, of the six stoves considered, only the charcoal stove and the Kirk Harris Natural Draft TLUD stove achieved performance metrics that fell within Tier 4. Table 8 explicitly highlights the superior performance of the charcoal stove in terms of thermal efficiency (weight: 0.382) and the Kirk Harris TLUD stove in terms of low indoor emissions (weight: 0.266).
Surprisingly, the charcoal stove that achieved all Tier 4 scores for total emissions, indoor emissions, and efficiency – the highest tier level defined by the ISO IWA 11: 2012 guidelines came first in Scenario 1 and second in Scenario 2. When charcoal has the wood burned out of it, it can combust very cleanly, emitting almost no appreciable amounts of smoke. Even the CO can meet the Tier 4 standards when temperatures are hot enough. Charcoal can be a clean burning prepared fuel such as propane or alcohol. However, traditional charcoal is not a recommended option due to its inefficiencies and environmental drawbacks : (1) 62.5% of energy is lost during the conversion of wood to charcoal, (2) the production process generates significant smoke, and (3) lighting charcoal releases harmful PM2.5 emissions. In contrast, the densification of biomass into briquettes offers a cleaner, more sustainable alternative. These high-density, energy-efficient briquettes are produced using methods that significantly reduce energy losses, smoke emissions and overall environmental impact.
When criterion weights were varied by ±20% to assess the stability of the rankings, the analysis confirmed that the consistency ratios remained stable and the overall hierarchy of alternatives (charcoal stove and Kirk Harris TLUD) did not shift under these perturbations. This confirms the reliability of the methodology and reinforces the prioritisation logic. Prioritising the charcoal stove (for high combustion efficiency) is consistent with Cameroon's focus on reducing deforestation through improved fuel efficiency, as outlined in its National Development Strategy. The Kirk Harris TLUD (Low Emission Preference) stove supports Cameroon's public health objectives under the National Health Development Plan
4. Conclusions and Recommendations
This study applied the AHP to evaluate and select the most appropriate clean-burning cookstove design for mass production in Cameroon, focusing on heat transfer and combustion efficiency. Six cookstove designs were evaluated against eight key performance criteria - high power thermal efficiency, low power specific consumption, high and low power CO, high and low power PM2.5, indoor emissions of CO, indoor emissions of PM2.5 - using the ISO/IWA tiers of performance framework.
The charcoal stove emerged as optimal for fuel efficiency (24% score), while the Kirk Harris Natural Draft TLUD stove excelled in minimising emissions (37% score), highlighting that design suitability depends on context-specific priorities. The AHP’s robustness was validated by a consistency ratio of less than 10% and a sensitivity analysis, reinforcing its utility in structured decision-making for clean energy technologies. These results highlight that the preferred cookstove design depends on specific market requirements and the relative importance attached to each criterion. This study highlights the value of AHP as a structured and reliable decision-making tool for clean energy technology development, providing actionable insights for policy makers and manufacturers seeking to meet diverse user needs and environmental objectives.
However, AHP-derived priorities should serve as preliminary guidance, necessitating iterative refinement through pilot programmes and stakeholder engagement to address real-world complexities before scaling up production. To deepen environmental impact assessments, we recommend integrating Life Cycle Assessment (LCA) into future AHP frameworks, assessing criteria such as life cycle carbon footprint, material circularity, and disposal costs. Such hybrid analyses could align performance metrics with sustainability goals.
To accelerate adoption, policy measures are critical: tax incentives or grants for manufacturers could lower production barriers, while subsidies for low-income households—particularly in environmentally vulnerable regions—would enhance affordability. Pairing this with subsidized distribution of efficient charcoal stoves through existing initiatives could leverage established networks, ensuring rapid deployment where fuel efficiency is paramount.
These recommendations collectively bridge technical evaluation, environmental stewardship, and equitable access, offering policymakers and manufacturers a multifaceted strategy to meet diverse user needs and climate objectives. By embedding iterative feedback and targeted incentives, Cameroon and similar contexts can foster scalable, sustainable transitions to clean cooking solutions.
Abbreviations

NDSP Rocket Stove

Natural Draft Sunken Pot Rocket Stove

KHND TLUD Stove

Kirk Harris Natural Draft TLUD Stove

SFBA Forced Draft Stove

Side Feed Bottom Air Forced Draft Stove

TL Forced Draft Stove

Top Lit Forced Draft Stove

SSMJ-Flame Stove

SSM Jet-Flame Stove

HPT Eff

High Power Thermal Efficiency

LPS Cons

Low Power Specific Consumption

HP CO

High Power CO

LP CO

Low Power CO

HP PM2.5

High Power PM2.5

LP PM2.5

Low Power PM2.5

IE CO

Indoor Emissions of CO

IE PM2.5

Indoor Emissions of PM2.5

Acknowledgments
The authors gratefully acknowledge the Aprovecho Research Center for providing access to CAD drawings of clean-burning biomass cookstoves. Additionally, the authors express their sincere thanks to the referees and editors for their valuable comments and suggestions towards the improvement of the article.
Author Contributions
Tsapi Tchoupou Kevin: Conceptualization, Funding acquisition, Methodology, Project administration, Supervision, Validation, Writing – original draft, Writing – review & editing
Magnou Ekokem Belinda: Data curation, Formal Analysis, Investigation, Methodology, Writing – original draft, Writing – review & editing
Annouar Djidda Mahamat: Resources, Validation, Writing – review & editing
Bienvenu Kenmeugne: Resources, Validation, Writing – review & editing
Funding
This work is not supported by any external funding.
Data Availability Statement
The authors confirm that the data supporting the findings of this study are available within the article.
Conflicts of Interest
The authors declare no conflicts of interest.
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Cite This Article
  • APA Style

    Kevin, T. T., Belinda, M. E., Mahamat, A. D., Kenmeugne, B. (2025). Analytical Hierarchy Process Applied to Clean Burning Cookstove Design Concept Selection. Industrial Engineering, 9(1), 9-19. https://doi.org/10.11648/j.ie.20250901.12

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    ACS Style

    Kevin, T. T.; Belinda, M. E.; Mahamat, A. D.; Kenmeugne, B. Analytical Hierarchy Process Applied to Clean Burning Cookstove Design Concept Selection. Ind. Eng. 2025, 9(1), 9-19. doi: 10.11648/j.ie.20250901.12

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    AMA Style

    Kevin TT, Belinda ME, Mahamat AD, Kenmeugne B. Analytical Hierarchy Process Applied to Clean Burning Cookstove Design Concept Selection. Ind Eng. 2025;9(1):9-19. doi: 10.11648/j.ie.20250901.12

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  • @article{10.11648/j.ie.20250901.12,
      author = {Tsapi Tchoupou Kevin and Magnou Ekokem Belinda and Annouar Djidda Mahamat and Bienvenu Kenmeugne},
      title = {Analytical Hierarchy Process Applied to Clean Burning Cookstove Design Concept Selection
    },
      journal = {Industrial Engineering},
      volume = {9},
      number = {1},
      pages = {9-19},
      doi = {10.11648/j.ie.20250901.12},
      url = {https://doi.org/10.11648/j.ie.20250901.12},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ie.20250901.12},
      abstract = {This study used the Analytic Hierarchy Process (AHP), a multi-criteria decision making (MCDM) method to evaluate six clean-burning cookstove designs - the Natural Draft Sunken Pot Rocket Stove, the Kirk Harris TLUD Stove, the Side Feed Bottom Air Forced Draft Stove, the Top Lit Forced Draft Stove, the Charcoal Stove and the SSM Jet-Flame Stove -for mass production in Cameroon, addressing the dual priorities of thermal efficiency and emissions reduction under the ISO/IWA Tiers of Performance framework. Building on a prior quantitative survey of cookstove performance, eight criteria— thermal efficiency, specific consumption, high and low power emissions (CO, PM2.5), indoor emissions (CO, PM2.5). —were used to assess the designs. Pairwise comparisons showed the charcoal stove as optimal for combustion efficiency (24% priority score) and the Kirk Harris TLUD stove as superior for minimizing emissions (37% score), demonstrating that design suitability depends on context-specific energy and environmental goals. The AHP methodology was validated through sensitivity analysis and a consistency ratio below 10%, confirming its robustness for structured decision-making. By systematically balancing technical performance, user needs, and environmental impact, this study underscores AHP’s utility in guiding the selection of clean energy technologies. The findings provide policy makers and manufacturers with actionable insights to prioritise designs that meet regional priorities, whether fuel efficiency in resource-constrained environments or emissions reduction in health-sensitive areas. This approach supports scalable, evidence-based transitions to sustainable cooking solutions in Cameroon and similar contexts.
    },
     year = {2025}
    }
    

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  • TY  - JOUR
    T1  - Analytical Hierarchy Process Applied to Clean Burning Cookstove Design Concept Selection
    
    AU  - Tsapi Tchoupou Kevin
    AU  - Magnou Ekokem Belinda
    AU  - Annouar Djidda Mahamat
    AU  - Bienvenu Kenmeugne
    Y1  - 2025/04/22
    PY  - 2025
    N1  - https://doi.org/10.11648/j.ie.20250901.12
    DO  - 10.11648/j.ie.20250901.12
    T2  - Industrial Engineering
    JF  - Industrial Engineering
    JO  - Industrial Engineering
    SP  - 9
    EP  - 19
    PB  - Science Publishing Group
    SN  - 2640-1118
    UR  - https://doi.org/10.11648/j.ie.20250901.12
    AB  - This study used the Analytic Hierarchy Process (AHP), a multi-criteria decision making (MCDM) method to evaluate six clean-burning cookstove designs - the Natural Draft Sunken Pot Rocket Stove, the Kirk Harris TLUD Stove, the Side Feed Bottom Air Forced Draft Stove, the Top Lit Forced Draft Stove, the Charcoal Stove and the SSM Jet-Flame Stove -for mass production in Cameroon, addressing the dual priorities of thermal efficiency and emissions reduction under the ISO/IWA Tiers of Performance framework. Building on a prior quantitative survey of cookstove performance, eight criteria— thermal efficiency, specific consumption, high and low power emissions (CO, PM2.5), indoor emissions (CO, PM2.5). —were used to assess the designs. Pairwise comparisons showed the charcoal stove as optimal for combustion efficiency (24% priority score) and the Kirk Harris TLUD stove as superior for minimizing emissions (37% score), demonstrating that design suitability depends on context-specific energy and environmental goals. The AHP methodology was validated through sensitivity analysis and a consistency ratio below 10%, confirming its robustness for structured decision-making. By systematically balancing technical performance, user needs, and environmental impact, this study underscores AHP’s utility in guiding the selection of clean energy technologies. The findings provide policy makers and manufacturers with actionable insights to prioritise designs that meet regional priorities, whether fuel efficiency in resource-constrained environments or emissions reduction in health-sensitive areas. This approach supports scalable, evidence-based transitions to sustainable cooking solutions in Cameroon and similar contexts.
    
    VL  - 9
    IS  - 1
    ER  - 

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Author Information
  • Department of Mechanical and Industrial Engineering, National Higher Polytechnic Institute, Bamenda, Cameroon

    Research Fields: Industrial Engineering, Reliability & Maintenance, Quality Management, Lean Six Sigma, and Digital Manufacturing

  • Department of Mathematics and Computer Science, Faculty of Science, University of Bamenda, Yaounde, Cameroon

    Research Fields: Operational Research, Bayesian Statistics, Biostatistics, Data science, Machine learning

  • Department of Technology, Faculty of Exact and Applied Sciences, University of N’Djamena, N’Djamena, Chad

    Research Fields: Mechanical Behaviour of Materials, Material Characterisation, Material Properties, Material Testing, Fracture Mechanics, and High Temperature Materials

  • Department of Mechanical and Industrial Engineering, National Advanced School of Engineering, Yaoundé, Cameroon

    Research Fields: Design Engineering, Engineering Optimization, Solid & Applied Mechanics, Computational Mechanics, and Multiscale Materials Analysis