Abstract
Introduction:
Sustainable stormwater management requires strategic decision-making that balances environmental, technical, economic, and social considerations while strengthening organizational capacity and human resource readiness. This study aimed to develop a strategic decision-making framework for selecting sustainable stormwater management strategies using a Multi-Criteria Decision-Making (MCDM) approach.
Methods:
The study employed the Analytic Hierarchy Process (AHP) and Technique for Order Preference by Similarity to Ideal Solution (TOPSIS) to evaluate five alternative stormwater management strategies: conventional drainage, green infrastructure (GI), low-impact development (LID), nature-based solutions (NbS), and integrated stormwater management systems. Data were collected from 15 experts through structured questionnaires and semi-structured interviews. Four decision criteria—environmental, technical, economic, and social—were incorporated into the evaluation framework.
Results:
The AHP analysis showed that environmental criteria received the highest priority weight (38.2%), followed by economic (27.9%), technical (21.4%), and social (12.5%) criteria. TOPSIS results identified green infrastructure as the preferred strategy with the highest preference score (0.918), demonstrating superior overall performance across the evaluated criteria. Low-impact development and nature-based solutions also performed well, whereas conventional drainage ranked lowest due to its limited long-term sustainability. Sensitivity analysis confirmed the robustness of the ranking results.
Discussion:
The findings demonstrate that green infrastructure represents the most suitable strategy for sustainable stormwater management because it simultaneously improves environmental performance, enhances urban resilience, and provides broader social and economic benefits. Successful implementation, however, depends not only on technical feasibility but also on organizational readiness and the development of Green Human Resource Management (GHRM) competencies to support long-term sustainability.
1 Introduction
Large cities worldwide face serious challenges in stormwater management due to rapid urbanization, climate change, and the increasing use of impervious surfaces. The expansion of areas covered by concrete and asphalt reduces natural infiltration, increasing surface runoff, leading to flooding, erosion, and stress on drainage systems. This also leads to social and economic consequences such as disruption of activities, infrastructure damage, and increased maintenance costs (; ). Furthermore, climate change is increasing the frequency and intensity of extreme rainfall events, making conventional drainage systems based on historical data less adaptable (; ), Therefore, successful stormwater management depends not only on technical aspects but also on organizational readiness and human resource capacity.
Previous studies have shown that improvements in organizational capacity do not automatically translate into better organizational performance unless they are supported by enabling institutional mechanisms and effective implementation processes (). This indicates that sustainable stormwater management requires not only appropriate technical solutions but also organizational capabilities that can effectively implement strategic decisions.
Jakarta's rapid urbanization has created various challenges in urban infrastructure management, particularly related to stormwater management. The increase in impervious surface area, changes in land use, and limitations of conventional drainage systems have increased the risk of flooding and reduced the quality of the urban environment (; ). Therefore, a stormwater management approach is needed that is not only technically effective but also economically, socially, and environmentally sustainable ().
Various approaches have been developed to address this issue, such as Conventional Drainage Systems, GI, LID, NbS, and Integrated Stormwater Management Systems. Conventional approaches tend to focus on accelerating water flow, while GI, LID, and NbS emphasize rainwater retention, infiltration, and reuse as part of an ecological system (; ; ; ). Each approach has distinct characteristics, advantages, and limitations, making selecting the best alternative a complex, multi-criteria decision-making process. Furthermore, integrating green infrastructure into urban planning also provides long-term economic and social benefits, including reduced flood control costs and improved quality of life for urban residents ().
In this context, the Multi-Criteria Decision Making (MCDM) approach becomes relevant for supporting decision-making involving multiple conflicting criteria (; ). Methods such as the Analytical Hierarchy Process (AHP) allow for systematic weighting of criteria through pairwise comparisons, while the Technique for Order Preference by Similarity to Ideal Solution (TOPSIS) is used to rank alternatives based on their proximity to the ideal solution (). The AHP-TOPSIS combination has been widely used in decision-making studies due to its ability to integrate subjective and objective assessments.
Various studies have addressed stormwater management using both technical and ecosystem-based approaches, but most studies still focus solely on evaluating hydrological performance or cost efficiency, without comprehensively integrating strategic management and long-term planning perspectives (; ; ). Limitations of previous research include the tendency to use only quantitative approaches without integrating qualitative perspectives from stakeholders, and the lack of comprehensive comparisons of various stormwater management methods in the context of a developing city like Jakarta. Furthermore, the use of sensitivity analysis to test the stability of decision outcomes is still relatively limited in MCDM studies ().
Therefore, the novelty of this research lies in the integration of a strategic management framework with the MCDM method (AHP-TOPSIS) in evaluating stormwater management alternatives. The development of an evaluation model that comprehensively integrates technical, economic, environmental, and social dimensions in accordance with the Triple Bottom Line (TBL) principle (), The application of the model to the context of a developing metropolitan city like Jakarta also identifies strategic implications, including the importance of organizational capacity and human resources in supporting the implementation of sustainable stormwater strategies.
Based on these gaps, this study aims to develop a comprehensive decision-making framework using the AHP–TOPSIS method to evaluate sustainable stormwater management alternatives in Jakarta. This study integrates technical, economic, environmental, and social dimensions, while also incorporating qualitative insights from expert interviews. In addition, a sensitivity analysis is conducted to test the robustness of the decision results. This research is expected to contribute by providing a more holistic, robust, and practical framework for strategic urban stormwater management.
2 Literature review
2.1 Urban stormwater concept
Urban stormwater is rainwater runoff that occurs due to the increase in impermeable surfaces such as roads, buildings, and urban infrastructure. Urbanization causes significant changes to the natural hydrological cycle, resulting in increased runoff volume, flood frequency, and decreased water quality (; ). Furthermore, climate change increases the intensity and frequency of extreme rainfall events, making conventional drainage systems less effective in managing stormwater runoff (; ).
Stormwater also carries various pollutants such as heavy metals, sediment, and surface waste that can contaminate water bodies and disrupt urban ecosystems (). Therefore, stormwater management is a crucial component in supporting environmental sustainability and urban resilience to climate change and urbanization (). Traditional approaches to stormwater management utilize gray infrastructure such as drainage channels, canals, and pipes. However, this approach has limitations in supporting long-term sustainability (). Therefore, green infrastructure and LID-based approaches have been developed to increase water infiltration and reduce surface runoff (; ).
Green infrastructure such as permeable pavements, rain gardens, and green roofs have proven effective in reducing runoff volume and improving water quality (). Furthermore, the integration of green and gray infrastructure can increase the resilience of urban drainage systems and support sustainable urban development (; ). NbS also provide additional benefits such as improved environmental quality, reduced urban temperatures, and increased resilience to climate change (; ).
2.2 Strategic management in stormwater
Strategic management is a long-term planning and decision-making process aimed at improving the effectiveness and sustainability of management systems. In the context of stormwater, strategic management helps integrate various technical, economic, environmental, and social aspects in the management of urban drainage systems (). A strategic management approach enables decision-makers to design adaptive and sustainable strategies to address the challenges of urbanization and climate change (). Furthermore, the use of decision support systems and data-driven models can improve the effectiveness of stormwater management and support the development of more resilient cities (; ).
2.3 MCDM in stormwater management
Stormwater management involves various complex criteria, such as cost, technical effectiveness, environmental impact, and sustainability. Therefore, MCDM methods are used to assist decision-makers in systematically evaluating various alternatives ().
MCDM methods such as AHP, TOPSIS, and VIKOR have been widely used in stormwater management to determine the most optimal strategy (). The use of MCDM allows the evaluation of various green infrastructure alternatives and helps select the most effective and sustainable solution (; ).
The integration of MCDM with hydrological models such as the Storm Water Management Model (SWMM) also improves decision-making accuracy and supports the development of more efficient and sustainable stormwater systems ().
The use of MCDM provides a systematic framework to support sustainable and resilient urban development. This method allows the evaluation of various alternatives based on various criteria and assists decision-makers in selecting the most optimal strategy (). This approach also supports the integration of strategic planning, technology, and environmental sustainability in urban stormwater management (). Thus, the integration of strategic management and MCDM is an effective approach to increasing urban resilience to flooding and climate change and supporting sustainable urban development (; ).
Recent developments in Multi-Criteria Decision Making (MCDM) methods demonstrate the increasing use of fuzzy approaches to accommodate uncertainty and subjectivity in expert judgment. Methods such as Fuzzy AHP and Fuzzy TOPSIS have been widely used in various complex decision-making contexts, including water resource management and the selection of sustainable strategies (; ).
Several studies have shown that fuzzy approaches can improve model accuracy and flexibility compared to classical methods, particularly in conditions of ambiguous or uncertain data (; ). Therefore, the integration of fuzzy methods in future research could provide an opportunity to develop more adaptive and comprehensive models.
Various MCDM methods such as ELECTRE, PROMETHEE, and VIKOR have been widely applied in environmental decision-making. ELECTRE is effective in handling outranking relations but tends to be complex in interpretation. PROMETHEE provides clear ranking but requires careful parameter selection. VIKOR focuses on compromise solutions but is sensitive to weight changes.
Compared to these methods, the integration of AHP and TOPSIS offers several advantages. AHP is effective in determining criteria weights through structured pairwise comparisons, while TOPSIS provides a clear ranking based on distance from the ideal solution. This combination is relatively simple, transparent, and suitable for integrating both qualitative and quantitative data. However, this method also has limitations, particularly in handling uncertainty, which can be addressed in future studies using fuzzy approaches.
2.4 Alternative stormwater strategies
The alternative strategies evaluated in this study were selected based on a Scopus-indexed literature review and international best practices in urban stormwater management. These alternatives represent key approaches used globally and are relevant to support strategic decision-making in sustainable urban infrastructure management (; ; ).
Gray infrastructure (GI) is a conventional approach that uses concrete channels, canals, and pipelines to rapidly channel stormwater runoff. This approach is effective for short-term flood control but has limitations in supporting sustainability and climate change adaptation because it does not increase infiltration and long-term system resilience (; ). GI and Low Impact Development (LID) are sustainable approaches that mimic natural hydrological processes by increasing infiltration, retention, and management of stormwater at the source, such as permeable pavement, green roofs, and bioretention. This approach has proven effective in reducing runoff, improving water quality, and providing environmental, social, and economic benefits (; ; ). NbS use ecosystem-based processes, such as green space and wetland restoration, to increase urban resilience to flooding and climate change, while providing ecological benefits and improving the quality of life for residents (; ). An Integrated Stormwater Management System is a strategic approach that integrates various management methods, including gray infrastructure, green infrastructure, and ecosystem-based solutions, to holistically improve the effectiveness, efficiency, and sustainability of the system (; ).
From a strategic management perspective, each alternative has different implications for resource allocation, organizational capacity, and human resource competency requirements in the planning, implementation, and management of sustainable infrastructure. Therefore, evaluating alternative strategies is not only crucial for determining optimal technical solutions, but also for supporting strategic decision-making and organizational capacity development in sustainable stormwater management.
Therefore, these five alternatives are suitable for evaluation using MCDM methods, specifically AHP and TOPSIS, to support a structured, objective, and sustainable strategic decision-making framework (; ). The characteristics, advantages, and limitations of the five stormwater management approaches evaluated in this study are summarized in Table 1.
Table 1
| Approach | Main focus | Key characteristics | Advantages | Limitations |
|---|---|---|---|---|
| Conventional drainage | Rapid water conveyance | Concrete channels, pipes, centralized system | Effective for short-term flood control | Low sustainability, no infiltration |
| Green infrastructure (GI) | Ecological integration | Green roofs, bioswales, permeable surfaces | Improves water quality, reduces runoff, multi-benefit | Requires land and maintenance |
| Low impact development (LID) | Source control | Small-scale, decentralized infiltration | Flexible, reduces runoff at source | Limited impact at large scale |
| Nature-based Solutions (NbS) | Ecosystem-based approach | Wetlands, urban forests, natural systems | High environmental and social benefits | Complex implementation |
| Integrated System | Hybrid approach | Combines gray + green + NbS | Holistic and adaptive | High complexity and coordination needs |
Comparison of rainwater management approaches.
Although GI, LID, and NbS share similarities in promoting infiltration and sustainability, their main differences lie in scale, approach, and implementation focus. LID operates at a micro-scale and emphasizes source control, GI focuses on integrating green elements into urban infrastructure, while NbS adopts a broader ecosystem-based perspective. Integrated systems combine these approaches to achieve optimal performance.
The main differences between the approaches lie in the level of integration of ecological aspects, the scale of implementation, and the orientation toward long-term sustainability.
In the context of modern sustainability, the NbS approach also aligns with the principles of the circular economy, which emphasizes efficient resource use and rainwater reuse as part of a closed-loop system. Stormwater management functions not only as a drainage system but also as an alternative resource through rainwater harvesting, groundwater recharge, and enhancing the value of urban ecosystems.
The integration of circular economy principles into NbS allows for the simultaneous optimization of environmental, economic, and social benefits, thus supporting more resilient and sustainable urban development.
3 Research methods
3.1 Research design
This study uses a quantitative approach with the MCDM method to determine the most sustainable urban stormwater management strategy and increase city resilience. This method was chosen because stormwater management involves various multidimensional criteria, such as environmental, economic, technical, and social aspects. Therefore, a systematic approach is needed to objectively evaluate and prioritize alternative strategies (; ). The MCDM approach has been widely used in urban water resources management because it integrates various indicators and supports complex decision-making (; ).
3.2 Research location and object
The research was conducted in Jakarta, an Indonesian city, which faces stormwater runoff issues, such as increased impervious surfaces, flood risk, and limitations of conventional drainage systems. The unit of analysis in this study is alternative urban stormwater management strategies, which can include conventional drainage infrastructure, green infrastructure, LID, NbS, and integrated management systems. These alternatives were selected based on literature reviews and best practices in sustainable stormwater management.
3.3 Data collection techniques
This research used primary and secondary data. Primary data was obtained through an expert judgment approach to conduct pairwise comparisons between criteria and alternatives within the MCDM framework, specifically the AHP. This approach is commonly used in complex decision-making because it systematically integrates professional knowledge and experience (; ). Expert selection was conducted using a purposive sampling technique with the following criteria: a minimum of a master's degree in a relevant field (environmental engineering, civil engineering, urban and regional planning, or infrastructure management), ≥5 years of professional experience in urban water management or drainage, direct involvement in stormwater planning, implementation, research, or policy, and willingness to participate voluntarily. These criteria were intended to ensure the competence and credibility of the respondents. A total of 15 experts participated in this study. This number falls within the recommended range in AHP and expert-based decision-making studies (5–20 respondents), which is considered sufficient to achieve stability and consistency in assessments (; ). Previous studies have also shown that 10–20 experts is common practice in MCDM research to maintain a balance between decision quality and result reliability ().
This study used a structured questionnaire based on the AHP pairwise comparison scale to obtain expert assessments of the relative importance of criteria and alternative stormwater strategies (Supplementary File 1). The questionnaire consisted of three sections: respondent profiles, pairwise comparisons between criteria, and pairwise comparisons between alternatives using the Saaty 1–9 scale (). In addition to the questionnaire, semi-structured interviews were also conducted to gain a deeper understanding of expert considerations in stormwater strategy selection and strategic implications, including organizational readiness and human resource capacity to support sustainable strategy implementation. Interview data was used to strengthen the interpretation of the quantitative analysis results and increase the validity of the study.
The semi-structured interview data was analyzed using a thematic analysis approach. This process included the following stages:
1. Transcription of interview results
2. Open coding to identify initial themes
3. Categorization based on criterion dimensions (environmental, economic, technical, social)
4. Interpretation to support the quantitative AHP results
This approach was used to ensure that the subjective perspectives of experts could be systematically integrated into the decision-making framework.
Secondary data was obtained from journal articles, government reports, urban planning documents, and literature related to stormwater management. Secondary data was used to identify relevant criteria and strategic alternatives (). The criteria used in this study were adapted from previous studies and cover four main dimensions: Environmental Criteria (Runoff Reduction, Water Quality Improvement, Ecosystem Conservation), Economic Criteria (Implementation Cost, Maintenance Cost, Long-Term Efficiency), Technical Criteria (System Effectiveness, Ease of Implementation, System Reliability), and Social Criteria (Community Acceptance, Social Impact, Contribution to Quality of Life). These criteria have been widely used in the evaluation of sustainable urban water management (; ).
The AHP hierarchy developed in this study consists of four levels to better represent the complexity of sustainable stormwater management decision-making. The first level defines the overall objective, which is to select the most sustainable stormwater management strategy. The second level consists of four primary decision criteria: Environmental, Economic, Technical, and Social. The third level consists of 12 sub-criteria derived from an extensive literature review and expert consultation. Specifically, the Environmental criteria include Runoff Reduction, Water Quality Improvement, and Ecosystem Conservation; the Economic criteria include Initial Investment Cost, Maintenance Cost, and Long-Term Cost Efficiency; the Technical criteria include System Effectiveness, Ease of Implementation, and System Reliability; and the Social criteria include Community Acceptance, Social Impact, and Quality of Life Improvement. The fourth level consists of five alternative stormwater management strategies: Conventional Drainage, Green Infrastructure, Low-Impact Development (LID), Nature-Based Solutions (NbS), and Integrated Stormwater Management Systems.
This hierarchical structure allows for a more comprehensive evaluation by capturing the multidimensional nature of sustainable stormwater management while enhancing the transparency and robustness of the AHP-based decision-making framework (Figure 1).
Figure 1
3.4 Research criteria and indicators
The main criteria, sub-criteria, and their operational descriptions used in the AHP model are presented in Table 2. Based on the literature review and interview results, the criteria used in this study encompass technical, economic, environmental, and social aspects. The selection of these criteria is based on previous research stating that stormwater management must consider various dimensions of sustainability in an integrated manner (; ; ; ; ).
Table 2
| Main criteria | Sub-criteria | Operational description |
|---|---|---|
| Environmental | Runoff reduction | Ability to reduce surface runoff volume |
| Water quality improvement | Improvement of receiving water quality | |
| Ecosystem conservation | Protection and enhancement of ecosystem functions | |
| Economic | Initial investment cost | Capital expenditure for infrastructure implementation |
| Maintenance cost | Operation and maintenance expenditure | |
| Long-term cost efficiency | Life-cycle economic efficiency and cost savings | |
| Technical | System effectiveness | Effectiveness in stormwater management |
| Ease of implementation | Technical feasibility and constructability | |
| System reliability | Reliability and operational performance | |
| Social | Community acceptance | Public acceptance and stakeholder support |
| Social impact | Positive impacts on communities | |
| Quality of life improvement | Contribution to urban livability and well-being |
Hierarchical criteria, sub-criteria, and descriptions used in the AHP model.
Indicators for each criterion were selected to represent key aspects of stormwater management: technical effectiveness, cost efficiency, environmental impact, and social acceptability. This approach aligns with the concept of sustainable development, which emphasizes a balance between economic, environmental, and social aspects in decision-making.
Each alternative was evaluated based on specific indicators under each criterion. For example, technical indicators include runoff reduction effectiveness and system reliability; economic indicators include investment and maintenance costs; environmental indicators include water quality improvement and ecosystem impact; and social indicators include public acceptance and aesthetic value. These indicators were applied consistently across all alternatives to ensure comparability and depth of analysis. This structured indicator-based evaluation ensures that each stormwater management approach is assessed not only conceptually but also based on measurable technical and sustainability parameters.
Data analysis was conducted using the AHP and TOPSIS methods. AHP was used to determine the importance weight of each criterion. This process included constructing a decision hierarchy structure, creating a pairwise comparison matrix, calculating criterion weights, and testing the consistency of assessments. The AHP method is effective in prioritizing criteria in complex decision-making systems (; ). TOPSIS was used to rank alternative strategies based on their proximity to the ideal solution. The TOPSIS method is widely used in evaluating environmental management strategies because it produces objective and easily interpretable results (; ). Research validity was ensured through the use of criteria from Scopus-indexed literature, consultation with experts, and the use of scientifically tested MCDM methods. Reliability is tested through the Consistency Ratio (CR) in the AHP method, with a CR value ≤ 0.1 indicating that the assessment is consistent and acceptable.
4 Research results
4.1 Respondent characteristics within a multi-criteria decision-making (MCDM) framework
This study involved 15 expert respondents selected using purposive sampling based on a minimum of 5 years of professional experience in urban drainage management, water resources, and urban infrastructure planning. Data collection was conducted from January to February 2026 through structured questionnaires and in-person interviews (Supplementary File 1). Respondents came from various institutions directly involved in stormwater management in Jakarta, enabling them to provide a comprehensive assessment within the MCDM framework.
The characteristics of the expert respondents are presented in Table 3. Based on work experience, 11 respondents (73.3%) had more than 8 years of experience, while 4 respondents (26.7%) had between 5 and 8 years of experience. This indicates that respondents possess an adequate level of competence to provide assessments in multi-criteria decision-making processes.
Table 3
| No | Respondent category | Number | Percentage |
|---|---|---|---|
| 1 | Academics in environmental engineering and regional planning | 5 | 33.3% |
| 2 | Environmental engineering practitioners and drainage consultants | 4 | 26.7% |
| 3 | Urban planners | 3 | 20.0% |
| 4 | Local government (Water Resources Agency and Bappeda) | 3 | 20.0% |
| Total | 15 | 100% |
Respondent characteristics.
4.2 Determining criteria weights using AHP
Within the MCDM framework, the AHP method is used to determine the relative weights of four main criteria: environmental, economic, technical, and social.
A pairwise comparison matrix is compiled based on the average of respondents' ratings. The pairwise comparison matrix is presented in Table 4.
Table 4
| Criteria | Environmental | Economic | Technical | Social |
|---|---|---|---|---|
| Environmental | 1.000 | 2.125 | 1.643 | 3.214 |
| Economic | 0.471 | 1.000 | 0.782 | 2.184 |
| Technical | 0.608 | 1.279 | 1.000 | 2.531 |
| Social | 0.311 | 0.458 | 0.395 | 1.000 |
Pairwise comparison matrix of criteria.
Next, normalization and eigenvector calculations were performed to obtain the weights for each criterion. The resulting criteria weights are presented in Table 5.
Table 5
| Criteria | Weight | Percentage | Rank |
|---|---|---|---|
| Environmental | 0.382 | 38.2% | 1 |
| Economic | 0.279 | 27.9% | 2 |
| Technical | 0.214 | 21.4% | 3 |
| Social | 0.125 | 12.5% | 4 |
Criteria weights.
These results indicate that environmental criteria have the highest weighting. This reflects that, in the context of urban stormwater management in Jakarta, the system's ability to reduce runoff, increase infiltration, and support environmental sustainability is a top priority.
4.3 AHP matrix consistency test
A consistency test was conducted to ensure that respondents' assessments in the pairwise comparison matrix had an acceptable level of consistency.
The test results showed:
Consistency Index (CI) = 0.048
Consistency Ratio (CR) = 0.054
Because the CR value is less than 0.10, the comparison matrix is considered consistent and can be used in further analysis.
4.4 Alternative evaluation matrix
Within the MCDM framework, the AHP method is used to determine the relative weights of four main criteria:
A1 = Conventional drainage
A2 = Green infrastructure
A3 = Low Impact Development (LID)
A4 = Nature-based solutions
A5 = Integrated management system
The assessment is carried out using a scale of 1–9 based on four criteria. The evaluation scores for each alternative under the four decision criteria are presented in Table 6.
Table 6
| Alternatives | Environmental | Economic | Technical | Social |
|---|---|---|---|---|
| A1 | 4.35 | 6.42 | 6.75 | 4.68 |
| A2 | 8.47 | 7.18 | 7.82 | 8.05 |
| A3 | 8.16 | 7.03 | 7.54 | 7.76 |
| A4 | 7.74 | 6.85 | 7.12 | 7.43 |
| A5 | 6.95 | 6.58 | 7.26 | 6.89 |
Decision matrix.
The highest score for the environmental criteria was given to green infrastructure, indicating that this strategy is considered the most effective in supporting sustainable rainwater management.
4.5 Normalization matrix and weighted normalization
Normalization was performed using the vector normalization method, then multiplied by the criterion weights obtained from the AHP.
These results indicate that green infrastructure has the highest total value. The normalized and weighted normalized decision matrix is presented in Table 7.
Table 7
| Environmental | Alternatives | Economic | Technical | Social | Total |
|---|---|---|---|---|---|
| A1 | 0.118 | 0.094 | 0.127 | 0.042 | 0.381 |
| A2 | 0.230 | 0.105 | 0.145 | 0.076 | 0.556 |
| A3 | 0.222 | 0.103 | 0.140 | 0.073 | 0.538 |
| A4 | 0.211 | 0.100 | 0.132 | 0.070 | 0.513 |
| A5 | 0.189 | 0.096 | 0.134 | 0.064 | 0.483 |
Weighted normalization matrix.
4.6 Ideal solution and preference value calculation using TOPSIS
Positive and negative ideal solutions are determined based on the maximum and minimum values of the weighted normalization matrix.
Positive ideal solution (A+): (0.230; 0.105; 0.145; 0.076)
Negative ideal solution (A−): (0.118; 0.094; 0.127; 0.042)
Based on the distance calculation to the ideal solution, the following preference values are obtained: The TOPSIS preference values and ranking of the alternative strategies are presented in Table 8.
Table 8
| Alternative | Values Preference | Rankings |
|---|---|---|
| Green infrastructure | 0.918 | 1 |
| Low-impact development | 0.841 | 2 |
| Nature-based solutions | 0.712 | 3 |
| Integrated systems | 0.528 | 4 |
| Conventional drainage | 0.084 | 5 |
Preference values and rankings.
4.7 Sensitivity analysis
To test the robustness of the alternative ranking results, a sensitivity analysis was conducted by varying the weights of the main criteria, particularly the economic and technical criteria, which significantly contribute to decision-making.
Simulations were conducted by increasing the weight of the economic criteria from 21.4 to 30% and the weight of the technical criteria from 27.9 to 35%, with proportional adjustments to the other criteria.
The analysis results show that:
1. GI remains in first place with insignificant changes in preference scores.
2. LID and NbS experienced slight changes in scores, but did not change their ranking positions.
3. Conventional drainage remains the alternative with the lowest score.
These findings indicate that the decision results are relatively stable against changes in criterion weights, thus demonstrating a good level of robustness in the AHP–TOPSIS model.
Therefore, the resulting decisions can be considered reliable in supporting strategic planning for sustainable stormwater management.
5 Discussion
5.1 Priority criteria in stormwater management
The AHP results indicate that environmental criteria have the highest weighting (38.2%), followed by technical (27.9%), economic (21.4%), and social (12.5%). This finding is consistent with the principles of sustainable urban water management, which emphasize ecosystem protection and sustainable runoff management (; ). According to the TBL theory, urban management must consider environmental, social, and economic aspects in a balanced manner (). This research data shows that although economic and social criteria are important, experts consider environmental protection to be the top priority for reducing flood risk and the impacts of climate change in Jakarta.
Consequently, urban planners and policymakers need to prioritize environmental aspects as a primary factor in selecting stormwater management strategies. Infrastructure investments should prioritize green infrastructure solutions, such as infiltration wells, bioswales, and urban vegetation, which can reduce runoff, improve environmental quality, and support city resilience to climate change.
Furthermore, the successful implementation of this strategy also depends on organizational readiness and human resource capacity. Planners, engineers, and infrastructure managers need to be competent in green infrastructure planning and management. Therefore, developing human resource capacity through training and competency enhancement is a crucial factor in supporting sustainable stormwater management.
5.2 Evaluation of alternative strategies: superior green infrastructure
Based on the TOPSIS calculation, GI had the highest preference score (0.918), surpassing LID (0.841) and NbS (0.712). This indicates that GI is closer to the ideal solution based on all criteria.
From the perspective of LID and NbS theory, this strategy effectively manages runoff, increases infiltration, and maintains water quality (; ). GI, such as infiltration gardens, permeable pavements, and green roofs, not only manages stormwater but also provides additional ecosystem benefits, including carbon sequestration, reduction of the urban heat island effect, and enhancement of the city's aesthetic quality.
The practical implications of these findings suggest that local governments need to prioritize the implementation of GI in urban drainage system planning, particularly in areas at high risk of flooding. Integrating GI into drainage master plans can improve the effectiveness of sustainable runoff management and reduce reliance on conventional systems. Furthermore, the MCDM approach used in this study can support more objective decision-making and assist city planners in determining optimal infrastructure investment priorities. GI implementation also provides additional benefits in the form of improved environmental quality and green open spaces. However, successful implementation of this strategy requires adequate human resource capacity, making the competency development of planners, engineers, and infrastructure managers a crucial factor in supporting sustainable stormwater management.
Interview results indicate that experts consistently emphasized the importance of environmental sustainability and system flexibility in the face of climate uncertainty. Key themes that emerged included the need for green infrastructure integration, the limitations of conventional drainage systems, and the importance of human resource capacity in implementation. These findings reinforce the quantitative results of the AHP, which prioritized environmental criteria.
To test the stability of the decision-making results, a sensitivity analysis was conducted by increasing the weighting of economic and technical criteria by 10%−20% each. The results showed that the ranking of alternatives was relatively stable, with Green Infrastructure remaining the best alternative. This indicates that the AHP–TOPSIS model used is robust enough to accommodate changes in criteria weightings, thus increasing the reliability of the results in supporting strategic decision-making.
5.3 Low-impact development and nature-based solutions: approaching the ideal alternative
LID and NbS ranked second and third, respectively, indicating that both strategies are effective alternatives in supporting sustainable stormwater management. This approach emphasizes managing rainwater at its source by increasing infiltration and utilizing natural processes, thereby reducing pressure on conventional drainage systems (). This finding aligns with the concept of urban resilience, which emphasizes the importance of adaptive and multifunctional infrastructure in addressing flood risks and climate change ().
Policy-wise, LID can be integrated into new residential area planning through the implementation of rain gardens and infiltration trenches, while NbS can be applied to public spaces and city parks to increase infiltration capacity and ecological function. However, implementing these strategies requires human resource readiness, particularly in terms of ecosystem-based planning competency, green infrastructure design, and cross-sector coordination. Therefore, strengthening technical and managerial capacity is crucial for successful implementation.
5.4 Limitations of conventional drainage and integrated systems
Conventional drainage had the lowest preference score (0.084), indicating that while this system is relatively stable technically and cost-wise, its contribution to environmental and social aspects is very limited. This finding confirms that a solely concrete channel-based approach is no longer adequate to address the challenges of climate change and the increasing risk of urban flooding. In line with the principles of Integrated Water Resource Management (IWRM), which emphasize the integration of technical, environmental, and social aspects in water resource management [], the integrated system actually offers a more holistic management framework. However, its fourth-place ranking indicates that its implementation in Jakarta still faces obstacles, such as budget constraints, weak inter-agency coordination, and limited land.
Consequently, strengthening the integrated system requires improved strategic coordination between the Water Resources Agency, the Regional Development Planning Agency (Bappeda), and the private sector to ensure that planning and implementation are aligned. Furthermore, investment in an integrated monitoring and maintenance system is crucial to ensure optimal infrastructure performance. Without integrated governance support and adequate organizational capacity, an integrated system may not deliver maximum benefits compared to a green infrastructure-based approach.
5.5 MCDM integration for strategic decision-making
This research demonstrates that the MCDM approach (AHP-TOPSIS) can be used as a systematic, transparent, and evidence-based strategic decision-making framework for evaluating stormwater management alternatives. In line with Decision Support System (DSS) theory, this method assists policymakers in addressing complex decisions by simultaneously considering multiple criteria ().
Practically, MCDM results can be used by local governments to prioritize infrastructure investments more objectively and accountably, and assist planners in balancing cost, technical effectiveness, environmental sustainability, and social acceptability. Furthermore, this model can be replicated in other cities with similar characteristics, potentially serving as a reference framework for sustainable stormwater planning. However, the effectiveness of this approach also depends on organizational capacity and human resource competencies, particularly in analytical skills, strategic planning, and data-driven decision-making. Therefore, human resource capacity development is a crucial factor in supporting its implementation.
This finding is in line with previous research showing that organizational capability and technology readiness are important determinants of successful strategy implementation and organizational performance (). Accordingly, decision-support tools such as AHP–TOPSIS should be accompanied by investments in organizational capability, analytical competencies, and strategic leadership to maximize their effectiveness.
5.6 Human resource and organizational implications
Research results indicate that green infrastructure is the best alternative for urban stormwater management. However, the successful implementation of this strategy depends not only on technical and financial aspects, but also on human resource capacity and organizational readiness.
This finding is consistent with previous studies showing that sustainable outcomes require not only technical interventions but also a structured process of capacity building, competency development, institutional support, and continuous stakeholder engagement (). Therefore, selecting the most appropriate stormwater management strategy should be accompanied by organizational efforts to strengthen human resource capabilities and institutional readiness to ensure successful implementation.
GI implementation requires multidisciplinary competencies, including environmental planning, infrastructure management, and cross-sector coordination. Therefore, public organizations need to develop supportive human resource strategies, such as enhancing technical competencies, sustainability training, and strengthening institutional capacity. The concept of GHRM suggests that integrating green values into HR practices, including green recruitment, environmental training, and environmentally-based performance management, can increase ecological awareness, strengthen employee pro-environmental behavior, and support the achievement of organizational sustainability performance (; ; ). From the Resource-Based View (RBV) perspective, human resources are valuable, rare, and difficult-to-imitate strategic assets, making them a crucial factor in creating competitive advantage and enhancing organizational capacity to effectively manage sustainable infrastructure (). Therefore, integrating infrastructure strategy and human resource development strategy is a key factor in supporting the success of long-term stormwater management and strengthening institutional capacity toward sustainable urban development.
6 Conclusion
Based on the research results using Multi-Criteria Decision-Making (MCDM) with AHP and TOPSIS, it can be concluded that urban stormwater management must emphasize environmental sustainability. Environmental criteria were the top priority (38.2%), emphasizing the importance of strategies that reduce runoff, prevent flooding, and maintain the quality of urban ecosystems. Green Infrastructure (GI) emerged as the best strategy with the highest preference score (0.918), as it was effective across all criteria and provided additional benefits, including green open space, urban aesthetics, and increased climate resilience. Conventional drainage systems proved to have limitations, as they did not support sustainability and climate change adaptation, even though they were technically functional. The MCDM approach proved effective as a systematic, evidence-based strategic decision-making tool. Successful strategy implementation also depends on organizational capacity and human resources, so integrating GHRM and improving technical competency are key to supporting sustainable stormwater management.
7 Recommendation
Based on the research results, practical recommendations for stormwater management in Jakarta:
1. Prioritize GI.
Focus investments on infrastructure, such as infiltration parks, green roofs, and permeable pavements, as they effectively manage water runoff and improve environmental quality and urban aesthetics.
2. Strengthen organizational and human resource capacity
Improve technical competency, environmental planning, and cross-sector coordination through training and the implementation of GHRM.
3. Use MCDM for strategic decision-making
Apply AHP-TOPSIS to systematically, transparently, and evidence-basedly assess alternative strategies.
4. Combine green and ecosystem approaches
Integrate GI with LID and NbS to enhance urban resilience to flooding and climate change.
Statements
Data availability statement
The datasets presented in this study can be found in online repositories. The names of the repository/repositories and accession number(s) can be found in the article/Supplementary material.
Ethics statement
The studies involving humans were approved by Sekolah Tinggi Ilmu Ekonomi Indonesia Jakarta. The studies were conducted in accordance with the local legislation and institutional requirements. The participants provided their written informed consent to participate in this study.
Author contributions
DP: Data curation, Visualization, Investigation, Validation, Methodology, Project administration, Conceptualization, Supervision, Funding acquisition, Software, Resources, Writing – review & editing, Writing – original draft, Formal analysis. SN: Formal analysis, Validation, Data curation, Writing – review & editing, Conceptualization, Software, Methodology. SHari: Investigation, Resources, Writing – review & editing, Formal analysis, Supervision, Conceptualization. SHara: Methodology, Writing – review & editing, Formal analysis, Data curation, Investigation. AS: Writing – review & editing, Conceptualization, Methodology, Formal analysis, Software, Data curation.
Funding
The author(s) declared that financial support was not received for this work and/or its publication.
Conflict of interest
The author(s) declared that this work was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Generative AI statement
The author(s) declared that Generative AI was not used in the creation of this manuscript.
Any alternative text (alt text) provided alongside figures in this article has been generated by Frontiers with the support of artificial intelligence and reasonable efforts have been made to ensure accuracy, including review by the authors wherever possible. If you identify any issues, please contact us.
Publisher’s note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
Supplementary material
The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/frsus.2026.1815426/full#supplementary-material
References
1
AhiablameL. M.EngelB. A. (2012). Effectiveness of low impact development practices : literature review and suggestions for future research. Water Air Soil Pollut.223, 4253–4273. doi: 10.1007/s11270-012-1189-2
2
AlhumaidM.GhummanA. R.HaiderH.BuraydahM.QassimA.ArabiaS. (2018). Sustainability evaluation framework of urban stormwater drainage options for arid environments using hydraulic modeling and multicriteria. Water10:581. doi: 10.3390/w10050581
3
AllisonL.LiuY.MurtinuS.WeiZ. (2023). Gender and firm performance around the world: the roles of finance, technology and labor. J. Bus. Res.154:113322. doi: 10.1016/j.jbusres.2022.113322
4
AlvesA.GersoniusB.SanchezA.VojinovicZ.KapelanZ. (2020). Multi-criteria approach for selection of green and grey infrastructure to reduce flood risk and increase resilience. Front. Environ. Sci.8:563227. doi: 10.1007/s11269-018-1943-3
5
AshleyR. M.GersoniusB.DigmanC.HortonB.SmithB.ShafferP. (2020). Including uncertainty in urban drainage infrastructure planning and design. Urban Water J.17, 147–158. doi: 10.1080/1573062X.2019.1707748
6
BehzadianM.Otaghsara KhanmohammadiS.YazdaniM.IgnatiusJ. (2012). A state-of the-art survey of TOPSIS applications. Expert Syst. Appl.39, 13051–13069. doi: 10.1016/j.eswa.2012.05.056
7
BerlandA.ShiflettS.RuggieroL.GarmestaniA. S. (2017). The role of green infrastructure in urban stormwater management: an interdisciplinary review. Front. Sustain.2:10. doi: 10.3389/frsus.2021.00010
8
CelebriniP.CamposD. O.PazR.CesarC.BritoG.LimaA.et al. (2020). Multi-criteria Decision method for sustainable watercourse management in urban areas. Sustainability12, 1–22. doi: 10.3390/su12166493
9
Cohen-ShachamE.WaltersG.JanzenC.MaginnisS. (2016). Nature-Based Solutions to Address Global Societal Challenges. IUCN. Available online at: https://portals.iucn.org/library/sites/library/files/documents/2016-036.pdf
10
Demirguc-KuntA.AnsarS.KlapperL.SingerD. (2022). The Global Findex Database 2021: Financial Inclusion, Digital Payments, and Resilience in the Age of COVID-19. World Bank. Available online at: http://hdl.handle.net/10986/37578 doi: 10.1596/978-1-4648-1897-4
11
DietzM. E. (2007). Low impact development practices: a review of current research and recommendations for future directions. Water, Air, Soil Pollut.186, 351–363. doi: 10.1007/s11270-007-9484-z
12
EckartK.McpheeZ.BolisettiT. (2017). Science of the total environment performance and implementation of low impact development—a review ?. Sci. Total Environ. 607–608, 413–432. doi: 10.1016/j.scitotenv.2017.06.254
13
EckartK.McPheeZ.BolisettiT. (2018). Multiobjective optimization of low impact development stormwater controls. J. Hydrol.562, 564–576. doi: 10.1016/j.jhydrol.2018.04.068
14
ElkingtonJ. (1997). Cannibals With Forks: The Triple Bottom Line of 21st Century Business. Mankato: Capstone Publishing. doi: 10.1002/tqem.3310080106
15
FletcherT. D.AndrieuH.HamelP. (2013). Understanding, management and modelling of urban hydrology and its consequences for receiving waters: a state of the art. Adv. Water Res.51, 261–279. doi: 10.1016/j.advwatres.2012.09.001
16
FletcherT. D.ShusterW.HuntW. F.AshleyR.ArthurS.TrowsdaleS.et al. (2015). SUDS, LID, BMPs, WSUD and more—the evolution and application of terminology surrounding urban drainage. Urban Water J.12, 525–542. doi: 10.1080/1573062X.2014.916314
17
GajewskaM.UrsinoN.KazakJ. K.ExpositoA.MasiF.ChristianD.et al. (2020). A review of nature-based solutions for urban water management in European circular cities : a critical assessment based on case studies and literature Hasan Volkan Oral a, Pedro Carvalho e, Eric D. van Hullebusch Giulia Cipolletta, Theis Raaschou Ande. Blue-Green Systems2, 112–136. doi: 10.2166/bgs.2020.932
18
Global Water Partnership (GWP)GWP) (2000). Integrated Water Resources Management. Stockholm: GWP Technical Advisory Committee. GWP Technical Advisory Committee.
19
HabitatU. (2020). World Cities Report 2020: The Value of SustainableUrbanization. Nairobi: UN-Habitat.
20
HariniS.PranitasariD.SaidM.EndriE. (2023). Determinants of SME performance: evidence from Indonesia. Probl. Perspect. Manag.21, 471–481. doi: 10.21511/ppm.21(1)0.2023.40
21
HuangY. (2020). Nature-based solutions for urban pluvial flood risk management. Sustain. Cities Soc.61, 1–17. doi: 10.1002/wat2.1421
22
HurlimannA.WilsonE. (2018). Sustainable urban water management under a changing climate : the role of spatial planning. Water10, 1–22. doi: 10.3390/w10050546
23
HwangC. L.YoonK. (1981). Multiple Attribute Decision Making: Methods and Applications, A State-of-the-Art Survey. New York: Springer-Verlag. doi: 10.1007/978-3-642-48318-9
24
IPCC (2022). Climate Change 2022: Impacts, Adaptation and Vulnerability. Available online at: https://iclei.org/news/iclei-affiliated-experts-selected-to-co-author-ipcc-special-report-on-climate-change-and-cities/?gad_source=1andgad_campaignid=11169773747andgbraid=0AAAAACOgMuGgf5n8C4F3XNefkZS5UvZhZandgclid=Cj0KCQiA49XMBhDRARIsAOOKJHaTosi4z3tqen2DSxyLyohMukiyNTI7GAlJ43T1cG-Q6Qu1W9WYa1kaAuR0EALw_wcB (Accessed January 15, 2026).
25
IshizakaA.LabibA. (2011). Review of the main developments in the analytic hierarchy process. Expert Syst. Appl.3, 14336–14345. doi: 10.1016/j.eswa.2011.04.143
26
JoksimovicD.AlamZ. (2014). Cost efficiency of low impact development (LID) stormwater management practices. Procedia Eng.89, 734–741. doi: 10.1016/j.proeng.2014.11.501
27
KaF.ChanS.GriffithsJ.SangY.KomoriD. (2022). Editorial : urban flood resilience and sustainable flood management strategies in megacities. Front. Water3, 2018–2022. doi: 10.3389/frwa.2021.738493
28
KabischN.KornH.StadlerJ.BonnA. (2017a). Nature-Based Solutions to Climate Change Adaptation in Urban Areas. Cham: Springer. doi: 10.1007/978-3-319-56091-5
29
KabischN.KornH.StadlerJ.BonnA. (2017b). “Nature-based solutions to climate change adaptation in urban areas — linkages between science, policy and practice,” in Theory and Practice of Urban Sustainability Transitions (Cham: Springer), 1–11. doi: 10.1007/978-3-319-56091-5_1
30
KahramanC. (2008). Fuzzy Multi-Criteria Decision Making: Theory and Applications with Recent Developments, ed C. Kahraman (Cham: Springer). doi: 10.1007/978-0-387-76813-7_1
31
KannadasanN. T.PolisettyA. (2025). Emerging trends and applications of fuzzy decision-making techniques in financial supply chains: a comprehensive dual-source bibliometric analysis. Cogent Bus. Manag. 12. doi: 10.1080/23311975.2025.2590878
32
KhanM. A.MihardjoL. W.AlamM. M. (2022). The impact of green training on environmental performance: the mediating role of green innovation. Front. Psychol. 13. doi: 10.3389/fpsyg.2022.916723
33
KonstadinosM.PantazisG.DimitraL. C.ChristosM.StefanosN. A.SeddaiuG.et al. (2025). Assessing sustainable water management in a resource-scarce environment (Ghana, West Africa) via the analytic hierarchy process. Agric. Water Manag. 313. doi: 10.1016/j.agwat.2025.109497
34
KullerM.BachP. M.RobertsS.BrowneD.DeleticA. (2019). Science of the total environment a planning-support tool for spatial suitability assessment of green urban stormwater infrastructure. Sci. Total Environ.686, 856–868. doi: 10.1016/j.scitotenv.2019.06.051
35
Li M ul Abidin R. Z Qammar R Qadri S. U Khan M. K Ma Z (2023) Pro-environmental behavior green HRM practices, green psychological climate: Examining the underlying mechanism in Pakistan. Front. Environ. Sci. 11:1067531. 10.3389/fenvs.2023.1067531
36
LiuI.HongboW.WenX.ZhangH.YipY. L.ChenQ.et al. (2026). Green human resource management and shipping firms' environmental performance: the serial mediating effects of seafarers' organizational commitment and green behavior. Front. Mar. Sci. 13. doi: 10.3389/fmars.2026.1858692
37
LocatelliL.GuerreroM.RussoB.MartE.SunyerD.MartM. (2020). Socio-economic assessment of green infrastructure for climate change adaptation in the context of urban drainage planning. Sustainability12:3792. doi: 10.3390/su12093792
38
MeerowS.NewellJ. P. (2019). Urban resilience for whom, what, when, where, and why?Urban Geogr.40, 309–329. doi: 10.1080/02723638.2016.1206395
39
NazariA.RoozbahaniA.Hashemy ShahdanyS. (2023). Integrated SUSTAIN-SWMM-MCDM approach for optimal selection of LID practices in urban stormwater systems. Water Resour. Manag.37, 3769–3793. doi: 10.1007/s11269-023-03526-9
40
PranitasariD.HariniS.NugrohoS. H. (2026). Digitalization and financial inclusion among women-led micro and small enterprises in Indonesia : an empirical perspective. Front. Soc.11, 1–18. doi: 10.3389/fsoc.2026.1813070
41
PranitasariD.SuriwinataS. I. Warcito. (2026). A gender-sensitive sustainable model of digital and financial inclusion for women-led MSMEs in Indonesia. Front. Hum. Dyn. 8. doi: 10.3389/fhumd.2026.1795115
42
RezaeiJ. (2015). Best-worst multi-criteria decision-making method. Omega53, 49–57. doi: 10.1016/j.omega.2014.11.009
43
RydningenU.RoghaniB.NilsenV.AleksanderK.PausH. (2025). Optimization of urban stormwater systems : a multi-criteria approach to sustainable and cost-effective LID implementation Abbas Roozbahani. Water Sci. Technol.91, 654–668. doi: 10.2166/wst.2025.030
44
SaatyT. L. (2008). Decision making with the analytic hierarchy process. Int. J. Serv. Sci.1, 83–98.
45
TeoF. Y.ChowM. F.ChangC. K. (2022). Sustainable urban stormwater management under climate change. Front. Sustain.3:876543. doi: 10.3389/frwa.2023.1304646
46
TriantaphyllouE.SslnchezA. (1997). A sensitivity analysis approach for some deterministic multi-criteria decision-making methods*. Decis. Sci.28, 151–194. doi: 10.1111/j.1540-5915.1997.tb01306.x
47
VelasquezM.HesterP. T. (2013). An analysis of multi-criteria decision-making methods. Int. J. Oper. Res.10, 56–66. Available online at: https://www.researchgate.net/publication/275960103_An_analysis_of_multi-criteria_decision_making_methods
48
YangW.ZhangJ. (2021). Assessing the performance of gray and green strategies for sustainable urban drainage system development: a multi-criteria decision-making analysis. J. Clean. Prod. 293. doi: 10.1016/j.jclepro.2021.126191
49
ZavadskasE. K.GovindanK.AntuchevicieneJ.TurskisZ. (2016). Hybrid multiple criteria decision-making methods: A review. Eng. Appl. Artif. Intell.64, 82–96. doi: 10.1016/j.engappai.2017.06.003
Summary
Keywords
AHP, green infrastructure, MCDM, stormwater, TOPSIS, urban sustainability
Citation
Pranitasari D, Nugroho SH, Harini S, Harahap SS and Sudiarso A (2026) Strategic decision framework and human resource implications for sustainable stormwater management: an AHP–TOPSIS approach. Front. Sustain. 7:1815426. doi: 10.3389/frsus.2026.1815426
Received
22 February 2026
Revised
26 June 2026
Accepted
03 July 2026
Published
24 July 2026
Volume
7 - 2026
Edited by
Abbas Roozbahani, Norwegian University of Life Sciences, Norway
Reviewed by
Umar Muhammad Modibbo, Modibbo Adama University, Nigeria
Shama Parween, Birla Institute of Technology, Mesra, India
Updates
Copyright
© 2026 Pranitasari, Nugroho, Harini, Harahap and Sudiarso.
This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Diah Pranitasari, nitadpranitasari@gmail.com
Disclaimer
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.