Authors | Year | Source title | Cited by | Purpose | Type of activity | Sustainability issues | Theoretical underpinnings | Perspective | Method | Author keywords |
---|---|---|---|---|---|---|---|---|---|---|
Beske P., Land A., Seuring S. | 2014 | 321 | Analyse how sustainable supply chain management tactics aid organizations in controlling their dynamic capabilities. | Link sustainable supply chain management and dynamic capabilities | Strategic management | Resource-based view and the knowledge-based view | Supply chain | Qualitative | Dynamic capabilities; food industry; literature review; sustainable supply chain management | |
Govindan K., Jafarian A., Khodaverdi R., Devika K. | 2014 | 301 | Analyse the effect of supply chain operations on environment, profit and people/society when creating a sustainable supply chain. | Integrate sustainability in decision-making, in the field of distribution in food supply chain management | Sustainable development | NA | Supply chain | Qualitative | Food supply chain; greenhouse gases emissions; perishable foods; robust multi-objective meta-heuristic; sustainability; sustainable supply chain design; two-echelon location-routing problem | |
Pullman M.E., Maloni M.J., Carter C.R. | 2009 | 285 | Analyse in the food industry, how sustainability impacts on environmental and society | Enhance quality performance and related cost performance | Performance management | NA | Manufacturer | Qualitative | Path analysis; social responsibility; supply chain management; survey methods; sustainability | |
Genovese A., Acquaye A.A., Figueroa A., Koh S.C.L. | 2017 | 279 | Integrate environmental issues into organizations' strategies, reducing negative effects of production and consumption processes | Highlight that integration of circular economy within sustainable supply chain management offers benefits from an environmental perspective | Circular economy | Circular economy | Supply network | Qualitative | Circular economy; decision support; environmental sustainability; green supply chain management; product life cycle analysis | |
Walker H., Jones N. | 2012 | 246 | Analyse what factors affect sustainable supply chain management | Explore sustainable supply chain management implemented by organizations leaders in their sector | Sustainable development | NA | Supply chain | Qualitative | Case studies; corporate responsibility; multiple retailers; supply chain management; sustainable development; sustainable supply chains; the United Kingdom | |
Van Der Vorst J.G.A.J., Tromp S.-O., Van Der Zee D.-J. | 2009 | 216 | Analyse food quality change, efficiency and responsiveness needs | Bond food quality and sustainability | Logistic management | NA | Conceptual | Qualitative | Food quality; logistics; simulation; supply chain; sustainability | |
Grimm J.H., Hofstetter J.S., Sarkis J. | 2014 | 182 | Analyse factors that aid to overcome challenges of sub-supplier management | Explore sustainability and critical success factors of sub-supplier management | Strategic management | Critical success factors | Supply chain | Quantitative | Corporate sustainability standards; field study; food industry; sub-supplier management; sustainable supply chain management; theory of critical success factors | |
Notarnicola B., Sala S., Anton A., McLaren S.J., Saouter E., Sonesson U. | 2017 | 171 | Analyse the challenges for life cycle assessment due to the complexity of food systems | Assess and improve food supply chain performance | Circular economy | Life cycle approach | Conceptual | Qualitative | Agri-food products; food lca; food supply chains; food waste; sustainable production and consumption | |
Erol I., Sencer S., Sari R. | 2011 | 169 | Analyse sustainability performance of supply chains | Evaluate and compare company performances in terms of sustainable supply chain. | Performance management | NA | Supplier/farmer | Quantitative | Fuzzy arithmetic; multi-criteria decision-making; performance analysis; sustainable supply chain | |
Georgiadis P., Besiou M. | 2008 | 158 | Analyse the effect of ecological motivation and technological innovations on the long-term behaviour of a closed-loop supply chain with recycling activities | Focus on closed-loop supply chain | Innovation | NA | Conceptual | Qualitative | Closed-loop supply chains; electronic and electrical equipment; recycling; sustainable development; system dynamics |
Applied tools/research methods in the field of FSSCM
Tool/research methods | No. of articles (%) | Type |
---|---|---|
Case study analysis | 46 (26%) | Case studies, multiple case studies, Delphi, focus groups, thematic analysis, etc. |
Statistical analysis | 38 (22%) | Regression analysis, structural equation models, econometric analysis, cluster analysis, analysis of variance (ANOVA/MANOVA), factor analysis, descriptive statistics, etc. |
Conceptual analysis and/or frameworks | 34 (19%) | Sustainability criteria, traceability, etc. |
Mathematical models | 23 (13%) | Algorithms, fuzzy, analytical tool, Decision making trial and evaluation laboratory (DEMATEL) method, simulation, etc. |
Quality tool | 19 (11%) | Integrated quality management system, life cycle approach, transaction cost approach, etc. |
Bibliometric analysis and/or literature review | 16 (9%) | Bibliometric analysis, co-citation analysis, structured and unstructured literature review, etc. |
Ahi , P. and Searcy , C. ( 2013 ), “ A comparative literature analysis of definitions for green and sustainable supply chain management ”, Journal of Cleaner Production , Vol. 52 , pp. 329 - 341 .
Allaoui , H. , Guo , Y. , Choudhary , A. and Bloemhof , J. ( 2018 ), “ Sustainable agro-food supply chain design using two-stage hybrid multi-objective decision-making approach ”, Computers and Operations Research , Vol. 89 , pp. 369 - 384 .
Ashby , A. , Leat , M. and Hudson-Smith , M. ( 2012 ), “ Making connections: a review of supply chain management and sustainability literature ”, Supply Chain Management , Vol. 17 No. 5 , pp. 497 - 516 .
Asian , S. , Hafezalkotob , A. and John , J.J. ( 2019 ), “ Sharing economy in organic food supply chains: a pathway to sustainable development ”, International Journal of Production Economics , Vol. 218 , pp. 322 - 338 .
Beer , S. and Lemmer , C. ( 2011 ), “ A critical review of ‘green’ procurement: life cycle analysis of food products within the supply chain ”, Worldwide Hospitality and Tourism Themes , Vol. 3 No. 3 , pp. 229 - 244 .
Beske , P. , Land , A. and Seuring , S. ( 2014 ), “ Sustainable supply chain management practices and dynamic capabilities in the food industry: a critical analysis of the literature ”, International Journal of Production Economics , Vol. 152 , pp. 131 - 143 .
Bosona , T. and Gebresenbet , G. ( 2013 ), “ Food traceability as an integral part of logistics management in food and agricultural supply chain ”, Food Control , Vol. 33 No. 1 , pp. 32 - 48 .
Brandenburg , M. and Rebs , T. ( 2015 ), “ Sustainable supply chain management: a modeling perspective ”, Annals of Operations Research , Vol. 229 No. 1 , pp. 213 - 252 .
Brandenburg , M. , Govindan , K. , Sarkis , J. and Seuring , S. ( 2014 ), “ Quantitative models for sustainable supply chain management: developments and directions ”, European Journal of Operational Research , Vol. 233 No. 2 , pp. 299 - 312 .
Carter , C.R. and Rogers , D.S. ( 2008 ), “ A framework of sustainable supply chain management: moving toward new theory ”, International Journal of Physical Distribution and Logistics Management , Vol. 38 No. 5 , pp. 360 - 387 .
Chen , Y. , Wang , S. , Yao , J. , Li , Y. and Yang , S. ( 2018 ), “ Socially responsible supplier selection and sustainable supply chain development: a combined approach of total interpretive structural modeling and fuzzy analytic network process ”, Business Strategy and the Environment , Vol. 27 No. 8 , pp. 1708 - 1719 .
Chkanikova , O. ( 2016 ), “ Sustainable purchasing in food retailing: inter-organizational relationship management to green product supply ”, Business Strategy and the Environment , Vol. 25 No. 7 , pp. 478 - 494 .
Corallo , A. , Latino , M.E. , Menegoli , M. and Pontrandolfo , P. ( 2020 ), “ A systematic literature review to explore traceability and lifecycle relationship ”, International Journal of Production Research , Vol. 58 No. 15 , pp. 4789 - 4807 .
Cosimato , S. and Troisi , O. ( 2015 ), “ Green supply chain management: practices and tools for logistics competitiveness and sustainability. The DHL case study ”, The TQM Journal , Vol. 27 No. 2 , pp. 256 - 276 .
Croom , S. , Cox , A. , Chicksand , D. and Yang , T. ( 2007 ), “ The proactive alignment of sourcing with marketing and branding strategies: a food service case ”, Supply Chain Management: An International Journal , Vol. 12 No. 5 , pp. 321 - 333 .
Czinkota , M. , Kaufmann , H.R. and Basile , G. ( 2014 ), “ The relationship between legitimacy, reputation, sustainability and branding for companies and their supply chains ”, Industrial Marketing Management , Vol. 43 No. 1 , pp. 91 - 101 .
Dania , W.A.P. , Xing , K. and Amer , Y. ( 2018 ), “ Collaboration behavioural factors for sustainable agri-food supply chains: a systematic review ”, Journal of Cleaner Production , Vol. 186 , pp. 851 - 864 .
Danny , P.C. and Priscila , B.D.O.C. ( 2004 ), “ Coordinating B2B cross-border supply chains: the case of the organic coffee industry ”, The Journal of Business and Industrial Marketing , Vol. 19 No. 6 , pp. 405 - 414 .
Dora , M. ( 2019 ), “ Collaboration in a circular economy: learning from the farmers to reduce food waste ”, Journal of Enterprise Information Management , Vol. 33 No. 4 , pp. 769 - 789 .
Erol , I. , Sencer , S. and Sari , R. ( 2011 ), “ A new fuzzy multi-criteria framework for measuring sustainability performance of a supply chain ”, Ecological Economics , Vol. 70 No. 6 , pp. 1088 - 1100 .
Fahimnia , B. , Sarkis , J. and Davarzani , H. ( 2015 ), “ Green supply chain management: a review and bibliometric analysis ”, International Journal of Production Economics , Vol. 162 No. c , pp. 101 - 114 .
Feng , Y. , Zhu , Q. and Lai , K.H. ( 2017 ), “ Corporate social responsibility for supply chain management: a literature review and bibliometric analysis ”, Journal of Cleaner Production , Vol. 100 No. 158 , pp. 296 - 307 .
Feng , H. , Wang , X. , Duan , Y. , Zhang , J. and Zhang , X. ( 2020 ), “ Applying blockchain technology to improve agri-food traceability: a review of development methods, benefits and challenges ”, Journal of Cleaner Production , Vol. 260 , 121031 .
Folkerts , H. and Koehorst , H. ( 1998 ), “ Challenges in international food supply chains: vertical co-ordination in the European agribusiness and food industries ”, British Food Journal , Vol. 100 No. 8 , pp. 385 - 388 .
Garcia-Buendia , N. , Moyano-Fuentes , J. , Maqueira-Marín , J.M. and Cobo , M.J. ( 2021 ), “ 22 Years of lean supply chain management: a science mapping-based bibliometric analysis ”, International Journal of Production Research , Vol. 59 No. 6 , pp. 1901 - 1921 .
Ghadge , A. , Kaklamanou , M. , Choudhary , S. and Bourlakis , M. ( 2017 ), “ Implementing environmental practices within the Greek dairy supply chain drivers and barriers for SMEs ”, Industrial Management and Data Systems , Vol. 117 No. 9 , pp. 1995 - 2014 .
Glover , J.L. , Champion , D. , Daniels , K.J. and Dainty , A.J. ( 2014 ), “ An institutional theory perspective on sustainable practices across the dairy supply chain ”, International Journal of Production Economics , Vol. 152 No. C , pp. 102 - 111 .
Govindan , K. ( 2018 ), “ Sustainable consumption and production in the food supply chain: a conceptual framework ”, International Journal of Production Economics , Vol. 195 No. C , pp. 419 - 431 .
Hassini , E. , Surti , C. and Searcy , C. ( 2012 ), “ A literature review and a case study of sustainable supply chains with a focus on metrics ”, International Journal of Production Economics , Vol. 140 No. 1 , pp. 69 - 82 .
Henk , F. and Hans , K. ( 1997 ), “ Challenges in international food supply chains: vertical co-ordination in the European agribusiness and food industries ”, Supply Chain Management: An International Journal , Vol. 2 No. 1 , pp. 11 - 14 .
Ilbery , B. and Maye , D. ( 2005 ), “ Food supply chains and sustainability: evidence from specialist food producers in the Scottish/English borders ”, Land Use Policy , Vol. 22 No. 4 , pp. 331 - 344 .
Joshi , S. , Singh , R.K. and Sharma , M. ( 2020 ), “ Sustainable agri-food supply chain practices: few empirical evidences from a developing economy ”, Global Business Review , Vol. 1 No. 24 .
Juettner , U. , Windler , K. , Podleisek , A. , Gander , M. and Meldau , S. ( 2020 ), “ Implementing supplier management strategies for supply chain sustainability risks in multinational companies ”, The TQM Journal , Vol. 32 No. 5 , pp. 923 - 938 .
Kahi , V.S. , Yousefi , S. , Shabanpour , H. and Saen , R.F. ( 2017 ), “ How to evaluate sustainability of supply chains? A dynamic network DEA approach ”, Industrial Management and Data Systems , Vol. 117 , pp. 1866 - 1889 .
Kamble , S.S. , Gunasekaran , A. and Gawankar , S.A. ( 2020 ), “ Achieving sustainable performance in a data-driven agriculture supply chain: a review for research and applications ”, International Journal of Production Economics , Vol. 219 , pp. 179 - 194 .
Khan , S.A.R. , Yu , Z. , Golpîra , H. , Sharif , A. and Mardani , A. ( 2020 ), “ A state-of-the-art review and meta-analysis on sustainable supply chain management: future research directions ”, Journal of Cleaner Production , Vol. 278 , 123357 .
Khan , S.A. , Mubarik , M.S. , Kusi‐Sarpong , S. , Zaman , S.I. and Kazmi , S.H.A. ( 2021 ), “ Social sustainable supply chains in the food industry: a perspective of an emerging economy ”, Corporate Social Responsibility and Environmental Management , Vol. 28 No. 1 , pp. 404 - 418 .
Kumar , A. , Mangla , S.K. , Kumar , P. and Karamperidis , S. ( 2020 ), “ Challenges in perishable food supply chains for sustainability management: a developing economy perspective ”, Business Strategy and the Environment , Vol. 29 No. 5 , pp. 1809 - 1831 .
Kumar Sharma , Y. , Mangla , S. , Patil , P. and Liu , S. ( 2019 ), “ When challenges impede the process: for circular economy driven sustainability practices in food supply chain ”, Management Decision , Vol. 57 No. 4 , pp. 995 - 1017 .
Kumari , S. , Raghuram , P. , Venkatesh , V.G. and Shi , Y. ( 2021 ), “ Future perspectives on progressive farming with adoption of virtual reality technology for sustainable quality in agriculture ”, The TQM Journal , Vol. ahead-of-print No. ahead-of-print , doi: 10.1108/TQM-06-2021-0191 .
Maditati , D.R. , Munim , Z.H. , Schramm , H.J. and Kummer , S. ( 2018 ), “ A review of green supply chain management: from bibliometric analysis to a conceptual framework and future research directions ”, Resources, Conservation and Recycling , Vol. 139 , pp. 150 - 162 .
Mangla , S.K. , Sharma , Y.K. , Patil , P.P. , Yadav , G. and Xu , J. ( 2019 ), “ Logistics and distribution challenges to managing operations for corporate sustainability: study on leading Indian diary organizations ”, Journal of Cleaner Production , Vol. 238 , 117620 .
Manning , L. ( 2013 ), “ Corporate and consumer social responsibility in the food supply chain ”, British Food Journal , Vol. 115 No. 1 , pp. 9 - 29 .
Manzini , R. , Accorsi , R. , Ayyad , Z. , Bendini , A. , Bortolini , M. , Gamberi , M. , Valli , E. and Toschi , T.G. ( 2014 ), “ Sustainability and quality in the food supply chain. A case study of shipment of edible oils ”, British Food Journal , Vol. 116 No. 12 , pp. 2069 - 2090 .
Massaroni , E. , Cozzolino , A. and Wankowicz , E. ( 2015 ), “ Sustainability in supply chain management-a literature review ”, Sinergie Italian Journal of Management , Vol. 33 , pp. 331 - 355 .
Matopoulos , A. , Barros , A.C. and van der Vorst , J.G.A.J. ( 2015 ), “ Resource-efficient supply chains: a research framework, literature review and research agenda ”, Supply Chain Management: An International Journal , Vol. 20 No. 2 , pp. 218 - 236 .
Morley , A. ( 2020 ), “ Procuring for change: an exploration of the innovation potential of sustainable food procurement ”, Journal of Cleaner Production , Vol. 279 , 123410 .
Naik , G. and Suresh , D.N. ( 2018 ), “ Challenges of creating sustainable agri-retail supply chains ”, IIMB Management Review , Vol. 30 , pp. 270 - 282 .
Pakdeechoho , N. and Sukhotu , V. ( 2018 ), “ Sustainable supply chain collaboration: incentives in emerging economies ”, Journal of Manufacturing Technology Management , Vol. 29 No. 2 , pp. 273 - 294 .
Pohlmann , C.R. , Scavarda , A.J. , Alves , M.B. and Korzenowski , A.L. ( 2020 ), “ The role of the focal company in sustainable development goals: a Brazilian food poultry supply chain case study ”, Journal of Cleaner Production , Vol. 245 , 118798 .
PRB ( 2020 ), “ 2020 world population data sheet. World population data sheet (population reference bureau, July 2020) ”, available at: https://www.prb.org/2020-world-population-datasheet .
Pullman , M.E. , Maloni , M.J. and Carter , C.R. ( 2009 ), “ Food for thought: social versus environmental sustainability practices and performance outcomes ”, Journal of Supply Chain Management , Vol. 45 No. 4 , pp. 38 - 54 .
Raut , R.D. , Luthra , S. , Narkhede , B.E. , Mangla , S.K. , Gardas , B.B. and Priyadarshinee , P. ( 2019 ), “ Examining the performance oriented indicators for implementing green management practices in the Indian agro sector ”, Journal of Cleaner Production , Vol. 215 , pp. 926 - 943 .
Seuring , S. and Muller , M. ( 2008 ), “ From a literature review to a conceptual framework for sustainable supply chain management ”, Journal of Cleaner Production , Vol. 16 No. 15 , pp. 1699 - 1710 .
Sharma , A. , Adhikary , A. and Borah , S.B. ( 2021 ), “ Covid-19's impact on supply chain decisions: strategic insights from NASDAQ 100 firms using Twitter data ”, Journal of Business Research , Vol. 117 , pp. 443 - 449 .
Sharma , R. , Kamble , S.S. , Gunasekaran , A. , Kumar , V. and Kumar , A. ( 2020 ), “ A systematic literature review on machine learning applications for sustainable agriculture supply chain performance ”, Computers and Operations Research , Vol. 119 , 104926 .
Sharma , V.K. , Chandna , P. and Bhardwaj , A. ( 2017 ), “ Green supply chain management related performance indicators in agro industry: a review ”, Journal of Cleaner Production , Vol. 141 , pp. 1194 - 1208 .
Siddh , M.M. , Soni , G. , Jain , R. and Sharma , M.K. ( 2018 ), “ Structural model of perishable food supply chain quality (PFSCQ) to improve sustainable organizational performance ”, Benchmarking: An International Journal , Vol. 25 No. 7 , pp. 2272 - 2317 .
Siddh , M.M. , Soni , G. , Jain , R. , Sharma , M.K. and Yadav , V. ( 2017 ), “ Agri-fresh food supply chain quality (AFSCQ): a literature review ”, Industrial Management and Data Systems , Vol. 117 No. 9 , pp. 2015 - 2044 .
Solér , C. , Bergström , K. and Shanahan , H. ( 2010 ), “ Green supply chains and the missing link between environmental information and practice ”, Business Strategy and the Environment , Vol. 19 No. 1 , pp. 14 - 25 .
Soni , G. and Kodali , R. ( 2011 ), “ A critical analysis of supply chain management content in empirical research ”, Business Process Management Journal , Vol. 17 No. 2 , pp. 238 - 266 .
Suchek , N. , Fernandes , C.I. , Kraus , S. , Filser , M. and Sjögrén , H. ( 2021 ), “ Innovation and the circular economy: a systematic literature review ”, Business Strategy and the Environment , Vol. ahead-of-print No. ahead-of-print , pp. 1 - 17 , doi: 10.1002/bse.2834 .
Taghikhah , F. , Voinov , A. , Shukla , N. , Filatova , T. and Anufriev , M. ( 2020 ), “ Integrated modeling of extended agro-food supply chains: a systems approach ”, European Journal of Operational Research , Vol. 288 No. 3 , pp. 852 - 868 .
Thomé , K.M. , Cappellesso , G. , Ramos , E.L.A. and de Lima Duarte , S.C. ( 2020 ), “ Food supply chains and short food supply chains: coexistence conceptual framework ”, Journal of Cleaner Production , Vol. 278 , 123207 .
Ting , S.L. , Tse , Y.K. , Ho , G.T.S. , Chung , S.H. and Pang , G. ( 2014 ), “ Mining logistics data to assure the quality in a sustainable food supply chain: a case in the red wine industry ”, International Journal of Production Economics , Vol. 152 , pp. 200 - 209 .
Touboulic , A. and Walker , H. ( 2015 ), “ Love me, love me not: a nuanced view on collaboration in sustainable supply chains ”, Journal of Purchasing and Supply Management , Vol. 21 No. 3 , pp. 178 - 191 .
Vodenicharova , M.S. ( 2020 ), “ Supply chain study in food industry in Bulgaria ”, International Journal of Retail and Distribution Management , Vol. 48 No. 9 , pp. 921 - 938 .
Wilhelm , M. , Blome , C. , Wieck , E. and Xiao , C.Y. ( 2016 ), “ Implementing sustainability in multi-tier supply chains: strategies and contingencies in managing sub-suppliers ”, International Journal of Production Economics , Vol. 182 , pp. 196 - 212 .
Winter , M. and Knemeyer , A.M. ( 2013 ), “ Exploring the integration of sustainability and supply chain management: current state and opportunities for future inquiry ”, International Journal of Physical Distribution and Logistics Management , Vol. 43 No. 1 , pp. 18 - 38 .
Xu , S. , Zhang , X. , Feng , L. and Yang , W. ( 2020 ), “ Disruption risks in supply chain management: a literature review based on bibliometric analysis ”, International Journal of Production Research , Vol. 58 No. 11 , pp. 3508 - 3526 .
Yakavenka , V. , Mallidis , I. , Vlachos , D. , Iakovou , E. and Eleni , Z. ( 2020 ), “ Development of a multi-objective model for the design of sustainable supply chains: the case of perishable food products ”, Annals of Operations Research , Vol. 294 No. 1 , pp. 593 - 621 .
Yakovleva , N. , Sarkis , J. and Sloan , T. ( 2012 ), “ Sustainable benchmarking of supply chains: the case of the food industry ”, International Journal of Production Research , Vol. 50 No. 5 , pp. 1297 - 1317 .
Zhong , R. , Xu , X. and Wang , L. ( 2017 ), “ Food supply chain management: systems, implementations, and future research ”, Industrial Management and Data Systems , Vol. 117 No. 9 , pp. 2085 - 2114 .
Zhu , Z. , Chu , F. , Dolgui , A. , Chu , C. , Zhou , W. and Piramuthu , S. ( 2018 ), “ Recent advances and opportunities in sustainable food supply chain: a model-oriented review ”, International Journal of Production Research , Vol. 56 No. 17 , pp. 5700 - 5722 .
Although the views and ideas expressed in this article are those of Maria Palazzo and Agostino Vollero; “sections 1; 3; 3.1; 3.2; 3.6; 3.8; 4” are attributed to Maria Palazzo; while “sections 2; 3.3; 3.4; 3.5; 3.7; 3.9; 5; 6” are attributed to Agostino Vollero.
Related articles, all feedback is valuable.
Please share your general feedback
Contact Customer Support
An empirical framework for assessing the balanced scorecard impact on sustainable development in healthcare performance measurement, exploring organizational sustainability: themes, functional areas, and best practices, motivators of social sustainability in healthcare supply chains in the uae—stakeholder perspective, evaluating organizational performance of public hospitals using the mckinsey 7-s framework, sustainability performance of organization: mediating role of knowledge management, organizational performance and sustainability: exploring the roles of it capabilities and knowledge management capabilities, stakeholder pressure and the adoption of proactive environmental strategies in healthcare: the mediating effect of “green” hrm, how human resource management practices translate into sustainable organizational performance: the mediating role of product, process and knowledge innovation, effects of healthcare quality management activities and sociotechnical systems on internal customer experience and organizational performance, impact of a balanced scorecard as a strategic management system tool to improve sustainable development: measuring the mediation of organizational performance through pls-smart, related papers.
Showing 1 through 3 of 0 Related Papers
An official website of the United States government
The .gov means it’s official. Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.
The site is secure. The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.
Preview improvements coming to the PMC website in October 2024. Learn More or Try it out now .
The various social issues that accompany economic development pose new challenges for leaders to integrate economic benefits, social responsibility, and environmental protection. In this context, various new leadership styles have emerged. Among them, sustainable leadership reveals the key role of leaders in balancing the triple goals of economy, society and environment, and has become an important part of leadership theory research in recent years. We searched the literature related to sustainable leadership in databases such as Web of Science, EBSCO and CNKI. Based on the existing literature, we systematically review the origins, connotations, analytical perspectives, measurement methods, and conceptual comparisons of sustainable leadership. And we also construct an integrated analytical framework of sustainable leadership on the premise of sorting out and summarizing the antecedents and consequences of sustainable leadership. Finally, we provide an outlook on the future research areas of sustainable leadership in order to further promote research of sustainable leadership.
Whether philosophical thinking—“harmonious coexistence between man and nature” or environmental protection in the era of industrial civilization, the concept of sustainable development has always played an important role in guiding global actions ( Piwowar-Sulej et al., 2021 ). In particular, the promulgation of “transforming our world: 2030 agenda for sustainable development” in 2015 has ushered in a new era of global sustainable development. Meanwhile, to strengthen human responsibility for sustainable development, in 2015, 193 ONU member states approved 17 Sustainable Development Goals (SDGs). These goals require countries, organizations and individuals to take action for sustainable development ( Cesário et al., 2022 ). Sustainable development is a highly diverse and dynamic system ( Dos Santos and Ahmad, 2020 ), which is not only aimed at solving the challenges related to climate change and environmental degradation, such as the pollution of air, water and soil, overfishing and species extinction but also related to health, wellbeing and the elimination of inequality and poverty. Due to the close relationship between the organizations and the sustainable development of social economy, some scholars pointed out that this goal can be achieved when enterprises fully accept the challenge of sustainable development, take it as an opportunity for business development, and change their business models ( Tideman et al., 2013 ). At the same time, scholars from different disciplines agree that although enterprises are one of the key perpetrators of these problems, they also play an important role in solving these problems ( Piwowar-Sulej et al., 2021 ). There is no doubt that enterprises have become the basic unit to ensure the implementation of sustainable development. But, for a long time, it has been difficult for enterprises to embed the concept of sustainable development into their own business operations and instead perform their social responsibilities in the form of charitable donations or public welfare activities, resulting in the concept of sustainable development becoming a mere form of social responsibility. However, it should be emphasized that the implementation of these activities of sustainable development is uncertainty. If the enterprise does not have high performance, it is impossible to give better consideration to sustainability ( Suriyankietkaew and Avery, 2016 ). To solve this problem, scholars are actively seeking solutions, and find that introducing the concept of sustainable development into leadership is the key to change the situation and build a sustainable organization ( Gerard et al., 2017 ). Based on this, sustainable leadership, which promotes enterprises to advance toward sustainable development, has attracted increasing attention ( Dalati et al., 2017 ; Piwowar-Sulej et al., 2021 ). Sustainable leadership is the product of the integration of sustainable development and leadership, which is a kind of leadership and management behavior that aims to meet the needs of stakeholders and develop the core business of the enterprise, so as to create long-term value for all stakeholders. It goes beyond the green transformational leadership and responsible leadership, and emphasizes the balanced development of economy, society, and environment. At the same time, it is conducive to helping enterprises achieve profitable growth and sustainability, and has become one of the hotpots of current leadership research ( Avery and Bergsteiner, 2011a , b ).
The existing research on sustainable leadership has made progress, and some scholars have found that sustainable leadership have a positive impact on employees’ organizational commitment, employees’ job satisfaction ( Suriyankietkaew and Avery, 2014 ), employees’ organizational trust ( Dalati et al., 2017 ), organizational sustainable performance ( Burawat, 2019 ; Iqbal et al., 2020a , b ), organizational financial performance ( Kantabutra and Thepha-Aphiraks, 2016 ; Suriyankietkaew and Avery, 2016 ) and organizational resilience ( Avery and Bergsteiner, 2011b ). However, the research of sustainable leadership is still in infancy, and there is a lack of systematic review in this field, which is in sharp contrast to the calls for sustainable leadership. In order to better promote the theoretical research and management practice of sustainable leadership, we searched the literature related to sustainable leadership in databases such as Web of Science, EBSCO and CNKI. We also sort out the existing literature on sustainable leadership, and systematically review, comb and comment on its origin, connotation, analytical perspective, antecedents and outcomes, construct an integrated research framework for sustainable leadership, and prospects for future research.
The origin of sustainable leadership.
The concept of sustainable development into the field of organizational management was introduced by Brundtland committee. They pointed out that sustainable development is a way of development that meets current needs without harming future generations’ needs. Later, this concept has aroused intense discussion in the academic circles and is still under extensive research. For example, Pearce and Turner (1990) put forward the circular economy model, emphasizing the interdependence between economy and environment. Weale (1992) believed that sustainable development challenges the mutually exclusive relationship between economy and environment, which makes the conflict between them conceptualized again. On this basis, Elkington and Rowlands (1999) proposed a triple bottom line framework for sustainable development, indicating that social, environmental (ecological) and financial (economic) indicators are the balance methods to measure enterprise business performance. That is, enterprises should not only pay attention to the profit and loss account, but also consider their own impact on the environment and social responsibility, which means that enterprises need to reduce the negative impact of economic growth to enhance the continuity of development. At the same time, existing studies have shown that the process of seeking sustainable development for enterprises that can carry out sustainable entrepreneurship has also won new opportunities for them ( Kumar and Kiran, 2017 ).
However, with the increasing social and environmental problems arising from economic development, there is a serious imbalance between economic benefits, social responsibility, and environmental protection in the process of enterprise operation. How to overcome this imbalance and achieve the goals of improving performance, resilience and sustainability has become a focus topic of common concern in the practical and theoretical circles. In order to better take into account a wider range of stakeholders, leaders need to establish the concept of sustainable development, embed it into the organization, and implement sustainable leadership behavior as the leader is the key to the enterprise transformation ( Avery, 2005 ). Hargreaves and Fink (2004) and Avery (2005) combined the concept of sustainable development with leadership and put forward the concept of sustainable leadership. Since then, many scholars have explored its connotation based on different context.
Hargreaves and Fink (2004) developed a model of sustainable leadership based on the educational organization, and proposed that sustainable leadership in education refers to the ability to maintain and promote in-depth and extensive learning (depth); make plans and preparations for succession in order to ensure long-term development (sustainability); emphasize dialogue, common development and shared decision-making (breadth); actively share knowledge and resources with neighboring schools or communities to improve the environment (justice); avoid consistency and standardization of policies, curricula, assessments and training to promote diversity (diversity); provide incentive and reward policies to attract talents, and establish a network to enhance mutual learning and support (resourcefulness); respect the past experience of leadership behavior and learn from it in pursuit of creating a better future (maintenance).
With the deepening of theoretical research, Avery (2005) introduced the concept of sustainable leadership into the field of enterprise management for the first time, and proposed a new concept of sustainable leadership based on comparing the differential impact of the two development models of capitalism—the British American model and the Rhine model on the leadership style of organizational managers, and summarized 19 elements. Avery (2005) pointed out that sustainable leadership means having long-term decision-making ability, promoting systematic innovation, cultivating a loyal staff team, and providing high-quality products, services and solutions. Its purpose is to balance the relationship between people, profits and the earth, and promote the sustainability of the enterprise through corresponding management practices. These management practices cover management systems, principles, processes and values, and can form a self-reinforcing leadership system within the organization, involving CEO role change, decentralized decision-making, ethical behavior, high social responsibility and high environmental responsibility. Based on this study, Avery and Bergsteiner (2011a , b) identified four additional practices (self-management, trust, innovation, and job involvement) and integrated them with the initial 19 elements to finally form a sustainable leadership framework including 23 elements. The framework is arranged in the form of a pyramid, reflecting the development concept of mutual support and interdependence. When lower level practices are in place, they will promote and support the emergence of higher-level practices, and higher-level practices in turn rely on the existence of these basic elements.
In general, the 23 practices of sustainable leadership are divided into three levels: basic practice, high-level practice and key performance drivers. Basic practice is at the bottom of the pyramid, including 14 basic practice activities, such as continuously developing every employee within the organization, seeking cooperative labor relations, long-term perspective and a wide range of stakeholder responsibilities; High level practice is at the second level of the pyramid, covering the creation of self-management employees, the use of team strength and knowledge sharing; The key performance drivers are the third layer of the pyramid, including innovation, emotional input and high quality, which essentially improve the customer experience and promote the development of organizational performance. Therefore, at the top of the pyramid is its possible performance results, such as brand and reputation, long-term value to multiple stakeholders, etc.
In the process of the continuous development of the research by scholars such as Hargreaves and Fink (2004) , other scholars followed them but put forward supplementary definitions or new definitions based on different situations ( Lambert, 2012 ; Tideman et al., 2013 ; Gerard et al., 2017 ). Some scholars also focused on the individual characteristics and personal behaviors of sustainable leadership and analyzed its connotation ( Casserley and Critchley, 2010 ). Others explained its concept from a cross-layer perspective ( Armani et al., 2020 ). Based on these scholars’ researches of sustainable leadership, we analyze sustainable leadership from three levels and five perspectives, as shown in Table 1 .
The connotation and analytical perspective of sustainable leadership.
Level | Perspective | Key features | Specific performance |
Individual level | Individual characteristic | Sustainable consciousness and values; How to cultivate sustainable consciousness and values | Moral values and principles, develop people; Action reflection (learning while doing), mental intelligence (clear goals, situational awareness), physical health (stress management, self-care); Environment shapes sustainable leaders |
Organizational level | Organizational culture | Emphasize the importance of leadership to a sustainable organizational culture | Encourage a green, innovative and sustainable organizational culture; Cultivate a strong and widely shared organizational culture; |
Strategic orientation | Emphasize that leadership helps to promote the formation of sustainable development strategies of organizations | Promote leadership → enterprise strategic orientation → sustainable organization/performance Expand the value chain of strategic decision-making to the social environment | |
Human resource development | Human resource development through Sustainable Leadership | Regard employees as one of the stakeholders of the enterprise to cultivate their ability to continuously develop themselves | |
Cross level | Interaction between individual and organization | Emphasize leadership integration and promote the correlation between multiple individual and organizational factors | Integrate personal practices with organizational initiatives Context, awareness, continuity, connection, creativity and collective leadership |
The author collates according to relevant literature.
At the individual level, sustainable leadership mainly relies on the sustainable individual characteristics of leaders to create sustainable organizations. Sustainable leadership from the characteristic perspective refers to the values of sustainable development possessed by leaders and their sustainable consciousness embodied in their work. In organizations, some leaders are more likely to adopt a responsible attitude toward sustainable initiatives and activities, which largely depends on the leader’s personal characteristics ( Waldman and Siegel, 2008 ). For example, Renwick et al. (2013) emphasized the importance of individual characteristics of leaders, such as moral values and principles, in implementing sustainable measures in enterprises. Casserley and Critchley (2010) pointed out that leaders’ attention to their own psychological and physical health needs is a prerequisite to ensure the effectiveness of their sustainable development leadership. On this basis, leaders would create a sustainable organizational environment, establish sustainable organizational goals and play a responsible role to protect the ecological environment. In addition, the level of sustainable development awareness of leaders also plays a key role in helping them cope with the complex economic, social and environmental situations, and make changes when necessary, so as to promote the sustainable innovation of organizations ( Macke and Genari, 2019 ).
At the organizational level, sustainable leadership is understood as a leadership activity that is embedded in the whole organization and forms a self-reinforcing system within the organization through relevant practices, so that enterprises can maintain economic, social and environmental balance in the whole life cycle, while helping organizations achieve long-term sustainable development. The literature on sustainable leadership at the organizational level can be analyzed from three perspectives: organizational culture, strategic orientation and human resource development. First, from the perspective of organizational culture, sustainable leadership is the key promoter of an organizational culture that focuses on innovation and sustainability within an organization ( Avery and Bergsteiner, 2011b ). At the same time, this organizational culture is an important factor in shaping sustainable leadership ( Amar, 2019 ). Therefore, under the relevant interaction and matching of them, the organization’s sustainable development goals can be achieved. For example, some scholars pointed out that senior leaders’ encouragement of a green, innovative and sustainable organizational culture is conducive to enabling employees to have the same environmental and social goals, thus having a positive impact on the sustainable development of the organization ( McCann and Sweet, 2014 ). Focusing on the long term, “doing the right thing”, promoting sustainable shared value creation and innovating sustainable business models are all basic skills and practices of sustainable leadership, which are conducive to improving organizational culture ( Tideman et al., 2013 ). In particular, Avery and Bergsteiner (2011b) clearly put forward that cultivating a strong and shared organizational culture is one of the high-level practices of sustainable leadership, and regarded it as a goal to be pursued in a longer time after anchoring basic elements. Second, from the perspective of strategic orientation. Sustainable leadership can not only consider the complex interrelationship between individuals, business communities, natural environment and market demand, but also expand it to the value chain of enterprises based on strategic decision-making to obtain long-term achievements, while caring about social welfare, and protecting ecosystems ( Burawat, 2019 ). Third, from the perspective of human resource development. Organizations can implement human resource development through sustainable leadership. Sustainable leadership includes all aspects of people-oriented management, regards employees as one of the stakeholders of the enterprise, and then regards it as the responsibility to cultivate a loyal and highly engaged staff team ( Avery and Bergsteiner, 2011b ). Sustainable leaders attach importance to and develop employees, and in return, employees support leaders and can show sustainable behaviors similar to leaders ( Iqbal et al., 2020b ). Therefore, sustainable leadership not only enables employees to develop themselves, but also makes this development sustainable ( Gilley et al., 2011 ). In addition, the encouragement and support of sustainable leadership also helps to promote the growth of human resource developers, making them more patient and caring for employees.
In terms of cross level, sustainable leadership emphasizes that on the basis of understanding the new paradigm of economics and business trends, leaders can integrate their sustainability vision into the development of the organization more easily by combining the organizational perspective with the individual perspective, so as to promote the transformation of the organization to sustainable business, and also contribute to the construction of a sustainable economic system ( Armani et al., 2020 ). Relevant studies can be analyzed from the perspective of interaction between individuals and organizations. The concept of interaction between individual and organization mainly believes that sustainable leadership not only covers the individual characteristics, organizational culture and strategy of leaders, but also has some intersections that can integrate them. For example, Armani et al. (2020) pointed out that interpersonal skills and change direction belongs to the leader’s individual characteristics, focus on stakeholders, seek sustainability in strategic and specific business outlook is related to the organization, and pay attention to sustainability, and coordinated organization culture and moral values and principles in the intersection, can into the personal practice and organizational measures. Tideman et al. (2013) pointed out that sustainable leadership is a kind of leadership behavior generated from the current situation of leaders and organizations under the background of recognizing the disruptive and transformational changes in current business and society. Whether it can promote the sustainable business transformation within the organization depends on the interaction of leadership awareness and situation in time and space.
Comparison between sustainable leadership and similar leadership styles.
The proposal of sustainable leadership provides a way to interpret the concept of sustainable development from the perspective of leadership. In recent years, some scholars have compared sustainable leadership with other similar leadership styles ( Tideman et al., 2013 ). Comparing it with transformational leadership, green transformational leadership, responsible leadership and moral leadership in terms of structural dimension, principle, mode of action and motivation is conducive to a better understanding of the connotation of sustainable leadership (shown in Table 2 ).
The comparison of leadership style.
Leadership type | Construct dimension | Principle | Mode of action | Motivation |
Green transformational leadership | Green personalized care, green intelligence stimulation, green charisma, green Charm | Instill green values and environmental goals into followers and motivate them to exceed the expected level of environmental performance | Rely on leaders’ Environmental Protection examples and the transmission of green values | Enhance the green innovation of the organization, stimulate the green creativity and green behavior of employees, and achieve excess environmental performance |
Moral leadership | People oriented, moral consciousness (moral quality and behavior), the formulation of moral standards and principles, and transparent decision-making style, etc. | Code of ethics | Set an example and moral rewards and punishments for followers through the moral exemplary role of leaders | Formation of employees’ moral behavior |
Responsible leadership | Effectiveness, ethics and sustainability | Normative principles | Democratic consultation and active dialogue with stakeholders | Promote the long-term development of the organization by focusing on social responsibility and business ethics |
Sustainable Leadership | Focus on the situation, show moral courage and high self-awareness, long-term vision, meet the needs of stakeholders, create sustainable shared value, and collective influence | Continuous learning, long-term success, maintaining others, social justice, development, developing environmental diversity and actively participating in environmental protection | Rely on the interaction of leaders’ leadership consciousness and situational consciousness in time and space | Pursue the balance of economic, social and ecological goals while achieving high performance, resilience and sustainability |
The author collated according to relevant literature.
Transformational leaders mainly show four skills or talents: cultivating the internal motivation of their followers (personalized care), being good at taking risks and improving their creativity by stimulating their independent thinking ability (intellectual stimulation), conveying their vision and instilling a sense of purpose and significance (charisma), and setting an example of honesty, reliability and morality for their followers (charm) ( Bass et al., 1987 ). And green transformational leadership is the behavior that can motivate followers to achieve environmental goals and encourage them to exceed the expected level of environmental performance ( Chen and Chang, 2013 ). If a transformational leader happens to have green values and can enhance the green creativity and green behavior of his subordinates through personalized care, intellectual stimulation, vision transmission and charisma, then this transformational leadership behavior is green transformational leadership ( Wang et al., 2018 ). Therefore, the essence of green transformational leadership is still transformational leadership, and its dimensions, principles, modes of action and influence motivation are still consistent with transformational leadership, but green value orientation is added on the basis of the four dimensions of transformational leadership ( Taşçı and Titrek, 2019 ). Although the green transformational leadership brings into the transformational leadership behavior the consideration of environmental issues, the attention to the product life cycle and the social and environmental impact of the whole supply chain, its goal is limited to passing on the values of green environmental protection, promoting green innovation, green environmental protection behavior and green product development. The breadth and depth of its connotation are still lower than that of sustainable leadership.
Ethical leadership means that leaders can not only show ethical behavior within the organization, but also promote followers to form an ethical behavior through decision-making and the process of interaction and communication with followers ( Brown et al., 2005 ). The composition of ethical leadership revolves around ethical norms, involving people-oriented, ethical consciousness (ethical quality and behavior), the formulation of ethical standards and principles, and transparent decision-making style. Its focus is still limited to the binary relationship between leaders and followers, aiming to set an example for followers through the ethical exemplary role of leaders, so as to form an ethical atmosphere within the organization, such as public-private distinction, integrity, kindness and integrity, respect and tolerance, and further affect the behavior of followers. Some scholars also pointed out that ethical leadership can also affect the behavior of followers through moral rewards and punishments. Sustainable leadership also practices ethical principles, but it emphasizes the moral principles centered on the environment and community, which goes beyond the scope of moral leadership. In addition, sustainable leadership means cooperation rather than leading others, so it generally does not affect followers through rewards and punishments ( Brown et al., 2005 ).
Maak and Pless (2006) put forward the concept of responsible leadership in the research of social responsibility integration leadership, which refers to the ability to establish and maintain trust and common collaborative relationships with stakeholders, and pursue common business vision. Some scholars also understand responsible leadership as the behavior of leaders practicing social responsibility. Both sustainable leadership and responsible leadership extend the relationship between leaders and followers to stakeholders inside and outside the organization, and have similarities in paying attention to social responsibility. However, responsible leadership emphasizes that leaders can promote the development of the organization by paying attention to social responsibility and business ethics. The key of sustainable leadership is not only embodied in ethical, social and responsible business behavior, but also rooted in the triple bottom line of economy, society and environment. Its purpose is to create long-term wellbeing and lasting value for all stakeholders, not just social and environmental responsibility. Sustainable leadership seeks to maintain an appropriate balance between economy, society and ecology while achieving high performance, resilience and sustainability ( Burawat, 2019 ), and goes beyond the concept of green and social responsibility in enterprises. Although responsible leadership has expanded its focus from the relationship between leaders and followers to stakeholders, it still takes the current situation of organizations as the starting point ( Tideman et al., 2013 ). In addition, responsible leadership implements democratic consultation with stakeholders, while sustainable leadership transcends its own interests by playing a beneficial role in society, which in turn enables it to achieve performance growth, resilience and sustainability, thus ensuring the balance of economy, society and ecology.
The measurement of sustainable leadership is primarily found in two areas: education and business management. There are many researches within the field of education. In terms of qualitative analysis, based on a comparison of different approaches to sustainable and unsustainable leadership in schools, Hargreaves and Fink (2004) summarized sustainable leadership around sustainable learning, environmental protection, and social justice. Burns et al. (2015) examined sustainable leadership in terms of observation and self-awareness, reflection, exploration of ecological and diversity perspectives, and learning from experience and community. Later, Taşçı and Titrek (2019) delved into sustainable leadership affecting lifelong learning in education, observing and asking questions about organizational vision improvement, social responsibility implementation and ethical standard setting. In terms of quantitative research, Farooq and Ibrahim (2017) developed a 25-item sustainable leadership questionnaire with 4 dimensions (staff capacity building, diversity, maintenance, and strategic leadership allocation) through an exploratory factor analysis of 300 administrative and academic staff questionnaires from 6 universities, sample item: “My university provides training opportunities for staff in leadership development programs.” Çayak (2021) developed a 36-item questionnaire with 4 dimensions (administration, economy, culture, and social sustainability) to measure the level of sustainable leadership of principals, sample item: “My principal tells his teachers about his sustainability practices.” In addition, leadership behaviors that promote sustainability in schools have also been investigated through a combination of qualitative and quantitative methods, such as Lambert (2012) who developed a sustainable leadership framework for colleges of continuing education through interviews and questionnaires to collect data consisting of 6 factors, including developing staff capacity, strategy and partnership building, developing long-term goals from short-term goals, diversifying workplace and curriculum development.
Current research within the field of business management has mainly used quantitative analysis, such as Avery and Bergsteiner (2011a) who designed a set of sustainable leadership questionnaires including 57 measures based on 23 practices of sustainable leadership. Later, Suriyankietkaew and Avery (2014) confirmed the validity of this questionnaire with a sample of 1,152 employees in Thai SMEs. Dalati (2015) developed a 10-item sustainable leadership questionnaire, sample item: “I have a good understanding of leadership.” Lee (2017) measures sustainable leadership in 5 dimensions: cohesive diversity, organizational justice, employee development, advancement orientation and work-life balance, with each dimension measured by 2 questions, sample item: “My supervisor works well with employees from diverse backgrounds.” McCann and Holt (2010) developed and empirically tested a sustainable leadership questionnaire based on sustainable leadership thinking and the ten pillars of sustainable leadership (e.g., social and environmental awareness, adaptability, patience), including 15 questions, sample item: “My leader cares about how sustainability affects employees.” This questionnaire has since been widely used in many studies such as McCann and Sweet (2014) , Al-Zawahreh et al. (2019) , Iqbal et al. (2020b) , and Javed et al. (2020) . Although there are more questionnaires for measuring sustainable leadership, the 15-item questionnaire developed by McCann and Holt (2010) has been more recognized and applied by scholars.
The antecedents of sustainable leadership.
Previous scholars have discussed less on the antecedents of sustainable leadership, and the relevant studies are mainly in two aspects: individual and organizational contextual factors. In terms of individual factors, Taşçı and Titrek (2019) and Armani et al. (2020) pointed out that developing managers’ self-awareness can enhance sustainable leadership, because the development of sustainability relied on the way managers view the world and the importance they placed on certain organizational behaviors that involved ethical issues. Cheng et al. (2021) pointed out that many individual characteristics, such as humility, cognition, and integrity, can positively influence sustainable leadership, but this promotion was more likely to occur in highly ethical organizations. In terms of organizational contextual factors, Shaaban (2020) discussed the concept of responsible leadership and sustainable leadership and empirically tested it with a sample of 250 employees and leaders from 18 companies in Egypt, confirming the facilitative effect of responsible leadership on sustainable leadership.
Although previous scholars have noted that the consequences of sustainable leadership can manifest at the individual, team, organizational, and societal levels, existing empirical analyses have focused primarily on the individual and organizational aspects.
The impact of sustainable leadership on employees is mainly reflected in two aspects: cognition and behavior. On the cognitive side, Suriyankietkaew and Avery (2014) stated that 20 out of 23 practices of sustainable leadership can significantly improve employees’ job satisfaction. Similarly, Lee (2017) identified several sustainable leadership practices as important predictor variables of employee satisfaction, such as work-family balance. Çayak and Çetin (2018) examined the impact of school principals’ sustainable leadership behaviors on teachers’ organizational commitment and job satisfaction and found that sustainable leadership could predict high levels of teachers’ organizational commitment and job satisfaction. Dalati et al. (2017) also examined the influence of sustainable leadership with teachers and found that sustainable leadership can increase the level of trust of employees in the organization. In terms of behavior, Shaaban (2020) argued that sustainable leadership improved employees’ behavior thus making them responsible employees. Moreira et al. (2022) believed that sustainable leadership enables employees to feel that the organization cared about them and valued their competency development, thus reducing their willingness to leave.
At the organizational level, the consequences of sustainable leadership are mainly reflected in performance-related variables, and the relationship of them has received more attention from scholars. For example, Avery and Bergsteiner (2011b) stated that sustainable leadership produced 5 performance-related outcomes, namely reputation, customer satisfaction, finances, shareholder value, and long-term value for multiple stakeholders. They also pointed to the ability of sustainable leadership to improve organizational resilience. An empirical analysis by Suriyankietkaew and Avery (2016) with a sample of Thai SMEs confirmed a significant positive relationship between 16 of the 23 sustainable leadership practices and corporate financial performance. Studies by Lee (2017) , Sezgin-nartgun et al. (2020) also pointed out that sustainable leadership can enhance organizational effectiveness. Recently, empirical analyses by scholars have mainly linked the outcomes of sustainable leadership to organizational sustainability. Burawat (2019) and Iqbal et al. (2020a , b) examined the effects of sustainable leadership in numerous SMEs in different countries, and found that sustainable leadership had a positive impact on sustainable performance. In addition, Fatoki’s (2021) analysis with a sample of hotel companies confirmed the positive relationship between sustainable leadership and sustainable performance. Empirical studies by Javed et al. (2020) and Iqbal et al. (2020a) based on many SMEs in Asian coastal countries had shown that sustainable leadership had a significant positive effect on environmental performance. Moreover, scholars have further explained the mechanism of the effect of sustainable leadership on performance-related consequences through mediating variables and moderating variables. Based on the above research, we develop a research framework for sustainable leadership (shown in Figure 1 ). And the research framework also contains related content in the research prospects.
The analysis framework for sustainable leadership. Solid arrows and “•” represent pathway relationships and variables explored by existing studies, dashed arrows and “°” represent pathway relationships and variables proposed by research outlooks, and (−) indicates negative correlations.
Deepening the conception of sustainable leadership.
Although the number of sustainable leadership research is limited, scholars still differ greatly in their understanding of its connotation, dimensional delineation, and measurement, and have yet to reach a consensus, which has seriously hindered the further development of sustainable leadership. In terms of connotation and dimensional division, most scholars agree that sustainable leadership is multidimensional ( Gerard et al., 2017 ), but there are many overlaps of the dimensional division between sustainable leadership and transformational leadership, ethical leadership, and responsible leadership in existing studies, resulting in numerous questions on sustainable leadership dimensions and measurement questionnaires, which not only affects the theoretical development of sustainable leadership, but also limits the related empirical analysis. Therefore, future research can further clarify the unique structure of sustainable leadership, identify its similarities and differences with other leadership styles, and develop a practical measurement questionnaires based on this.
Future research could explore its potential antecedent variables from a dynamic perspective. The focus of research on sustainable leadership ignores the fact that sustainable leadership behavior may change or fluctuate over time, and thus tapping into its antecedent variables at only one point in time clearly fails to capture changes in sustainable leadership behaviors. Based on existing research, the dynamics of sustainable leadership behavior can be of two kinds, namely, transformation and growth of leadership behavior ( McClean et al., 2019 ). In terms of the study of antecedent variables in the perspective of sustainable leadership transformation, we hypothesize that the main factors that trigger sustainable leadership include experiences, interactions, and conditional triggers. Experiential triggers refer to discrete, work-related experiences of the leader that may cause the leader to face new challenges in the workplace and thus trigger a change in the leader’s behavior; interactive triggers refer to interactive factors that can change the leader’s behavior, such as feedback. Sustainability feedback, social responsibility feedback, etc. may improve sustainable leadership; conditional triggers refer to triggers that are conditional on other factors, such as specific conditional events. In terms of antecedent variables from a sustainable leadership growth perspective, we hypothesize that the triggers for sustainable leadership include experience, relationship building, and traits and orientations. Because sustainable leadership requires leaders to have a broad focus, not only on developing people and teams and improving organizational operations, but also on social wellbeing, socially responsible outputs, and environmental protection, the formation of sustainable leaders is hardly abrupt, but rather evolves over time, with experience leading to higher levels of skills and competencies, and the participatory behaviors of more experienced and established leaders being more effective, making it more likely that the accumulation of experience will shape high-level sustainable leaders over time. In addition, certain traits of leaders, such as self-monitoring, self-efficacy, boldness, commitment, and charisma, may inspire sustainable leadership.
We speculate on the possible weighting factors affecting sustainable leadership formation from the perspectives of structural empowerment theory, resource conservation theory, and institutional theory. First, structural empowerment theory states that power sharing, such as the granting of rights and the delegation of tasks, can enhance individual engagement ( Wang et al., 2022 ). Since sustainable leadership is a rich leadership behavior that requires leaders to balance economic, social, and environmental aspects, it means that leaders need to have a lot of information and resources, and even continuous development opportunities, etc. In a high structural empowerment work environment, leaders are more likely to have access to rich information, support, and resources, thus creating a good working environment for their sustainable leadership behavior. Second, according to resource conservation theory, leaders have limited resources available to them, and the resources they consume to engage in an activity affect their resource investment in other activities. When the workload at work is high, overload reduces the likelihood that leaders will exhibit sustainable leadership behaviors because their need to handle high loads reduces leaders’ perceived progress toward their goals and also causes them to prioritize economic tasks, which leads them to reduce sustainable leadership behaviors. Finally, as open systems, managers’ leadership behaviors are also influenced by external contextual factors. In social contexts, managers’ perceived external normative pressures influence their sustainable leadership behaviors, and in order to gain sustained social support and legitimacy, managers will act to respond to public expectations in a timely manner and position themselves as key contributors to social sustainability, thereby assuming greater social and environmental responsibility. Therefore, future research could also explore the moderating effects that normative pressures play in the formation of sustainable leaders based on institutional theory.
While studies on the mechanisms of sustainable leadership have focused on the organizational level, this paper seeks to suggest possible mediating variables between sustainable leadership and its outcomes at the individual level with the help of relevant theories. Specifically, this paper applies AMO theory, similar attraction theory, and social learning theory to propose corresponding perspectives. First, AMO theory states that employees’ behavior or performance is determined by their abilities, motivation and opportunities, and that leaders’ leadership behaviors can have an impact on employees’ abilities, motivation and opportunities. Based on this, sustainable leadership is used as a starting point to explore the mechanisms underlying the influence of sustainable leadership on employees’ sustainability behaviors, in which AMO factors necessarily play a mediating role. First, the inherent explanatory mechanism centered on competencies. In sustainable activities, employees need to possess certain sustainable competencies, i.e., the mental and cognitive abilities of employees related to effectively engaging in a sustainable activity, including knowledge and skills related to sustainable activities, etc. Sustainable leaders enhance the sustainability of their employees by setting sustainable role models for them in their daily management process, and they also provide the necessary resources to enhance sustainability, such as enhanced coaching and training, and the creation of a positive environment. Second, with motivation as the core explanatory mechanism, internal motivation is the most favorable motivating factor that drives employees to engage in an activity. In sustainable activities, internal motivation that can inspire sustainable behaviors carries the same sustainability, reflecting sustainable behaviors implemented by employees out of their love for sustainable activities. Sustainability leadership uses organizational culture to promote sustainability concepts, values, and goals within the organization to induce internal motivation for sustainability. Third, opportunity-centered explanatory mechanisms, in general, refer to factors in the work environment that can promote individual behavior, such as organizational policies and working conditions. In sustainability activities, the opportunities that can drive employee behavior are primarily sustainability opportunities, i.e., a set of policies, conditions, elements, etc. that are conducive to improving employee sustainability behavior. Sustainable leadership can provide opportunities for employees to implement sustainable behaviors, such as providing relevant training and development opportunities and shaping a sustainable organizational culture.
YL contributed to conducting the literature review, designing the research, collecting some of the data, analyzing the data, drafting the manuscript, meanwhile, repeatedly revised, and refined the content of the manuscript.
This research was supported by the Zhejiang Province Social Science Planning Project “Research on the Mechanism and Implementation Path of High-quality Urban and Rural Integrated Development in Zhejiang Province under the Background of Rural Revitalization” (Project Number. # 22NDJC341YBM).
The author declares that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
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.
You are accessing a machine-readable page. In order to be human-readable, please install an RSS reader.
All articles published by MDPI are made immediately available worldwide under an open access license. No special permission is required to reuse all or part of the article published by MDPI, including figures and tables. For articles published under an open access Creative Common CC BY license, any part of the article may be reused without permission provided that the original article is clearly cited. For more information, please refer to https://www.mdpi.com/openaccess .
Feature papers represent the most advanced research with significant potential for high impact in the field. A Feature Paper should be a substantial original Article that involves several techniques or approaches, provides an outlook for future research directions and describes possible research applications.
Feature papers are submitted upon individual invitation or recommendation by the scientific editors and must receive positive feedback from the reviewers.
Editor’s Choice articles are based on recommendations by the scientific editors of MDPI journals from around the world. Editors select a small number of articles recently published in the journal that they believe will be particularly interesting to readers, or important in the respective research area. The aim is to provide a snapshot of some of the most exciting work published in the various research areas of the journal.
Original Submission Date Received: .
Find support for a specific problem in the support section of our website.
Please let us know what you think of our products and services.
Visit our dedicated information section to learn more about MDPI.
Environmental considerations and sustainable solutions for outdoor advertising banners.
2. advantages, disadvantages, and environmental impact of banners, 2.1. overview of the outdoor advertising industry, 2.2. flex banners and the environmental impact, 3. models and strategies for extending banner lifespan and promoting the circular economy, 3.1. rethink, reduce, 3.2. upcycling, reuse, repurpose, 3.3. remanufacturing, 4. case study—transforming a banner into a raincoat, 5. discussion.
Author contributions, institutional review board statement, informed consent statement, data availability statement, conflicts of interest.
Click here to enlarge figure
The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content. |
Cuc, S.; Secan, C. Environmental Considerations and Sustainable Solutions for Outdoor Advertising Banners. Sustainability 2024 , 16 , 5366. https://doi.org/10.3390/su16135366
Cuc S, Secan C. Environmental Considerations and Sustainable Solutions for Outdoor Advertising Banners. Sustainability . 2024; 16(13):5366. https://doi.org/10.3390/su16135366
Cuc, Sunhilde, and Cristina Secan. 2024. "Environmental Considerations and Sustainable Solutions for Outdoor Advertising Banners" Sustainability 16, no. 13: 5366. https://doi.org/10.3390/su16135366
Article access statistics, further information, mdpi initiatives, follow mdpi.
Subscribe to receive issue release notifications and newsletters from MDPI journals
BMC Oral Health volume 24 , Article number: 751 ( 2024 ) Cite this article
Metrics details
Early childhood caries (ECC) is a multifactorial disease in which environmental factors could play a role. The purpose of this scoping review was to map the published literature that assessed the association between the Sustainable Development Goal (SDG) 11, which tried to make cities and human settlements safe, inclusive, resilient and sustainable, and ECC.
This scoping review followed the Preferred Reporting Items for Systematic Reviews and Meta-Analyses Extension for Scoping Reviews (PRISMA-ScR) guidelines. In July 2023, a search was conducted in PubMed, Web of Science, and Scopus using tailored search terms related to housing, urbanization, waste management practices, and ECC. Studies that solely examined ECC prevalence without reference to SDG11 goals were excluded. Of those that met the inclusion criteria, a summary highlighting the countries and regions where the studies were conducted, the study designs employed, and the findings were done. In addition, the studies were also linked to relevant SDG11 targets.
Ten studies met the inclusion criteria with none from the African Region. Six studies assessed the association between housing and ECC, with findings suggesting that children whose parents owned a house had lower ECC prevalence and severity. Other house related parameters explored were size, number of rooms, cost and building materials used. The only study on the relationship between the prevalence of ECC and waste management modalities at the household showed no statistically significant association. Five studies identified a relationship between urbanization and ECC (urbanization, size, and remoteness of the residential) with results suggesting that there was no significant link between ECC and urbanization in high-income countries contrary to observations in low and middle-income countries. No study assessed the relationship between living in slums, natural disasters and ECC. We identified links between ECC and SDG11.1 and SDG 11.3. The analysis of the findings suggests a plausible link between ECC and SDG11C (Supporting least developed countries to build resilient buildings).
There are few studies identifying links between ECC and SDG11, with the findings suggesting the possible differences in the impact of urbanization on ECC by country income-level and home ownership as a protective factor from ECC. Further research is needed to explore measures of sustainable cities and their links with ECC within the context of the SDG11.
Peer Review reports
By 2018, more than half of the global population resided in urban areas, indicating a significant trend towards urbanization [ 1 ]. Projections suggest that this number will further escalate to 6.5 billion by the year 2050 [ 1 ]. The rise in urbanization is accompanied by an increase in the number of mega-cities. Nine out of ten mega-cities will be in developing countries and about 90% of urban expansion is expected to occur in these nations [ 1 ]. Within mega-cities, there are disparities in socio-economic status, with pockets of poverty and deprivation alongside affluent areas often resulting from the growth of urban slums [ 2 ]. Presently, the slum population stands at 828 million individuals and is continuously growing [ 3 ]. This problem is more pronounced in some countries in Africa like Nigeria, where three out of every five people residing in urban regions reside in slums [ 4 ].
These statistics are significant as they highlight the increased risk factor for early childhood caries (ECC) in urban areas. Populations residing in urban slums have challenges accessing adequate oral health services due to structural factors limited availability of dental clinics, shortage of oral health professionals, and long waiting times to access oral health care [ 5 ]. In addition, children may individually deal with issues that increase their difficulties accessing nutritious foods, quality oral care products, and regular dental check-ups, all of which further contributes to their high vulnerability to ECC [ 6 , 7 ]. These factors impede timely preventive and treatment interventions for ECC [ 5 ]. On the other hand, children residing in cities may also have a high prevalence of ECC for different reasons [ 8 ]. In the cities, there is ready access to unhealthy food options and unhealthy lifestyles, which may contribute to the adoption of unhealthy dietary behaviours such as inadequate fruit and vegetable consumption and increased energy intake [ 9 , 10 , 11 , 12 ]. For children living in cities and urban slums, the urban environment can increase their exposure to air pollution, which may also contribute to ECC [ 13 ]. Therefore, there is a complex interplay of urban-related behavioural, social, economic, and environmental factors that may constitute significant risk factors to the occurrence and progression of ECC.
ECC is defined by any cavitated or non-cavitated lesions in primary teeth in the mouths of children < 72 months of age [ 14 ]. The multifaceted risk factors prevalent in urban environments heighten children’s susceptibility to ECC, primarily due to high sugar consumption and exposure to cariogenic diets. Therefore, urban planning must consider the potential impact on children’s oral health, as poor oral health and ECC can impede the achievement of Sustainable Development Goal (SDG) 3. Previous research suggests a correlation between SDG 3 and SDG 11 [ 15 ] and a correlation between ECC and SDG 3 [ 16 ]. The connection between oral health and SDG 11 remains unclear there is currently no clear evidence on the links between oral health and the SDG 11 [ 17 ].
Achieving the SDG 11 may contribute to controlling ECC. The 10 targets of the SDG 11 are focused on improving the quality of life in urban areas, making cities more accessible, safer, and sustainable while mitigating environmental impacts like disasters, ensuring air quality, and waste management. This involves upgrading slums, ensuring basic services and safe transport systems, and creating safe, inclusive, green public spaces. Targets addressing children focus on safe, affordable transport systems and accessible public spaces, benefiting vulnerable groups (SDG 11.2; SDG11.7) [ 18 ]. Sustainable cities may also address concerns like air pollution and access to safe waste collection, which is linked with ECC [ 19 , 20 ], and access to safe waste collection systems, urban green spaces and housing that are also linked to oral health [ 21 , 22 , 23 , 24 ].
The concept of a smart sustainable city is relatively new with numerous methods and indicators to assess whether the city is smart or sustainable. Its conceptualisation is, however, devoid of health as an indicator though the dimensions and components all contribute to healthy living and wellbeing [ 25 ], and possibly oral health. The purpose of this scoping review was to map the evidence in the literature on the association between ECC and targets of the SDG11.
We conducted a systematic search to identify literature on the link between sustainable cities and communities and ECC. Our Scoping Review was done in accordance with the Preferred Reporting Items for Systematic Reviews and Meta-Analyses Extension for Scoping Reviews guidelines (PRISMA-ScR) [ 26 ].
This review was guided by the question: What is the existing evidence on the association between the SDG11 targets (housing, urbanization, waste management practices, natural disasters) and ECC (prevalence and severity)?
The electronic data searched were PubMed, Web of Science and Scopus, in July 2023. The search terms used are accessible in Appendix 1.
Literature obtained through database searches was exported to the reference management software Endnote version 20.6 (Clarivate ™ ). Duplicate articles were removed. Title and abstract screening were done independently by two researchers (EMRBC and MOF) using pre-defined inclusion and exclusion eligibility criteria. Full-text reviews of the remaining publications were then done independently by three researchers (EMRBC, CAF and MOF) and reference lists of potentially relevant publications were manually searched. Uncertainty regarding whether publications met the inclusion criteria was resolved through discussion among the three researchers. No authors or institutions were contacted to identify additional sources.
All epidemiological studies with information on the association between housing, natural disaster, urbanization, and community related factors, and ECC were included. Studies were limited to those that recruited children less than 72 months in keeping with the established case definition for ECC. Publications that included children older than 71 months were included if the findings were appropriately disaggregated by age and enabled the extraction of information and data on children less than 72 months. Publications also had to be peer review articles.
We excluded studies that did not report ECC as an outcome and those that made no reference to the targets of SDG 11. We also excluded reviews, editorials, case reports and ecological studies. In addition, there were no language restrictions for the search conducted in the databases.
The data extraction process involved gathering specific information from the included publications, such as the first author’s name, publication year, study location, World Health Organization’s (WHO) region where the study was conducted, sample size, age range of the children, study design, and main findings. All relevant information from each publication was compiled and summarized in Table 1 to facilitate a comprehensive analysis. The summarized data was then shared with four experts (MET, BG, JIV and RJS) for their review. Publications were retained only when there was a consensus between the experts and the earlier three reviewers. The final consensus document was also shared with members of the Early Childhood Caries Advocacy Group ( www.eccag.org ) for validation.
We performed a descriptive analysis of the publications included in the review, which involved providing detailed information about various aspects of the studies. These descriptions encompassed the countries where the studies were conducted, study design, journal (whether dental or non-dental), prevalence of ECC, and findings regarding the associations between ECC and the indicators of SDG11, which included housing profiles, urbanization, and the impacts of natural disasters. The countries where the studies took place were classified as the Americas region (AMR), Eastern Mediterranean Region (EMR), African region (AFR), European region (EUR), South East Asian region (SEAR), and the Western Pacific region (WPR).
The scoping review was funded by out-of-pocket expenses. This had no role to play in the study design, data collection and analysis, decision to publish, or preparation of the manuscript.
The initial search across three databases yielded 87 potentially relevant publications. After removing duplicates, 65 articles were assessed to determine whether they met the inclusion criteria. Ultimately, only 10 studies were deemed suitable for this scoping review [ 27 , 28 , 29 , 30 , 31 , 32 , 33 , 34 , 35 , 36 ]. The study selection process is depicted in Fig. 1 .
Flow diagram based on the Preferred Reporting Items for Systematic Reviews and Meta-Analyses 2020 flowchart template of the search and selected process
Table 1 shows that the selected studies were conducted between 1976 and 2020, with only one study conducted before 2000 [ 27 ]. Among the 10 studies, five (50.0%) were cross-sectional in design [ 27 , 28 , 30 , 31 , 35 ], four (40.0%) were cohort studies [ 29 , 32 , 33 , 34 ], and one (10.0%) was a case-control study [ 36 ]. In addition, seven of the 10 studies (70.0%) were published in dental journals [ 27 , 28 , 29 , 30 , 31 , 35 , 36 ], while three (30.0%) were published in non-dental journals [ 33 , 34 , 35 ].
These studies were distributed across the five of the six World Health Organization regions. Three studies (30.0%) were from EUR, with one each from Denmark [ 27 ], Greece [ 30 ], and Italy [ 32 ]. There were two studies (20.0%) from WPR, with one from Australia [ 29 ], and one from South Korea [ 31 ]; and two studies (20.0%) were from the AMR, with one from the USA [ 33 ] and one from Brazil [ 35 ]. Additionally, there was one study (10.0%) from the EMR - Iran [ 36 ], and one study (10.0%) from SEAR - Taiwan [ 28 ], and no study from AFR.
The study populations consisted of children aged between 4 months to 2 years [ 28 , 29 , 31 , 32 , 34 ] and children aged 3 years to 6 years [ 28 , 29 , 30 , 31 , 33 , 34 , 35 , 36 ]. Only One study included children older than 71 months in their sample [ 36 ]. Furthermore, two studies had a sample size of less than 350, with one being a cohort study with 50 participants [ 33 ] and the other a cross-sectional study with 122 children [ 27 ].
Six studies identified an association between housing and ECC [ 30 , 31 , 32 , 34 , 35 , 36 ] with a study finding suggesting that children whose parents owned a house had lower ECC prevalence [ 36 ] and lower ECC severity [ 30 ]. However, variables such as living in small apartments [ 31 ], low-cost apartments [ 32 ], and non-masonry houses [ 34 ] were associated with higher ECC prevalence. However, one study found no association between living in masonry houses and ECC prevalence [ 35 ] and another showed that children who lived in larger houses had higher ECC severity [ 30 ]. There was no difference in ECC prevalence based on the number of rooms in the house [ 35 ].
Furthermore, five studies identified a relationship between urbanization and ECC [ 27 , 28 , 29 , 33 , 35 ]. One study found no difference in ECC severity based on the size of the residential area [ 27 ], while another showed that children living in smaller municipalities had a higher prevalence of ECC [ 35 ]. Two studies indicated that the remoteness of the residential area was not associated with a higher prevalence of ECC [ 29 , 33 ], while a study showed that children living in low urbanized areas had a higher prevalence of ECC [ 28 ].
In addition, among the studies we reviewed, one study investigated the relationship between the prevalence of ECC and waste management practices [ 35 ]. The study revealed that there was no significant difference in the prevalence of ECC based on the way waste was managed at the household level, whether it was burned/buried, collected, or left uncollected.
The findings on the links between urbanization and ECC were the most diverse. This variation appears to be associated with the income level of the countries where the research was conducted. Studies from high-income countries did not show a significant link between ECC and urbanization [ 27 , 29 , 33 ]. Conversely, the study from low and middle-income countries indicated that ECC prevalence was higher in low urbanized areas [ 28 ]. Based on this analysis, a connection between ECC and SDG11.C is suggested.
There was no study that assessed the relationship between living in slums and ECC, and the relationship between natural disasters such as floods, earthquakes, or hurricanes and ECC.
Figure 2 illustrates our conceptual framework depicting the connection between ECC and SDG11. We identified associations between ECC and SDG11.1 [ 30 , 31 , 32 , 34 , 35 , 36 ]. The studies that explored the association between SDG11.3 and ECC [ 27 , 28 , 29 , 33 , 36 ] suggest that that the influence of SDG11 on ECC risk could vary based on the income levels of different countries. In lower income countries, urbanization may elevate the risk of ECC, whereas in higher income countries, urbanization might not be linked to the risk of ECC. This finding strengthens the argument of a plausible association between ECC and SDG11.C (which pertains to supporting least developed countries in constructing sustainable and resilient buildings utilizing local materials).
The single study linking SDG 11.6 and ECC [ 35 ] found no association between waste management methods and ECC. In addition, we found no study establishing a link between ECC and SDG11.2 (urban transportation access for children), SDG 11.7 (access to safe, inclusive, and accessible, green, and public spaces), SDG11.8 (strengthening national and regional development planning), and SDG11.9 (climate change and disaster management). We did not explore the links between ECC and SDG11.4 (protect and safeguard the world’s cultural and natural heritage) due to the low likelihood of a connection between the two; nor did we explore the link between ECC and SDG 11.5 (economic losses relative to global gross domestic product caused by disasters) because this had been investigated when we explored the link between ECC and SDG8 (decent work and economic growth).
A conceptual framework on the link between ECC and SDG 11
The purple box shows the SDG targets statistically associated with ECC in the current study
11 − 1 safe and affordable housing
11 − 2 affordable and sustainable transport systems
11 − 3 inclusive and sustainable urbanization
11 − 4 protect the world’s cultural and natural heritage
11 − 5 reduce the adverse effects of natural disasters
11 − 6 reduce the environmental impact of cities
11 − 7 provide access to safe and inclusive green and public spaces
11-A strong national and regional development planning
11-B implement polices for inclusion, resource efficiency and disaster risk reduction
11-C support least developed countries in sustainable and resilient building
https://knowsdgs.jrc.ec.europa.eu/sdg/11
This scoping review was performed to map the existing literature on the links between ECC and SDG11. The study findings revealed that there was a limited number of studies investigating the link between ECC and SDG11. Most of these studies were cross-sectional in design, and the results indicated that owning a house was associated with lower risk of having ECC and lower ECC severity. However, it became evident that other housing-related factors such as apartment size, the number of rooms, and construction materials used may also play a role. The relationship between ECC and urbanization was less distinct, although diverse observations seemed to vary based on the income level of the countries under study. Notably, there were no studies from the African Region. Household waste management did not show a significant association with the prevalence of ECC. This scoping review found studies linking ECC and three SDG 11 targets. There were no accessible studies linking ECC and the other seven SDG 11 targets though there was the plausibility of a link between one of these based on the review of the literature.
The results suggest that having adequate, safe, and affordable housing is associated with lower ECC prevalence and severity. Upgrading slums may also have a positive impact on the risk of ECC, as studies among older children and adolescents have already indicated that living in slums increases the risk for caries [ 24 , 37 , 38 ]. The connections between ECC, housing, and living in urban/rural/remote areas may be related to socioeconomic status, as higher socioeconomic status is associated with improved housing [ 39 ], better nutrition and diet [ 40 , 41 ] and better health [ 42 ]. This suggests that the relationship between housing, urbanization and ECC is not causal but rather, housing and urbanization are markers of better socioeconomic status, which is causally linked to ECC risk [ 43 , 44 , 45 ]. It is also possible that housing is a marker of better public policies in a neighbourhood, community, or country, and may explain in part, the connection between the SDG 11 and ECC. However, there might be other pathways through which housing and urbanization are linked to the risk and severity of ECC and this needs to be explored by further studies, including doing the difficult task of measuring the direct impact of public policies on oral health.
Some ecological studies have also provided insight into the possible complexity in assessing the links between ECC and SDG11. One of such studies indicated an inverse relationship between urbanization and ECC among European Union member countries [ 46 ]. A study conducted on Serbia, one of the European member countries, further corroborated this finding by indicating that residence in parts of a country with lower social and health care expenditures per capita, lower population density, lower local self-government budget and a higher unemployment rate – a profile that may be synonymous with living in a rural or remote area - may increase the risk for both ECC and untreated ECC [ 47 ]. It is also possible that urbanization may be linked to higher maternal education, higher income, greater access to information; or it may be a proxy for prompt access to oral health services [ 48 ]. The converse may be observed in low middle income countries where a possible pathway linking SDG11 and ECC may be infant feeding practices. Infant feeding practices differ between the urban and rural areas, with infant feeding practices better in the rural area [ 49 ]. Urbanization may negatively affect breast feeding practices [ 50 ]. These suggest there may be a complex interplay of factors that influence the risk of ECC that housing and urbanization may either moderate or mediate.
In addition, natural disasters may also be linked to the risk of ECC, as they can cause damage to houses including dental facilities and infrastructure such as water and electricity [ 51 ]. This increases the risk of poor access to urgently needed preventive dental care and promotes the consumption of cheap foods with high sugar contents, as well as the deterioration of self-care [ 52 ]. Previous studies have suggested a causal relationship between economic deterioration and housing damage resulting from natural disasters [ 51 ], a decrease in oral health quality of life [ 53 ], and the connection between oral disease and insomnia resulting from natural disasters [ 54 ]. There were, however, no studies on the link between ECC and natural disasters despite this plausibility. Future disaster management studies should explore the possibilities of this link.
Encouraging further research on the link between ECC and the SDG11 targets, along with exploring plausible connections with other SDG11 targets yet to be studied, holds significant potential for effectively addressing the current high global burden of ECC. Particular attention must be given to the African Region, which currently experiences a substantial burden of untreated ECC [ 55 ], high susceptibility to urban migration and the proliferation of slums [ 56 ]. Within Africa, attention should be paid to regions in Africa with the highest rate of urban-slum dwellers in the world [ 57 ]. The rapid growth of the urban population in Africa, driven by rural-urban migration, is accompanied by poor waste management in these slums [ 58 ]. These studies should take into consideration the use of appropriate methodologies including adjustment for socioeconomic status which may diminish the association between the prevalence of caries and urban residency with no impact on the association between caries and semi-urban residency [ 59 ]. Therefore, studies exploring the links between ECC and SDG11 may require differentiation between urban, semi-urban, rural, and slum residency. Likewise, access to fluoridated water can attenuate the impact of risk factors on ECC and therefore may also change the relationship between urbanization and ECC [ 60 ]. The studies on ECC should profile the risk factors for children 0-2-years old differently from those 3–5 years old [ 61 ].
The study had a few limitations. We limited our data extraction to only three databases. As a result, some relevant publications might have been unintentionally excluded. In addition, the scope of our study was restricted to children under six years old, limiting the applicability of our findings to other age cohorts. Despite these limitations, the study underscores plausible connections between ECC and the SDG 11 that warrant empirical exploration in future research especially in Africa.
In conclusion, the findings of this scoping review from the few included studies show there is potential for connections between ECC and SDG11. Firstly, the relationship between housing and the prevalence and severity of ECC indicates a potential mediating role of socioeconomic status. Secondly, studies examining the links between urbanization and ECC were inconclusive, yet hint at possible variations based on country income levels. Thirdly, there were no studies exploring the connections between ECC, living in slums, and natural disasters. Finally, the sole study on waste management practices found no significant association with ECC prevalence. Additionally, the studies were limited to investigating only three of the 10 SDG11 targets. Further research is warranted not only to explore the correlations between ECC and all aspects of SDG11 but also to assess the mediating pathways underlying these connections.
The datasets used and/or analysed for the study are publicly accessible. Data used are summarised in the publication.
Early Childhood Caries
Preferred Reporting Items for Systematic Reviews and Meta-Analyses Extension for Scoping Reviews guidelines
Sustainable Development Goal
Americas region
Eastern Mediterranean Region
African region
European region
South East Asian region
Western Pacific region
UNDP. What are the sustainable development goals. https://www.undp.org/sustainable-development-goals/sustainable-cities-and-communities?gclid=CjwKCAjw44mlBhAQEiwAqP3eVn67PLvKFZE0cWSwcIxlcNFM3xb6erZVL1YDnMPAMf_nY-fEChv_3xoCuBkQAvD_BwE . Accessed 4 Aug 2023.
Fotso JC. Child health inequities in developing countries: differences across urban and rural areas. Int J Equity Health. 2006;5:9. https://doi.org/10.1186/1475-9276-5-9 .
Article PubMed PubMed Central Google Scholar
WHO, UNHabitat. Hidden cities: unmasking and overcoming health inequities in urban settings. Nairobi, Kenya: UN Habitat and World Health Organisation; 2013.
Google Scholar
Obembe TA, Levin J, Fonn S. Prevalence and factors associated with catastrophic health expenditure among slum and non-slum dwellers undergoing emergency surgery in a metropolitan area of South Western Nigeria. PLoS ONE. 2021;16(8):e0255354. https://doi.org/10.1371/journal.pone.0255354 .
Article CAS PubMed PubMed Central Google Scholar
Northridge ME, Kumar A, Kaur R. Disparities in Access to oral Health Care. Annu Rev Public Health. 2020;41:513–35. https://doi.org/10.1146/annurev-publhealth-040119-094318 .
Vilar-Compte M, Burrola-Méndez S, Lozano-Marrufo A, et al. Urban poverty and nutrition challenges associated with accessibility to a healthy diet: a global systematic literature review. Int J Equity Health. 2021;20:40. https://doi.org/10.1186/s12939-020-01330-0 .
Onyejaka NK, Folayan MO, Folaranmi N. Barriers and facilitators of dental service utilization by children aged 8 to 11 years in Enugu State, Nigeria. BMC Health Serv Res. 2016;16:93. https://doi.org/10.1186/s12913-016-1341-6 .
Maserejian NN, Tavares MA, Hayes C, Soncini JA, Trachtenberg FL. Rural and urban disparities in caries prevalence in children with unmet dental needs: the New England Children’s Amalgam Trial. J Public Health Dent 2008 Winter;68(1):7–13. https://doi.org/10.1111/j.1752-7325.2007.00057.x .
Gesteiro E, García-Carro A, Aparicio-Ugarriza R, González-Gross M. Eating out of home: influence on Nutrition, Health, and policies: a scoping review. Nutrients. 2022;14(6):1265. https://doi.org/10.3390/nu14061265 .
Juma K, Juma P, Shumba C, Otieno P, Asiki G. Non-communicable diseases and Urbanization in African cities: a narrative review. In: Anugwom EE, Awofeso N, editors. Public Health in developing countries: challenges and opportunities. London, UK: IntechOpen; 2019.
Owino VO. Challenges and opportunities to tackle the rising prevalence of diet-related non-communicable diseases in Africa. Proc Nutr Soc. 2019;78:506–12. https://doi.org/10.1017/S0029665118002823 .
Finlay A, Robinson E, Jones A, Maden M, Cerny C, Muc M, Evans R, Makin H, Boyland E. A scoping review of outdoor food marketing: exposure, power and impacts on eating behaviour and health. BMC Public Health. 2022;22(1):1431. https://doi.org/10.1186/s12889-022-13784-8 .
Kabulbekov AA, Amrin KR. Vliianie Zagriazneniia Vozdukha na techenie kariesa zubov [Effects of air pollution on the etiology of dental caries]. Gig Sanit. 1991;(4):6–8.
Drury TF, Horowitz AM, Ismail AI, Maertens MP, Rozier RG, Selwitz RH. Diagnosing and reporting early childhood caries for research purposes. A report of a workshop sponsored by the National Institute of Dental and Craniofacial Research, the Health Resources and Services Administration, and the Health Care Financing Administration. J Public Health Dent. 1999 Summer;59(3):192–7. https://doi.org/10.1111/j.1752-7325.1999.tb03268.x .
Space for climate observatory. SCOlutions to Sustainable Development Goals - #3, SDG11. 2022. https://www.spaceclimateobservatory.org/scolutions-sustainable-development-goals-3-sdg11 . Accessed: 30 April 2024.04.30.
Huang YK, Chang YC. Oral health: the first step to sustainable development goal 3. J Formos Med Assoc. 2022;121(7):1348–50. https://doi.org/10.1016/j.jfma.2021.10.018 .
Article PubMed Google Scholar
Abodunrin OR, Olagunju MT, Alade OT, Foláyan MO. Relationships between oral health and the Sustainable Development Goals: a scoping review. BioMed. 2023;3(4):460–70. https://doi.org/10.3390/biomed3040037 .
Article Google Scholar
United Nations. Sustainable Development Goal 11: Sustainable cites and communities. https://nigeria.un.org/en/sdgs/11 . Accessed: 5 August 2023.
Kim YS, Ha M, Kwon HJ, Kim HY, Choi YH. Association between low blood lead levels and increased risk of dental caries in children: a cross-sectional study. BMC Oral Health. 2017;17:42. https://doi.org/10.1186/s12903-017-0335-z .
Wiener RC, Long DL, Jurevic RJ. Blood levels of the heavy metal, lead, and caries in children aged 24–72 months: NHANES III. Caries Res. 2015;49:26–33. https://doi.org/10.1159/000365297 .
Article CAS PubMed Google Scholar
Yeh C-T, Cheng Y-Y, Liu T-Y. Spatial Characteristics of Urban Green Spaces and Human Health: an Exploratory Analysis of Canonical Correlation. Int J Environ Res Public Health. 2020;17(9):3227. https://doi.org/10.3390/ijerph17093227 .
Kothencz G, Kolcsár R, Cabrera-Barona P, Szilassi P. Urban Green Space Perception and its contribution to well-being. Int J Environ Res Public Health. 2017;14(7):766. https://doi.org/10.3390/ijerph14070766 .
World Health Organisation, Prüss A, Giroult E, Rushbrook. p. Safe management of wastes from health-care activities. 1999.
Olatosi OO, Oyapero A, Ashaolu JF, Abe A, Boyede GO. Dental caries and oral health: an ignored health barrier to learning in Nigerian slums: a cross sectional survey. PAMJ - One Health. 2022;7:13. https://doi.org/10.11604/pamj-oh.2022.7.13.27641 .
Janik A, Ryszko A, Szafraniec M. Smart and Sustainable Cities: In Search Of Comprehensive Theoretical Framework. 2019. https://doi.org/10.29119/1641-3466.2019.140.10 .
Page MJ, McKenzie JE, Bossuyt PM, et al. The PRISMA 2020 statement: an updated guideline for reporting systematic reviews. BMJ. 2021;372:71. https://doi.org/10.1136/bmj.n71 .
Thylstrup A, Poulsen S. Dental caries in faeroese children aged 5–13 years. Community Dent Oral Epidemiol. 1976;4(3):115–20. https://doi.org/10.1111/j.1600-0528.1976.tb02110.x .
Tsai AI, Chen CY, Li LA, Hsiang CL, Hsu KH. Risk indicators for early childhood caries in Taiwan. Community Dent Oral Epidemiol. 2006;34(6):437–45. https://doi.org/10.1111/j.1600-0528.2006.00293.x .
Lucas N, Neumann A, Kilpatrick N, Nicholson JM. State-level differences in the oral health of Australian preschool and early primary school-age children. Aust Dent J. 2011;56(1):56–62. https://doi.org/10.1111/j.1834-7819.2010.01287.x .
Mantonanaki M, Koletsi-Kounari H, Mamai-Homata E, Papaioannou W. Prevalence of dental caries in 5-year-old Greek children and the use of dental services: evaluation of socioeconomic, behavioural factors and living conditions. Int Dent J. 2013;63(2):72–9. https://doi.org/10.1111/idj.12016 .
Han DH, Kim DH, Kim MJ, Kim JB, Jung-Choi K, Bae KH. Regular dental checkup and snack-soda drink consumption of preschool children are associated with early childhood caries in Korean caregiver/preschool children dyads. Community Dent Oral Epidemiol. 2014;42(1):70–8. https://doi.org/10.1111/cdoe.12065 .
Majorana A, Cagetti MG, Bardellini E, Amadori F, Conti G, Strohmenger L, Campus G. Feeding and smoking habits as cumulative risk factors for early childhood caries in toddlers, after adjustment for several behavioral determinants: a retrospective study. BMC Pediatr. 2014;14:45. https://doi.org/10.1186/1471-2431-14-45 .
Batliner T, Wilson A, Davis E, Gallegos J, Thomas J, Tiwari T, Fehringer K, Wilson K, Albino J. A Comparative Analysis of Oral Health on the Santo Domingo Pueblo Reservation. J Community Health. 2016;41(3):535–40. https://doi.org/10.1007/s10900-015-0127-9 .
Cabral M, Mota ELA, Cangussu MCT, Vianna MIP, Floriano FR. Risk factors for caries-free time: longitudinal study in early childhood. Rev Saude Publica. 2017;51. https://doi.org/10.11606/S1518-8787.2017051006558 .
Martins Júnior JC, de Abreu MHNG, Vieira LC, Gaudereto D, Andrade DA, Pinto RDS, et al. Association between water sanitation and living conditions and dental caries in Brazilian schoolchildren. Pesqui Bras Odontopediatria Clin Integr. 2020;20:1–9. https://doi.org/10.1590/pboci.2020.114 .
Yazdani R, Mohebbi SZ, Fazli M, Peighoun M. Evaluation of protective factors in caries free preschool children: a case-control study. BMC Oral Health. 2020;20(1):177. https://doi.org/10.1186/s12903-020-01154-y .
Osuh ME, Oke GA, Lilford RJ, Owoaje E, Harris B, Taiwo OJ, Yeboah G, Abiona T, Watson SI, Hemming K, Quinn L, Chen YF. Prevalence and determinants of oral health conditions and treatment needs among slum and non-slum urban residents: evidence from Nigeria. PLOS Glob Public Health. 2022;2(4):e0000297. https://doi.org/10.1371/journal.pgph.0000297 .
Chakraborty M, Saha JB, Bhattacharya RN, Roy A, Ram R. Epidemiological correlates of dental caries in an urban slum of West Bengal. Indian J Public Health. 1997;41(2):56–60, 67. PMID:9988979.
Jagun A, Brown DR, Milburn NG, Gary LE. Residential satisfaction and Socioeconomic and Housing Characteristics of Urban Black Adults. J Black Stud. 1990;21:40–51.
Gómez G, Kovalskys I, Leme ACB, Quesada D, Rigotti A, Cortés Sanabria LY, Yépez García MC, Liria-Domínguez MR, Herrera-Cuenca M, Fisberg RM, Nogueira Previdelli A, Guajardo V, Ferrari G, Fisberg M, Brenes JC, On Behalf Of The Elans Study Group. Socioeconomic status impact on Diet Quality and Body Mass Index in eight latin American countries: ELANS Study results. Nutrients. 2021;13(7):2404. https://doi.org/10.3390/nu13072404 .
Alkerwi A, Vernier C, Sauvageot N, Crichton GE, Elias MF. Demographic and socioeconomic disparity in nutrition: application of a novel correlated component regression approach. BMJ Open. 2015;5(5):e006814. https://doi.org/10.1136/bmjopen-2014-006814 .
Fauth RC, Leventhal T, Brooks-Gunn J. Short-term effects of moving from public housing in poor to middle-class neighborhoods on low-income, minority adults’ outcomes. Soc Sci Med. 2004;59(11):2271–84. https://doi.org/10.1016/j.socscimed.2004.03.020 .
Vasireddy D, Sathiyakumar T, Mondal S, Sur S. Socioeconomic factors Associated with the risk and prevalence of Dental Caries and Dental Treatment trends in children: a Cross-sectional Analysis of National Survey of Children’s Health (NSCH) Data, 2016–2019. Cureus. 2021;13(11):e19184. https://doi.org/10.7759/cureus.19184 .
Karam SA, Costa FDS, Peres KG, Peres MA, Barros FC, Bertoldi AD, et al. Two decades of socioeconomic inequalities in the prevalence of untreated dental caries in early childhood: results from three birth cohorts in southern Brazil. Community Dent Oral Epidemiol. 2023;51(2):355–63. https://doi.org/10.1111/cdoe.12747 .
Feldens CA, Giugliani ER, Vigo Á, Vítolo MR. Early feeding practices and severe early childhood caries in four-year-old children from southern Brazil: a birth cohort study. Caries Res. 2010;44(5):445–52. https://doi.org/10.1159/000319898 .
Bencze Z, Mahrouseh N, Andrade CAS, Kovács N, Varga O. The Burden of Early Childhood caries in children under 5 Years Old in the European Union and Associated Risk factors: an ecological study. Nutrients. 2021;13(2):455. https://doi.org/10.3390/nu13020455 .
Markovic D, Soldatovic I, Vukovic R, Peric T, Campus GG, Vukovic A. How much Country Economy influences ECC Profile in Serbian Children-A Macro-level Factor Analysis. Front Public Health. 2019;7:285. https://doi.org/10.3389/fpubh.2019.00285 .
Priesnitz MC, Celeste RK, Pereira MJ, Pires CA, Feldens CA, Kramer PF. Neighbourhood determinants of caries experience in preschool children: a multilevel study. Caries Res. 2016;50(5):455–61. https://doi.org/10.1159/000447307 .
Folayan MO, Sowole CA, Owotade FJ. Residential location and caries risk of preschool children in Lagos, Nigeria. Afr J Med Med Sci 41(1):43–8.
Anyanwu RC, Enwonwu CO. The impact of urbanization and socioeconomic status on infant feeding practices in Lagos, Nigeria. FoodNutr Bull. 1985;7(1):1–5.
Matsuda S, Yoshimura H, Kawachi I. Impact of natural disaster on oral health: a scoping review. Med (Baltim). 2023;102(8):e33076. https://doi.org/10.1097/MD.0000000000033076 .
Matsuyama Y, Aida J, Tsuboya T, Hikichi H, Kondo K, Kawachi I, Osaka K. Are lowered socioeconomic circumstances causally related to tooth loss? A natural experiment involving the 2011 Great East Japan Earthquake. Am J Epidemiol. 2017;186(1):54–62. https://doi.org/10.1093/aje/kwx059 .
Kishi M, Aizawa F, Matsui M, Yokoyama Y, Abe A, Minami K, Suzuki R, Miura H, Sakata K, Ogawa A. Oral health-related quality of life and related factors among residents in a disaster area of the Great East Japan Earthquake and giant tsunami. Health Qual Life Outcomes. 2015;13:143. https://doi.org/10.1186/s12955-015-0339-9 .
Tsuchiya M, Aida J, Hagiwara Y, et al. Periodontal disease is associated with insomnia among victims of the Great East Japan earthquake: a panel study initiated three months after the disaster. Tohoku J Exp Med. 2015;237:83–90. https://doi.org/10.1620/tjem.237.83 .
Peres MA, Macpherson LMD, Weyant RJ, Daly B, Venturelli R, Mathur MR, et al. Oral diseases: a global public health challenge. Lancet. 2019;394(10194):249–60. https://doi.org/10.1016/S0140-6736(19)31146-8 .
Amegah AK. Slum decay in Sub-saharan Africa: Context, environmental pollution challenges, and impact on dweller’s health. Environ Epidemiol. 2021;5(3):e158. https://doi.org/10.1097/EE9.0000000000000158 .
UN-Habitat. Urbanization and development: emerging futures. World Cities Report; 2016.
Parienté W. Urbanization in sub-saharan Africa and the challenge of access to basic services. J Demographic Econ. 2017;83:31–9. https://doi.org/10.1017/dem.2017.3 .
el-Nadeef MA, Adegbembo AO, Honkala E. The association of urbanisation with the prevalence of dental caries among schoolchildren in Nigeria new capital territory. Int Dent J. 1998;48(1):44–9. https://doi.org/10.1111/j.1875-595x.1998.tb00693.x .
Ha DH, Spencer AJ, Peres KG, Rugg-Gunn AJ, Scott JA, Do LG. Fluoridated water modifies the effect of breastfeeding on dental caries. J Dent Res. 2019;98(7):755–62. https://doi.org/10.1177/0022034519843487 .
El Tantawi M, Folayan MO, Mehaina M, Vukovic A, Castillo JL, Gaffar BO, Arheiam A, Al-Batayneh OB, Kemoli AM, Schroth RJ, Lee GHM. Prevalence and Data Availability of Early Childhood Caries in 193 United Nations Countries, 2007–2017. Am J Public Health. 2018;108(8):1066–72. https://doi.org/10.2105/AJPH.2018.304466 .
Download references
Not applicable.
Authors and affiliations.
Early Childhood Caries Advocacy Group, Winnipeg, Canada
Morẹ́nikẹ ́Oluwátóyìn Foláyan, Carlos Alberto Feldens, Balgis Gaffar, Jorma I Virtanen, Arthur Kemoli, Duangporn Duangthip, Ray M. Masumo, Ana Vukovic, Ola B. Al-Batayneh, Tshepiso Mfolo, Robert J Schroth & Maha El Tantawi
Department of Child Dental Health, Obafemi Awolowo University, Ile-Ife, Nigeria
Morẹ́nikẹ ́Oluwátóyìn Foláyan
Department of Pediatric Dentistry, Lutheran University of Brazil, Canoas, Brazil
Elisa Maria Rosa de Barros Coelho & Carlos Alberto Feldens
Department of Pediatric Dentistry, Pontifical Catholic University of Rio Grande do Sul, Porto Alegre, Brazil
Elisa Maria Rosa de Barros Coelho
Department of Preventive Dental Sciences, College of Dentistry, Imam Abdulrahman bin Faisal University, Dammam, Saudi Arabia
Balgis Gaffar
Faculty of Medicine, University of Bergen, Bergen, Norway
Jorma I Virtanen
Department of Paediatric Dentistry and Orthodontics, University of Nairobi, Nairobi, Kenya
Arthur Kemoli
Faculty of Dentistry, The University of Hong Kong, Hong Kong SAR, China
Ivy Guofang Sun
Department of Community Health and Nutrition, Tanzania Food and Nutrition Centre, Dar es Salaam, Tanzania
Ray M. Masumo
Clinic for Pediatric and Preventive Dentistry, School of Dental Medicine, University of Belgrade, Belgrade, Serbia
Ana Vukovic
Department of Preventive Dentistry, Faculty of Dentistry, Jordan University of Science and Technology, Irbid, Jordan
Ola B. Al-Batayneh
Department of Preventive and Restorative Dentistry, College of Dental Medicine, University of Sharjah, Sharjah, United Arab Emirates
Department of Community Health, University of Pretoria, Pretoria, South Africa
Tshepiso Mfolo
Dr. Gerald Niznick College of Dentistry, Rady Faculty of Health Sciences, University of Manitoba, Winnipeg, Canada
Robert J Schroth
Department of Pediatric Dentistry and Dental Public Health, Faculty of Dentistry, Alexandria University, Alexandria, Egypt
Maha El Tantawi
College of Dentistry, The Ohio State University, Columbus, OH, USA
Duangporn Duangthip
You can also search for this author in PubMed Google Scholar
M.O.F conceived the study. The Project was managed by M.O.F., C.A.F., B.G. and J.I.V. Data curating was done by I.A., A.N., and E.M. R. de B.C. C. Data analysis was conducted by M.O.F., C.A.F., M.O.F. and M.ET. D.D. and I.G.S. drew the conceptual framework. M.O.F. developed the first draft of the document. E.M. R. de B.C. C., C.A.F, B.G., J.I.V., A.K., D.D., I.G.S., R.M.M., A.V., O.A.A-B., T.M., R.J.S. and M.E.T. read the draft manuscript and made inputs prior to the final draft. All authors approved the final manuscript for submission.
Correspondence to Morẹ́nikẹ ́Oluwátóyìn Foláyan .
Ethics approval and consent to participate, consent for publication, competing interests.
Duangporn Duangthip is an Associated Editor with the BMC Oral Health. Jorma Virtanen is a Senior Editor Board member with BMC Oral Health. Morẹ́nikẹ́ Oluwátóyìn Foláyan and Maha El Tantawi are Senior Editor Board members with BMC Oral Health. Arthur Kemoli is an Editor Board member with BMC Oral Health. All other authors declare no conflict of interest.
Publisher’s note.
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Below is the link to the electronic supplementary material.
Rights and permissions.
Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article’s Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article’s Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/ . The Creative Commons Public Domain Dedication waiver ( http://creativecommons.org/publicdomain/zero/1.0/ ) applies to the data made available in this article, unless otherwise stated in a credit line to the data.
Reprints and permissions
Cite this article.
Foláyan, M., de Barros Coelho, E.M.R., Feldens, C.A. et al. A scoping review on the associations between early childhood caries and sustainable cities and communities using the sustainable development goal 11 framework. BMC Oral Health 24 , 751 (2024). https://doi.org/10.1186/s12903-024-04521-1
Download citation
Received : 14 September 2023
Accepted : 23 June 2024
Published : 28 June 2024
DOI : https://doi.org/10.1186/s12903-024-04521-1
Anyone you share the following link with will be able to read this content:
Sorry, a shareable link is not currently available for this article.
Provided by the Springer Nature SharedIt content-sharing initiative
ISSN: 1472-6831
You have full access to this open access article
21 Accesses
Explore all metrics
Natural resource degradation poses a major challenge to the sustainable livelihoods of farmers in developing countries, hindering progress toward achieving sustainable rural development. Watershed development and management practices (WDMPs) are powerful tools for enhancing sustainable rural development in developing countries. These practices have been shown to significantly improve livelihoods and food security. This research examined how WDM programs help achieve sustainable development in rural areas, focusing on examples from Ethiopia. This study used a systematic literature review (SLR) approach following a PRISMA review protocol. The research question was formulated using the CIMO (context, intervention, mechanisms, and outcomes) approach: “Does the watershed development and management (WDM) initiative lead to sustainable rural livelihoods?” Considering this research question, the findings indicated that WDM contributes to the socioeconomic and environmental sustainability of rural communities. It does this by enhancing households’ livelihood in terms of income generation, employment opportunities, agricultural productivity, and improvements in social services and infrastructure, as evidenced by numerous studies, thereby leading to better livelihoods and food security. This research also emphasizes the importance of community participation and supportive policies and legal frameworks for successful WDM. Overall, the systematic literature review highlights the potential of WDMPs in promoting sustainable rural development in developing countries such as Ethiopia while also highlighting the need for a supportive policy and institutional environment.
Avoid common mistakes on your manuscript.
The sustainable use of natural resources is becoming an increasingly urgent concern globally, as many of these resources face the threat of depletion [ 1 , 2 ]. The depletion of natural resources can profoundly affect human beings and jeopardize the sustenance and welfare of those who rely on these resources [ 3 , 4 ]. Indeed, farmers in developing countries’ highlands depend on natural resources for their well-being. Four-fifths of the world’s poor live in rural areas, and most depend on natural resources for their livelihoods [ 5 , 6 , 7 ]. Sub-Saharan Africa in particular faces significant vulnerability regarding the depletion of natural resources [ 8 , 9 ].
The depletion of natural resources is a critical issue in Ethiopia [ 10 ]. The highlands in the country are among the most degraded lands in Africa [ 11 ]; the ecology in many parts of the highlands is considerably damaged, sometimes beyond recovery [ 12 ]. Ethiopia has experienced high rates of land degradation, soil erosion, deforestation, and frequent droughts [ 10 , 13 , 14 , 15 ]; central highlands are among the areas experiencing persistent declines in the potential productive capability of watershed resources [ 16 , 17 , 18 , 19 , 20 , 21 ]. In light of these challenges, both the government and nongovernmental organizations have launched several initiatives aimed at natural resource development and management to alleviate the impact and address these issues. Among these approaches, WDM have evolved significantly over time.
A watershed is a natural land unit that collects water and channels it through a common outlet via a network of drains [ 22 , 23 ]. It is a hydrologic unit and is used as a physical-biological or socioeconomic-political unit for planning and managing natural resources for increasing productivity, generating employment, overall socioeconomic development and, consequently, the well-being of the community [ 22 , 24 , 25 , 26 ]. Watershed development is defined as programs involving targeted technical interventions, such as afforestation, construction of check dams, and soil conservation practices. These interventions aim to enhance the productivity of specific natural resources within the watershed, with the objective of optimizing resource utilization while ensuring sustainable water availability [ 27 , 28 , 29 ]. On the other hand, watershed management refers to the holistic understanding and regulation of hydrological relationships within a watershed. Rather than solely investing in physical interventions, socioeconomic and ecological factors are considered. The emphasis is on safeguarding resources from degradation, with the objective of maintaining ecological balance, preventing resource depletion, and promoting sustainable livelihoods [ 27 , 30 , 31 ].
Recognizing the interdependence between technical interventions and subsequent management efforts, this study adopts the combined term watershed development and management (WDM) to underscore the necessity of integrating both ecological and socioeconomic aspects for effective watershed governance. Initially, the focus was primarily on physical aspects, such as reforestation and soil conservation, which contribute to climate resilience by mitigating the impacts of extreme weather events and maintaining ecosystem services crucial for agriculture [ 32 , 33 , 34 ]. However, this approach has transformed into a holistic perspective integrating social, economic, and environmental dimensions. Today, effective WDM encompasses the coordinated management of land, water, biota, and other resources within a defined geographical area [ 22 , 35 ].
As the world collectively tackles urgent environmental, social, and economic issues, strategic WDM plays a crucial role. This approach, supported by research from various scholars [ 27 , 36 , 37 , 38 , 39 ], is instrumental in achieving sustainable development goals (SDGs). By safeguarding natural resources, promoting sustainable livelihoods, and bolstering resilience, effective WDM contributes significantly to the SDGs. The significance of WDM in achieving sustainable rural development is explored through the lens of the SDGs. The central focus of SDG 6 (Clean Water and Sanitation) and SDG 15 (Life on Land) from the perspective of watershed management lies in conserving natural resources. In the context of SDGs 6 and 15, watershed management serves as a preventive measure against soil erosion, deforestation, and habitat degradation. This approach promotes biodiversity and preserves ecosystem functions. Moreover, watershed management plays a critical role in sustaining freshwater reservoirs, which are essential for human settlements, agriculture, and ecological balance. The scope of SDG 1 (No Poverty) emphasizes the enhancement of livelihoods. Effective watershed management practices lead to increased agricultural productivity, thereby generating livelihood opportunities for rural communities [ 40 , 41 , 42 ].
Furthermore, through the lens of watershed management, SDG 13 (climate action) emphasizes the strengthening of resilience. Proficient watershed management significantly boosts climate resilience and communal well-being. This is evident in SDG 13, where effective watershed management mitigates climate-induced challenges such as floods and regulates water flow, thereby fortifying community resilience against environmental adversities. SDG 8 (Decent Work and Economic Growth) underscores the role of well-managed watersheds in bolstering sustainable livelihoods by ensuring water access for industries, fisheries, and tourism [ 40 , 42 ]. Additionally, within the ambit of SDG 11 (Sustainable Cities and Communities), competent watershed management reduces vulnerability to natural disasters, thereby fostering safer urban environments [ 40 , 41 , 42 ].
WDM are crucial for achieving sustainable rural development, particularly in developing countries; Ethiopia, a developing country, has acknowledged the significance of WDM in tackling challenges and promoting sustainable rural development since mid-1970 [ 17 , 38 , 43 , 44 , 45 , 46 , 47 , 48 ]. These efforts aim to restore natural resources, enhance agricultural productivity, and improve the livelihoods of people living in watershed areas. By implementing integrated WDM practices (WDMPs), Ethiopia seeks to be effective in terms of soil conservation, reforestation, and water harvesting; communities can improve their resilience to the impacts of climate change, enhance their food security and improve agricultural productivity in the country [ 37 , 48 , 49 , 50 , 51 , 52 , 53 , 54 ]. However, despite the existence of actionable research, these efforts have yet to translate into substantial enhancements in sustainable rural development regarding livelihood outcomes. These outcomes include income and employment generation, agricultural productivity, social services, infrastructure, and food security within the country. Consequently, this study aimed to identify a comprehensive framework for optimizing WDMPs, specifically focusing on the Ethiopian central highlands.
The remainder of the article is organized as follows: In sect. 2 , the methodology of the study is discussed. Section 3 presents the study’s results, and Sect. 4 presents a discussion of the findings. Sections 5 and 6 present the conclusions and recommendations, respectively.
This study aims to contribute new knowledge to the literature by addressing how watershed development is integral to sustainable rural development. This study employs the pragmatist worldview [ 55 , 56 ]. Pragmatism explores the origin, nature, and limits of human understanding, prioritizing practical implications over abstract truths [ 56 , 57 , 58 , 59 , 60 ]. Pragmatic theories emphasize the importance of practical aspects when assessing the role of WDM in sustainable rural development. This study employed a systematic literature review (SLR) as the research technique. This approach contributes to the current understanding of social aspects of sustainable rural development through enhanced watershed management practices and to finding, critiquing, and synthesizing the results of all available studies to establish overall findings for a question. SLRs provide a structured approach for reviewing the literature and follow a detailed process. The methods used were predefined, and the research and reporting followed specific guidelines and frameworks, as highlighted by [ 61 ]. This method involves establishing a protocol beforehand, applying rigorous search strategies across multiple databases, and conducting a critical appraisal of selected studies to address a specific research question [ 62 ].
While prior research has explored the potential benefits of watershed management, these studies lacked a focus on sustainable rural development or did not specifically address households in developing countries such as Ethiopia. Poonia and Singh [ 63 ] for example, focused on groups in India, while Worku and Tripathi [ 64 ] and Abebaw [ 65 ] focused on Ethiopia using traditional review methods and did not focus on the role of watershed management in sustainable rural development. The scarcity of research, according to the researchers, on the issue within a developing country context such as Ethiopia prompted this SLR, aiming to bridge the knowledge gap and offer a comprehensive understanding of the literature.
This study was guided by a preferred reporting items for systematic review and meta-analysis (PRISMA) review protocol. Based on the review protocol, the authors started the SLR by formulating an appropriate research question for the review. The research question was formulated using the context, intervention, mechanisms, and outcomes (CIMO) approach. The CIMO framework is more applicable in nonmedical research where there is a limited requirement to compare interventions [ 66 ]. This study investigates the impact of WDM (intervention) on achieving sustainable rural development (outcome) through livelihood outcomes (mechanisms) for rural communities (context). The final question read as follows: “Does watershed development and management initiative lead to sustainable rural livelihoods?” This question examines the role of WDM in contributing to sustainable rural livelihoods. The question also examines the various benefits that households are likely to gain from WDM in terms of livelihood outcomes. The question also touches on community participation and policy to ensure the sustainability and conservation of watershed resources to meet the needs of the community.
Following the research question development, the next step involved a “web search” using keywords and “Boolean operators”. This search targeted articles relevant to the research question and qualitative variables. Keywords such as “watershed development”, “watershed management”, “sustainable rural development”, “livelihood outcome”, and “food security” were used. The purpose of using the keywords was to enhance the accuracy of the literature. The Boolean operators approach was also used to combine search terms in ways that broaden and limit the search results to the specific inclusion and exclusion criteria. The primary sources of information for this review were the electronic journal databases Web of Science, Google Scholar, Scopus, and WorldCat for peer-reviewed articles, books, and gray literature. The search strategy was continuously revised by trial and error until the databases yielded the maximum number of articles for screening. Based on the results of the first stage of screening, a literature search revealed a total of 1132 articles, of which 356 were from the Web of Science, 235 were from Scopus, 465 were from Google Scholar, and 76 were from other methods. All bibliographical details were imported into the EndNote 20 reference manager to manage the references and eliminate duplications. The next stage of the method involved selecting relevant articles. Duplicates were removed first, and the authors applied specific criteria (detailed in Table 1 ) to include or exclude studies. The inclusion and exclusion criteria used to select relevant studies for this research are detailed in Table 1 . This table outlines the specific criteria considered for the included and excluded studies.
In the first phase, 735 articles remained for further screening, while others were eliminated from the review at this stage because they did not meet the inclusion criteria. Next, article screening was performed by reading titles and abstracts, and in some cases, the entire text manually relevant to this study and irrelevant articles were removed, resulting in 277 potentially relevant articles. However, not all these articles were eligible for the study. A total of 243 articles were rejected for being ineligible or removed for other reasons, such as the year of publication, and subjected to further evaluation to identify those with specific answers to the research question. A total of 34 articles met the final criteria and were selected based on their relevance and accuracy in answering the research question. Following the PRISMA guidelines, the inclusion and exclusion criteria were applied to select relevant studies. The selection process is visualized in a flowchart in Fig. 1 .
PRISMA flowchart
This study applied a thematic analysis of the SLR. The retrieved articles ( n = 34) were classified into various critical dimensions for analysis, as shown in Fig. 1 . The main classifications included title, authors, region, and main findings. The analysis involved examining each of the findings to determine how they relate to sustainable rural development. This study aimed to determine whether WDM are correlated with or support sustainable rural development. Each of the findings was carefully examined to determine the relationship between watershed and sustainability.
This research asks, “Does the watershed development and management initiative lead to sustainable rural development?” Considering the research question of this research, the findings indicate that WDM contributes to the socioeconomic and environmental sustainability of the rural community by enhancing households’ livelihoods in terms of income generation, employment opportunities, agricultural productivity, and improvements in social services and infrastructure, as evidenced by numerous studies, thereby improving livelihoods and food security. The research findings emphasize the importance of community participation and policies and legal frameworks governing WDM. Finally, the study synthesized the findings by exploring key themes such as assessing community livelihood status, understanding the interplay between livelihood assets and watershed practices, evaluating the role of watershed development in socioeconomic aspects, measuring household food security, measuring community participation, and analysing relevant policies and legal frameworks on WDM.
Many studies have focused on watershed management in Ethiopia and India. Of the 34 articles reviewed, 15 explored initiatives in Ethiopia, and 13 explored initiatives in India. The remaining studies covered a wider range of regions, including China, Tanzania, South Africa, Thailand, and Vietnam, often in combination. This suggests a significant emphasis on WDM in the two countries of Ethiopia and India. The reviewed articles span a range of publication dates, with the earliest published in 2002 and the most recent appearing in 2024 (the current year). One was published in 2002, two in 2004, two in 2005, one in 2006, one in 2008, four in 2009, two in 2010, one in 2011, four in 2014, one in 2014, four in 2015, two in 2016, two in 2018, two in 2019, two in 2020, one in 2023, and one in 2024. This distribution suggests the inclusion of both established and more recent research on watershed management.
Following PRISMA guidelines, relevant articles were identified through a systematic review process. This resulted in a table summarizing the selected articles in Appendix . The table includes titles, authors, publication dates, study locations, and key findings of each study. To ensure the validity and applicability of the findings, the study further evaluated the evidence (detailed in Appendix ) based on four criteria: strength, content validity, potential bias, and relevance to watershed development and sustainable rural livelihoods. Subsequently, based on the findings, the researcher constructed a diagram (Fig. 2 ) that explained how well-managed watersheds create a solid foundation for sustainable rural development. WDM initiatives have a direct impact on the sustainable rural development of communities through livelihood assets, thereby affecting household income and employment generation capacity, agricultural productivity, social services and infrastructure, and food security status in terms of food availability, access, food utilization, and stability. Community participation in WDM initiatives has a multifaceted impact on sustainable rural development both within a watershed and outside the watershed community. Policy is one of the master key factors, in addition to other considerations, that shape the outcome of initiatives for the sustainable rural development of a country.
Diagram illustrating how watershed development serves as the cornerstone for achieving sustainable development in rural areas
This study synthesized the effect of WDM on sustainable rural development by exploring several key themes. Based on the thematic analysis, six themes were developed: assessing community livelihood status (Sect. 4.1 ), understanding the interplay between livelihood assets and watershed practices (Sect. 4.2 ), evaluating the role of watershed development in socioeconomic aspects (Sect. 4.3 ), measuring household food security (Sect. 4.4 ), measuring community participation (Sect. 4.5 ), and analysing relevant policies and legal frameworks on WDM (Sect. 4.6 ).
This section focuses on evaluating the livelihood situation of households within the community. From a theoretical perspective, the sustainable livelihoods framework offers insights into assessing the livelihood status of communities. This framework highlights the importance of various livelihood assets (social, human, natural, physical, and financial capital) in achieving sustainable livelihoods [ 67 , 68 ]. Individuals engaged in watershed management benefitted from improved access to natural resources, enhanced social networks, and increased income diversification, leading to greater livelihood resilience than that of nonpractitioners [ 50 , 69 ].
According to Argaw, Abi [ 50 ], the status of the livelihood assets of the Shankur Tereqo and Mende-Tufesa watersheds (supposed as a control watershed) were comparatively analysed based on the five capital statuses of the livelihood assets. To measure the livelihood status of the households, eighteen variables representing the five livelihood assets of the households were selected. Human capital is measured by the age and education level of the household head, household size, and number of working members [ 70 , 71 , 72 , 73 ]. Financial capital refers to the household’s income sources, including annual agricultural and nonagricultural income, livestock holdings, and access to credit [ 68 , 71 , 73 ]. Natural capital focuses on households’ access to and quality of agricultural land, including total land area, fertility, and the availability of high-quality farmland [ 71 , 72 , 73 ]. Physical capital assesses the quality of housing, household possessions, access to public transportation, and proximity to markets [ 71 , 72 , 73 , 74 ]. Finally, social capital evaluates the community’s level of social interaction and support, including participation in social organizations, social networks, and the presence of nongovernmental organizations (NGOs) or local institutions [ 71 , 72 , 73 , 75 , 76 ].
Argaw, Abi [ 50 ] found no significant overall difference in livelihood status between households in the Mende Tufesa and Shankur Tereqo watersheds. However, there are variations in the different types of capital that contribute to livelihood status. The variations are depicted by the pentagon that states the livelihood status of the practitioners in Fig. 3 and non-practitioners in Fig. 4 .
Livelihood status of the untreated watershed (based on [ 50 ])
Livelihood status of the treated watershed (based on [ 50 ])
The variation in livelihood status in terms of livelihood capital between the households in the study watersheds showed the following:
Financial and physical capital: Households in both watersheds scored low (below 0.33) on these measures, indicating a relatively poor state compared to the Shankur-Tereqo watershed .
Human and natural capital: These aspects showed some variation but still fell within the “average” range (0.33–0.66) for both watersheds.
Social capital: This measure stood out, with both watersheds scoring in the “good” category. This suggests a strong level of social interaction and support within the communities.
Another study by Siraw, Bewket [ 51 ] also revealed the significant contribution of WDM to livelihood benefits in terms of overall livelihood capital indices, with variations in the improvement of different livelihood capitals across different micro-watersheds and considerable improvements in natural and human capital. Studies have investigated the true effect of the initiative by analysing the livelihood status of the community using a sustainable livelihood framework. Focusing on the approach implemented by Argaw, Abi [ 50 ], this study suggested conducting a comparative analysis of the livelihood status of households practising and those not practising watershed management, which revealed a significant difference. As households engaged in watershed initiatives often have diversified livelihood strategies and access to natural resources, nonparticipants face greater vulnerabilities and dependence on external support [ 50 , 77 , 78 ]. Individuals engaged in watershed management often exhibit greater resilience and livelihood diversification than those not involved, as they benefit from improved access to natural resources and sustainable land management practices [ 79 , 80 ].
To enhance the rural livelihoods of households in watersheds, optimizing the WDM is expected. Rural livelihoods in Ethiopia are experiencing widespread challenges, including limited access to education, healthcare, and basic infrastructure. Moreover, vulnerability to natural disasters such as droughts and floods exacerbates the plight of agricultural and livestock-dependent communities [ 51 , 81 ]. Concerted efforts are imperative at the community and governmental levels to address these pressing issues. Interventions entailed enhancing access to education, healthcare, and potable water alongside strategic investments in infrastructure such as roads and electricity [ 51 , 82 ]. Promoting sustainable agricultural practices and extending financial and technical support to smallholder farmers are pivotal steps toward resilience-building [ 83 ]. Crucially, community engagement may need to underpin the planning and execution of these initiatives to ensure their effectiveness and long-term sustainability.
This section investigates how a community’s resources (livelihood assets) influence and is influenced by their WDMPs. The interconnection between livelihood assets and watershed management practices is a multifaceted relationship that plays a pivotal role in the sustainable development of communities. Livelihood assets within a sustainable livelihood framework encompass various tangible and intangible resources that individuals and communities utilize to support their livelihoods, including natural, human, social, physical, and financial assets [ 67 , 68 , 84 ]. Access to these assets plays a crucial role in influencing engagement in watershed development practices to enhance community resilience, promote sustainable resource management, and facilitate participation in watershed initiatives [ 50 , 85 , 86 , 87 ].
The relationships between livelihood assets and WDMPs are bidirectional and dynamic. On the one hand, the availability and quality of livelihood assets significantly impact the effectiveness of watershed management interventions [ 88 ]. For instance, communities blessed with abundant natural resources and social capital—such as fertile soil and water—tend to be better prepared to implement sustainable land management practices and adapt to the effects of climate change, and their efforts have resulted in greater success and long-term sustainability [ 89 , 90 ]. On the other hand, WDMPs can directly influence livelihood assets [ 50 , 78 ]. When watershed management is effective, natural capital can be enhanced by improving soil fertility, water availability, and biodiversity. These improvements, in turn, support agricultural productivity and provide essential ecosystem services for livelihoods [ 91 ]. Additionally, community-based watershed management approaches empower local communities by creating income generation, capacity building, and collective decision-making opportunities. This empowerment strengthens these communities’ human and social capital [ 88 ]. Comparisons between Ethiopia, Nepal, and Indonesia highlight the diverse interplay of social, human, natural, physical, and financial capital in shaping community engagement and resilience [ 92 , 93 , 94 ].
Argaw, Abi [ 50 ] examined the relationships between livelihood assets and watershed development and management practices (WDMPs) using structural equation modelling (SEM). The analysis revealed that the WDMP generally had statistically significant and positive relationships with all livelihood assets. As depicted in Fig. 5 , the WDMP had the highest correlation or significant positive relationship with natural capital (NC), with a path coefficient of 0.553, compared to livelihood assets. In contrast, it had the lowest correlation with social capital (SC), with a path coefficient of 0.232, yet a statistically significant positive relationship existed. Other human capital (HC), physical capital (PC), and financial capital (FC) had statistically significant and positive relationships with the WDMP according to standard estimation or path coefficients of 0.43, 0.378, and 0.336, respectively [ 50 ].
The diagram represents the interconnectedness between livelihood assets and the practices they use to manage their watershed (based on [ 50 ])
Ethiopia has the potential to enhance rural livelihood assets in several ways through WDMPs. First, these practices can improve the availability and accessibility of water resources, which are critical for supporting agriculture and livestock production. This can increase the productivity and income of farmers and herders, thereby enhancing their livelihood assets. Second, watershed management practices can help conserve soil and water resources, prevent soil erosion and improve soil fertility. This can lead to better crop yields and improved food security, which can also enhance livelihood assets. Third, watershed development practices can promote the use of renewable energy sources, such as solar and wind power, which can provide alternative energy sources for rural communities. This can reduce their dependence on nonrenewable energy sources and enhance their economic and social assets. Overall, adopting WDMPs can significantly positively impact rural livelihood assets in Ethiopia and promote sustainable development in the region.
Studies suggest that WDMPs may hold promise for improving the lives of people in developing countries such as Ethiopia. These practices could enhance rural livelihoods in several ways.
Improved agriculture and livestock production: By enhancing the availability and accessibility of water, watershed management practices could support agriculture and livestock production [ 95 , 96 ]. This might lead to increased productivity and income for farmers and herders, ultimately contributing to their overall well-being.
Soil conservation and fertility: WDMPs have the potential to conserve soil and water resources, prevent erosion, and improve soil fertility [ 82 , 97 ]. This could result in better crop yields and improved food security, further benefiting rural livelihoods.
Source of energy: These practices might also encourage the use of renewable energy sources such as solar energy, providing alternative energy options for rural communities [ 50 , 97 ]. This could lead to a reduction in the dependence on non-renewable sources, potentially boosting economic and social well-being.
In conclusion, adopting WDMPs appears to be a promising approach to positively impact rural livelihoods in Ethiopia and contribute to the region’s sustainable development.
This section explores how developing and managing watersheds contribute to positive social and economic outcomes for the community. Economic development theories, such as human capital and agricultural development theories, offer insights into how watershed development contributes to socioeconomic aspects [ 98 , 99 ]. Human capital and agricultural development are intertwined concepts; human capital development theories highlight the crucial role of investing in farmers’ knowledge, skills, health, and empowerment to achieve sustainable agricultural development. This approach goes beyond physical capital (machinery, equipment) and recognizes the human factor as a key driver of progress [ 100 ]. Watershed development initiatives can lead to increased income generation, employment opportunities, and agricultural productivity through improved access to water resources, soil conservation measures, and sustainable land management practices [ 101 , 102 , 103 , 104 ].
Watershed development initiatives significantly contribute to the socioeconomic development of developing countries across several key areas, including income generation, employment opportunities, agricultural productivity, and improvements in social services and infrastructure, as evidenced by numerous studies, thereby improving livelihoods and reducing poverty [ 36 , 83 , 96 , 105 ].
Research shows that watershed development projects increase local communities’ income generation opportunities [ 105 , 106 ]. For instance, watershed management activities such as soil conservation and water harvesting have enhanced land productivity, enabling farmers to cultivate higher-value crops and generate additional income. Additionally, the implementation of sustainable agricultural practices, such as agro forestry and integrated crop-livestock systems, has been found to improve crop yields and diversify income sources [ 50 , 107 , 108 , 109 ]. It creates employment opportunities by involving local communities in activities such as afforestation and infrastructure building; these initiatives significantly contribute to poverty reduction and foster social inclusion [ 50 , 107 , 110 ].
Watershed development interventions improve agricultural productivity by enhancing soil fertility, water availability, and land management practices. For instance, implementing soil and water conservation practices prevents soil erosion and enhances soil moisture retention [ 97 ]. This, in turn, results in higher crop yields and greater agricultural resilience to climate fluctuations [ 83 ]. Additionally, the adoption of WDM initiatives has been proven to enhance agricultural productivity and food security [ 111 , 112 , 113 ].
Several studies, such as Kerr [ 114 ], Hope [ 115 ], Hassan, Alam [ 116 ], Ibrahim, Hassan [ 117 ], Surya, Syafri [ 118 ], Herrera, Ellis [ 119 ], Norton, Seddon [ 120 ], Adeniran, Daniell [ 121 ], suggest that watershed development projects can have a positive influence on social services and infrastructure in rural areas. Investments in water supply systems, irrigation infrastructure, and rural roads may lead to improved access to essential services and markets, potentially enhancing the quality of life of local communities. Furthermore, activities focused on strengthening social services such as healthcare, education, and sanitation have been shown to potentially contribute to overall human development and well-being.
Although WDM initiatives hold promise for building resilient and prosperous communities in the long term, the extent and nature of these impacts vary across countries. While these initiatives have the potential to generate income, create employment opportunities, enhance agricultural productivity, and improve social services and infrastructure, the specific results depend on various factors, such as contextual nuances in policy formulation [ 122 , 123 ], institutional capacity [ 2 ], governance frameworks [ 124 ], implementation strategies, and socioeconomic contexts [ 27 , 122 , 124 ].
Argaw, Abi [ 50 ] examined the impacts of the WDMP on livelihood outcomes in terms of income generation, employment opportunities, agricultural productivity, improvement in social services, and infrastructure through SEM. The study suggested that the WDM program may be a promising tool for households in the study area. The program appears to have the potential to contribute to increased income and job creation by supporting various aspects of their well-being, known as livelihood assets. These assets include skills and knowledge (human capital), access to financial resources (financial capital), infrastructure and tools (physical capital), and environmental resources (natural capital). The study also revealed a potential increase in agricultural productivity as a result of the WDMPs. This could be linked to improved practices in land and water conservation, leading to greater use of double cropping, a shift towards more intensive cropping systems, and ultimately, greater crop production. Finally, the study suggested a positive association between the program and improved access to social services and infrastructure for participating households. This could be due to the overall enhancement of their livelihood assets, particularly in terms of natural resources and social networks. Figure 6 shows the SEM path coefficients for WDMPs and their standardized direct effects on the five livelihood assets and the indirect effects of income and employment generation, agricultural productivity, and social services and infrastructure.
The diagram depicts the influence of watershed development and management practices on a community’s socioeconomic aspects, mediated by livelihood assets (based on [ 50 ])
According to the findings from studies, WDM initiatives play an important role in developing countries, specifically in Ethiopia; they have helped improve the livelihoods of the rural population by providing them with access to generate employment opportunities and helping increase and diversify the income sources of the household as well as improving the well-being of people [ 50 , 82 , 83 ]. They improved the agricultural productivity of households in rural areas [ 95 , 96 , 97 , 125 ]. This might lead to increased productivity and income for farmers and herders, ultimately contributing to their overall well-being. The government of Ethiopia has been actively promoting WDM programs and has invested heavily in building infrastructure to support these programs [ 64 , 65 , 83 ]. As a result, there has been a noticeable improvement in the socioeconomic conditions of people living in rural areas of Ethiopia [ 126 ]. Thus, investing in WDM can significantly impact the overall socioeconomic development of communities and regions.
This section compares the food security situation of households between WDM practitioners and non-practitioners. The food systems approach highlights the interconnectedness of all parts of the system and the need for a holistic approach to achieving food security [ 49 , 127 , 128 ]. WDM contributes to a more resilient food system. It helps conserve soil fertility and water resources, which are crucial for sustainable food production. Additionally, by improving water quality and reducing erosion, it protects downstream agricultural areas. This holistic approach strengthens the entire food system, contributes to food security, and offers a valuable lens for analysing the role of WDM in achieving food security and evaluating the food security status of households within WDM initiatives.
In developing countries, household food security status can vary significantly between communities in treated watersheds and those in untreated watersheds due to several interconnected factors. Participants in WDM programs usually have a more favourable food security status than nonparticipants. Interventions such as soil conservation, water harvesting, and agro forestry within watersheds help support sustainable farming practices. They lead to improved agricultural productivity, increased crop yields, a variety of food sources, and greater resilience to climate fluctuations [ 34 , 129 , 130 , 131 , 132 , 133 , 134 ].
Households practicing WDM experience better food security, and these interconnected benefits underscore the importance of investing in sustainable WDM to enhance food security in vulnerable communities. For instance, interventions such as soil conservation, afforestation, and water harvesting are crucial for enhancing water availability and maintaining water quality within watersheds. As a result, they enable more dependable irrigation practices, especially during dry periods. This, in turn, leads to increased agricultural productivity and ensures a diverse food supply for households. Furthermore, contour ploughing, terracing, and agro forestry help prevent soil erosion, conserve soil moisture, and enhance soil fertility. Healthy soils support better crop yields, thus increasing food production and contributing to household food security [ 27 , 47 , 135 , 136 , 137 ].
A study by Naji, Abi Teka [ 138 ] measured the impacts of the WDMP on household food security status using the household food insecurity access scale (HFIAS) and household dietary diversity score (HDDS). This study disaggregated the results among WDM practitioners and non-practitioners; the HFIAS results are presented in Fig. 7 , and the HDDS results are shown in Fig. 8 .
HFIAS survey results (based on [ 138 ])
HDDS survey results (based on Naji, Abi Teka [ 138 ])
The HFIAS and HDDS results painted a concerning picture of food insecurity in the study area. The HFIAS survey results (Fig. 6 ) revealed that a significant portion of households (over 70%) worried that food would run out and ate only a few kinds of food. A substantial number of households (over 35%) experienced an actual food shortage, and some households (over 15%) had gone to sleep hungry more than once. Among the communities, 84.94% were food insecure at various levels (mild, moderate, or severe), of which 54.33% were found in the Mende-Tufesa watershed area. The study calculates the household food insecurity access incidence (HFIAP) to assess overall food insecurity. The results were concerning: only 15.1% of respondents were classified as food secure. In contrast, the number of severely food insecure households was three times greater. These households were forced to cut back on meal sizes or the number of meals they ate frequently. Additionally, some even experienced harsher food insecurity conditions, such as going a whole day without eating [ 138 ].
This study further implemented the HDDS food security measurement tool to assess dietary quality. Figure 7 shows that a significant portion (31.7%) of households had low dietary diversity. This means that their diets lacked variety and essential nutrients. However, there were also positive findings: 42.3% of households had medium dietary diversity, and 26% even achieved high dietary diversity. Overall, the average HDDS score was 4.83, indicating a medium level of dietary diversity for the study area. This suggests that households typically consume approximately five different food groups on average. The study clearly showed that the household food security status of rural households differed between Shankur-Tereqo and Mende-Tufesa . These findings support those of previous studies showing that household practices related to watershed initiatives were more conducive to food security for households than for non-practices households in the study area [ 138 ].
An assessment of household food security within watershed communities revealed a multifaceted interplay of factors. These factors are influenced by the agro-ecological conditions (such as climate, soil fertility, and water availability), institutional contexts (including land tenure policies, market access, and government support programs), and socioeconomic dynamics (such as income levels, education, and social safety nets) of the community. Comparative analyses between Ethiopia, India, and Malawi can shed light on the diverse determinants that shape food security outcomes across different contexts. This highlights the need for interventions that are tailored to the specific circumstances of each community [ 139 , 140 , 141 ].
According to the findings from the studies, watershed development initiatives play an important role in developing countries, specifically in Ethiopia; they have helped improve the household food security of the rural population. WDM interventions within watersheds help support sustainable farming practices and lead to improved agricultural productivity, increased crop yields, a variety of food sources, and greater resilience to climate fluctuations [ 47 , 83 , 112 , 125 , 126 , 130 , 138 , 142 ]. Investing in watershed development initiatives holds promise for enhancing household food security across communities and regions. This is likely achieved through improved WDM and potentially increased agricultural productivity.
This section focuses on assessing the role of community participation in watershed intervention for sustainable rural development. From a theoretical standpoint, social capital theory offers insights into the level of community participation in watershed development endeavors. Robust social connections, trust, and collaboration among community members enable effective engagement in decision-making, execution of watershed initiatives, and durability of interventions over time [ 143 , 144 ].
Community participation refers to the involvement of residents, including community leaders, farmers, women, youth, and other stakeholders, in watershed management project planning, implementation, and decision-making processes. Community participation is essential for the success of watershed development initiatives because it fosters ownership, enhances local knowledge and capacity, promotes social cohesion, and ensures the sustainability of interventions [ 145 , 146 , 147 , 148 ]. Community participation in watershed development in developing countries is facilitated through various mechanisms and approaches aimed at engaging local communities in decision-making processes, project planning, implementation, and monitoring [ 146 , 149 , 150 ].
The study conducted by Naji, Abi Teka [ 148 ] measured the extent to which people participated in the WDMP across the planning, implementation, monitoring and evaluation phases and applied a People’s Participation Index (PPI). The findings portrayed in the chart (Fig. 9 ) indicated that non-practitioners exhibited moderate participation, while WDM practitioners were highly engaged. Overall, the PPIs were categorized as moderate, reflecting the diverse roles and responsibilities assumed by households during watershed implementation and contributing to their significant stakes in multiple activities within the study area. Figure 9 presents a chart comparing the level of community participation between WDM practitioners and non-practitioners.
Community participation level in watershed management (based on [ 148 ])
Community participation has emerged as a linchpin for the success of watershed initiatives, yet its dynamics vary widely across countries. Factors affecting the successful participation of the community in the implementation of watershed projects exhibit considerable heterogeneity, necessitating context-specific approaches. In the context of developing countries, community participation can be shaped by several factors [ 63 ]. These include local leadership and governance, community skills and technical capacity, perceived benefits and risks, cultural and social norms, access to resources and infrastructure, stakeholder engagement, communication and awareness, policy and institutional frameworks, and environmental degradation and climate change, all of which impact the success and sustainability of watershed development initiatives [ 151 , 152 , 153 , 154 , 155 , 156 , 157 , 158 , 159 , 160 , 161 , 162 , 163 , 164 ].
At the household level, various factors influence participation in WDM initiatives in developing countries. These factors include the socioeconomic status of the household head, educational level, land size, family size, perceived benefits and costs, institutional support, and extension services [ 145 , 165 , 166 , 167 , 168 , 169 , 170 ]. Drawing on insights from various studies, it appears that several factors can play a significant role in the success and long-term sustainability of WDM initiatives. To encourage active participation from local communities, agricultural authorities at the local and regional levels can play a key role. This could involve providing training opportunities, fostering a sense of ownership among participants, and highlighting the long-term benefits for the community.
The policies, strategies, programs, and legislative frameworks for watershed development and management (WDM) in developing countries vary significantly depending on the country’s specific context, political structure, environmental challenges, and socioeconomic conditions. However, many developing nations can observe some common themes and approaches. Theoretically, this study incorporates political ecology theory, which examines the political-economic factors that shape environmental governance, resource distribution, and access to decision-making processes [ 171 ]. It emphasizes the inherent “politicalness” of the environment, arguing that environmental degradation cannot be solely understood through scientific and technical lenses [ 172 ]. Political ecology offers a valuable lens for analysing WDM policies, programmes, and strategies. Ensuring alignment with local needs and environmental realities enhances the impact of WDM initiatives [ 173 , 174 , 175 ].
Strengthening the legal frameworks for WDM is crucial. It helps regulate land use, protect water resources, uphold community rights, and promote sustainable practices, ultimately enhancing watershed governance and resilience. Continuously assessing existing policies, programs, and strategies is essential for identifying strengths, weaknesses, and areas for improvement, leading to more effective interventions and better outcomes. Identifying gaps in current WDMPs and recommending policy options are vital for enhancing the effectiveness, sustainability, and long-term resilience of watershed management in developing countries [ 27 , 43 , 44 , 93 , 116 , 137 , 176 ].
Legal frameworks for WDM vary significantly across countries, reflecting differences in legal traditions, governance structures, and environmental policies. Comparative analyses among developing countries have shed light on diverse regulatory approaches and their implications for watershed governance [ 27 , 177 , 178 , 179 , 180 ]. To effectively assess policies, programs, and strategies, as well as to identify gaps and recommend policy options, nuanced contextualization within each country’s socioeconomic and environmental context is essential. Furthermore, comparative studies have provided insights into the effectiveness of different approaches and underscore the importance of adaptive management and context-specific policy prescriptions tailored to local realities [ 39 , 175 , 180 , 181 , 182 ].
WDM plays a crucial role in sustainable development, especially in developing countries such as Ethiopia, where water scarcity and soil erosion are pressing concerns. Despite substantial efforts to enhance WDMPs, more policy execution is still needed in the country. While the government has crafted well-formulated policies, programs, and strategies, the true hurdle lies in their implementation. Legal provisions for watershed management, such as the Water Resources Management Policy and the Proclamation on Watershed Management, face significant challenges during execution. Bridging the gap between policy design and practical implementation is essential. Ensuring that formulated policies and strategies are translated into action is vital for achieving desired goals and positively impacting the environment and people.
One significant gap in WDM in the study area was the need for coordination among various government agencies involved in the process, and the absence of effective enforcement mechanisms and penalties weakens the impact of existing legal frameworks in WDM. This results in fragmented and inefficient programs. Establishing a national coordinating body with clear mandates and responsibilities for coordinating WDM across different sectors and at different government levels is crucial to addressing this issue. Another gap lies in the need for more participation of local communities in decision-making processes related to watershed management. Encouraging participatory approaches, such as community-based natural resource management, can empower communities to take ownership and responsibility for their watersheds.
Developing countries, including Ethiopia, have established appealing policies, strategies, programs, approaches, and legal frameworks for and related to WDM. However, practical execution of these methods remains challenging. Countries must address coordination and enforcement issues to ensure effective implementation and sustainable watershed management. Bridging the gap between policy formulation and execution is crucial, with active community involvement playing a key role. Investing in research and capacity building will also enhance evidence-based decision-making and policy effectiveness. Collaborative efforts among the government, academia, and civil society can drive positive changes in the country’s natural resource management and contribute to sustainable development and poverty reduction.
WDMPs have been shown to significantly enhance sustainable rural development, particularly in terms of livelihood and food security in developing countries. Wani and Ramakrishna [ 183 ] and Wani, Dixin [ 184 ] both highlighted the potential of these practices for improving rainwater use efficiency, reducing soil erosion, and increasing agricultural productivity and rural incomes. This approach, as discussed by [ 132 ] and [ 34 ], highlights the potential of community watershed programs for improving livelihoods and resilience, particularly in the face of climate change impacts. These programs have been successful in increasing agricultural productivity, doubling family incomes, and reducing runoff and soil loss.
Yoganand and Gebremedhin [ 185 ] and Naji, Abi Teka [ 148 ] further emphasized the role of participatory WDM in achieving sustainable rural livelihoods. Finally, Habtu [ 186 ] and Poonia and Singh [ 63 ] identify challenges such as poor institutional support and lack of participation in the promotion of watershed-based interventions and suggest key conditions for their revitalization, including institutional support, community participation, and capacity building. These studies collectively underscore the potential of WDMPs for promoting sustainable rural development while also highlighting the need for supportive policies and institutional environments.
Effective WDM are crucial for sustainable rural development, especially in developing countries such as Ethiopia, where various ecosystems and weather conditions pose significant challenges. It is essential for environmental conservation and directly contributes to achieving multiple SDGs. Recognizing the interconnectedness of natural systems and human well-being can create a more sustainable and resilient future. Advancing WDM in developing countries requires a holistic approach that integrates socioeconomic aspects, community participation, policy and institutional dimensions. By addressing the key elements outlined in this article and implementing the recommended policy options, countries could achieve more sustainable and resilient watershed management outcomes, contributing to the well-being of their people and the preservation of their natural resources. The findings highlight the critical role of watershed management in promoting sustainable development goals and provide valuable insights for policymakers, practitioners, and researchers in developing countries.
Based on the findings, the following recommendations are made to enhance the effectiveness of WDM in developing countries:
Promote participatory approaches: The government should prioritize participatory approaches to WDM involving community members in decision-making. WDM thrives on community involvement. Local residents hold valuable knowledge of the land and its resources, fostering more effective solutions. When communities participate in decision-making, they become invested in the project’s success, ensuring its long-term viability. Participatory approaches consider the diverse needs of various stakeholders within a watershed, leading to fairer solutions. By empowering communities to manage their resources, these projects promote sustainability and local ownership. Despite these challenges, this research overwhelmingly supports participatory approaches for effective WDM.
Promote integrated approaches: The government should promote integrated WDM approaches that recognize the interconnectedness of environmental, social, and economic factors. Integrated watershed management (IWM) is a highly regarded approach in academic discussions. It acknowledges that environmental, social, and economic factors within a watershed are intricately linked. Land use impacts water quality, economic activities affect social justice, and environmental health influences livelihoods. The IWM avoids treating these factors in isolation. This holistic approach fosters sustainable solutions that consider all aspects of the watershed, balancing environmental protection with economic development and social well-being. Furthermore, IWM allows flexible solutions that can adapt to changing circumstances, making it a valuable tool for effective WDM according to the findings of this study.
Invest in capacity building: The government and development partners should invest in capacity-building programs to enhance the skills and knowledge of stakeholders involved in WDM. Capacity building is a cornerstone concept in academic discussions on WDM. Equipping stakeholders with the necessary skills and knowledge is crucial. Training programs on various WDMPs, monitoring techniques on watershed resources, and project management empower participants to be more effective. This translates to improved decision-making as stakeholders gain the ability to analyse complex issues and data. Furthermore, capacity building fosters long-term sustainability by equipping stakeholders with the skills to manage and maintain watershed projects. This study highlights that investing in human resources strengthens not only individual capabilities but also the overall capacity for effective and sustainable WDM.
Improving monitoring and evaluation: The government should establish a robust monitoring and evaluation system to track the effectiveness of WDM interventions and inform policy decisions. Robust monitoring and evaluation systems are championed for WDM. They provide the data needed for evidence-based decision-making. By tracking the effectiveness of interventions, policymakers can see what works and adapt future strategies accordingly. Monitoring and evaluation also allows for early identification of challenges, enabling course correction before problems become entrenched. Furthermore, it fosters accountability by tracking progress towards goals and ensuring that resources are used effectively. Monitoring environmental indicators allows for the assessment of long-term sustainability, a crucial aspect of successful WDM. This study confirms the importance of well-designed monitoring and evaluation systems. These systems ensure that interventions achieve their goals and pave the way for ongoing improvements in WDM strategies.
Strengthening legal frameworks: The government should review existing legal frameworks and develop new ones that promote sustainable WDMPs. Robust legal frameworks establish clear guidelines for water use, pollution control, and land management practices, reducing uncertainty and promoting responsible behaviour. Enforcement mechanisms such as permits and penalties deter unsustainable practices and ensure compliance with regulations. Furthermore, clear legal frameworks regarding water rights and responsibilities encourage practices that conserve and protect watersheds, promoting long-term sustainability. By ensuring equitable water distribution and preventing conflicts between stakeholders, a well-crafted legal framework fosters fairness within the watershed. This research highlights the importance of reviewing existing laws and developing new ones to create a strong legal foundation for sustainable WDM.
In general, by implementing these recommendations, developing countries such as Ethiopia could enhance the effectiveness of watershed management interventions and promote sustainable development in rural areas.
The authors declare that the data will be made available upon request.
Not applicable.
Safi A, et al. Can sustainable resource management overcome geopolitical risk? Resour Policy. 2023;87: 104270.
Article Google Scholar
Lu C, Wang K. Natural resource conservation outpaces and climate change: roles of reforestation, mineral extraction, and natural resources depletion. Resour Policy. 2023;86: 104159.
Byaro M, Nkonoki J, Mafwolo G. Exploring the nexus between natural resource depletion, renewable energy use, and environmental degradation in sub-Saharan Africa. Environ Sci Pollut Res. 2023;30(8):19931–45.
Abbass K, et al. A review of the global climate change impacts, adaptation, and sustainable mitigation measures. Environ Sci Pollut Res. 2022;29(28):42539–59.
Mekuria W, et al. The role of landscape management practices to address natural resource degradation and human vulnerability in Awash River basin, Ethiopia. Curr Res Environ Sustain. 2023;6: 100237.
Independent Evaluation Group. The natural resource degradation and vulnerability nexus. Washington, DC: World Bank; 2021.
Book Google Scholar
World Bank. World development report 2019: the changing nature of work. Washington, DC: The World Bank; 2018.
Google Scholar
Baloch MA, Khan SU-D, Ulucak ZŞ. Poverty and vulnerability of environmental degradation in sub-Saharan African countries: what causes what? Struct Change Econ Dyn. 2020;54:143–9.
Bedeke SB. Climate change vulnerability and adaptation of crop producers in sub-Saharan Africa: a review on concepts, approaches and methods. Environ Dev Sustain. 2023;25(2):1017–51.
Yigezu Wendimu G. The challenges and prospects of Ethiopian agriculture. Cogent Food Agric. 2021;7(1):1923619.
Fenta AA, et al. Land susceptibility to water and wind erosion risks in the East Africa region. Sci Total Environ. 2020;703: 135016.
Article CAS Google Scholar
Taddese G. Land degradation: a challenge to Ethiopia. Environ Manag. 2001;27:815–24.
Wassie SB. Natural resource degradation tendencies in Ethiopia: a review. Environ Syst Res. 2020;9(1):1–29.
Asnake B. Land degradation and possible mitigation measures in Ethiopia: a review. J Agric Ext Rural Dev. 2024;23–9.
Godana G, Legesse B. Assessment of the socioeconomic impact of soil erosion: the case of Dire and Dugda Dawa districts, southern Ethiopia. J Trop Agric. 2022;60(1):1–12.
Mesene M. Extent and impact of land degradation and rehabilitation strategies: Ethiopian highlands. J Environ Earth Sci. 2017;7(11):22–32.
Bantider A, et al. From land degradation monitoring to landscape transformation: four decades of learning, innovation and action in Ethiopia. 2019;19.
Hurni H, et al. Land degradation and sustainable land management in the highlands of Ethiopia. 2010.
Tizale CY. The dynamics of soil degradation and incentives for optimal management in the Central Highlands of Ethiopia. Pretoria: University of Pretoria; 2007.
Gessesse B, Bewket W. Drivers and implications of land use and land cover change in the central highlands of Ethiopia: evidence from remote sensing and socio-demographic data integration. Ethiop J Soc Sci Humanit. 2014;10(2):1–23.
Abi M, et al. Enabling policy and institutional environment for scaling-up sustainable land management in Central Highlands of Ethiopia. Ethiop J Dev Res. 2021;43(1):21–50.
Wani SP, Garg KK. Watershed management concept and principles. 2009.
Lotspeich FB. Watersheds as the basic ecosystem: this conceptual framework provides a basis for a natural classification system 1. J Am Water Resour Assoc. 1980;16(4):581–6.
Knox A, Gupta S. CAPRi technical workshop on watershed management institutions: a summary paper. 2000.
Swallow BM, Johnson NL, Meinzen-Dick RS. Working with people for watershed management. No longer published by Elsevier; 2002. p. 449–55.
Mayer A, Winkler R, Fry L. Classification of watersheds into integrated social and biophysical indicators with clustering analysis. Ecol Ind. 2014;45:340–9.
Wang G, et al. Integrated watershed management: evolution, development and emerging trends. J For Res. 2016;27:967–94.
Abbaspour KC, et al. Modelling hydrology and water quality in the pre-alpine/alpine Thur watershed using SWAT. J Hydrol. 2007;333(2–4):413–30.
Kerr J. Watershed management: lessons from common property theory. Int J Commons. 2007;1(1):89–109.
France RL. Introduction to watershed development: understanding and managing the impacts of sprawl. Lanham: Rowman & Littlefield; 2006.
Wani SP, Venkateswarlu B, Sharda V. Watershed development for rainfed areas: concept, principles, and approaches. Integrated watershed management in rainfed agriculture. Balkema Book. CRC Press. 2011; 53-86.
FAO. Climate change and food security: risks and responses. Rome: FAO; 2015.
Misra AK. Climate change and challenges of water and food security. Int J Sustain Built Environ. 2014;3(1):153–65.
Wani S, et al. Community watersheds for food security and coping with impacts of climate change in rain-fed areas. 2010.
Srivastava PK, et al. Concepts and methodologies for agricultural water management. In: Agricultural water management. Amsterdam: Elsevier; 2021. p. 1–18.
Wani S, et al. Community watersheds for improved livelihoods through consortium approach in drought prone rainfed areas. J Hydrol Res Dev. 2008;23:55–77.
Siraw Z, Adnew Degefu M, Bewket W. The role of community-based watershed development in reducing farmers’ vulnerability to climate change and variability in the northwestern highlands of Ethiopia. Local Environ. 2018;23(12):1190–206.
Hassan AA. Strategies for out-scaling participatory research approaches for sustaining agricultural research impacts. Dev Pract. 2008;18(4–5):564–75.
Perez C, Tschinkel H. Improving watershed management in developing countries: a framework for prioritising sites and practices. London: Overseas Development Institute; 2003.
UN. Transforming our world: the 2030 agenda for sustainable development. United Nations; 2016.
Gupta AK, Goyal MK, Singh S. Ecosystem restoration: towards sustainability and resilient development. Springer Nature: Singapore; 2023.
FAO. The state of food and agriculture 2018: migration, agriculture and rural development. UN; 2018.
MoALR. Integrated watershed development strategy of Ethiopia. Addis Ababa: Ministry of Agriculture and Livestock Resources; 2018.
MoA. Community based participatory watershed and rangeland development: a guideline. Addis Ababa: Ministry of Agriculture; 2020.
Lakew D, et al. Community based participatory watershed development: a guidelines. Part 1. Addis Ababa: Ministry of Agricultural Rural Development; 2005.
Gashaw T. The implications of watershed management for reversing land degradation in Ethiopia. Res J Agric Environ Manag. 2015;4(1):5–12.
Gobena T, et al. Watershed management intervention on land use land cover change and food security improvement among smallholder farmers in Qarsa Woreda, East Hararge zone, Ethiopia. Acta Agriculturae Scandinavica Sect B Soil Plant Sci. 2024;74(1):2281922.
Fikadu G, Olika G. Impact of land use land cover change using remote sensing with integration of socio-economic data on rural livelihoods in the Nashe watershed, Ethiopia. Heliyon. 2023;9(3): e13746.
Dejene A. Integrated natural resources management to enhance food security. The case for community-based approaches in Ethiopia. Environment and natural resources. Working Paper (FAO). 2003.
Argaw T, Abi M, Abate E. The impact of watershed development and management practices on rural livelihoods: a structural equation modeling approach. Cogent Food Agric. 2023;9(1):2243107.
Siraw Z, Bewket W, AdnewDegefu M. Assessment of livelihood benefits of community-based watershed development in northwestern highlands of Ethiopia. Int J River Basin Manag. 2020;18(4):395–405.
Mekuriaw A, Amsalu T. Assessing the effectiveness of community-based watershed management practices in reversing land degradation in the Finchwuha watershed, Gojjam, Ethiopia. Int J River Basin Manag. 2023;21(4):697–709.
Moges DM, Bhat HG. Watershed degradation and management practices in north-western highland Ethiopia. Environ Monit Assess. 2020;192:1–15.
Gumma MK, et al. Assessing the impacts of watershed interventions using ground data and remote sensing: a case study in Ethiopia. Int J Environ Sci Technol. 2022;19(3):1653–70.
James W. Pragmatism: a new way for some old ways of thinking. London: Longmans, Green; 1916.
Kloppenberg JT. Pragmatism: an old name for some new ways of thinking? J Am Hist. 1996;83(1):100–38.
Dewey J. What does pragmatism mean by practical? J Philos Psychol Sci Methods. 1908;5(4):85–99.
Almeder R. A definition of pragmatism. Hist Philos Q. 1986;3(1):79–87.
Rorty R. Pragmatism, relativism, and irrationalism. In: The new social theory reader. London: Routledge; 2020. p. 147–55.
Chapter Google Scholar
Capps J. The pragmatic theory of truth. 2019.
Dewey A, Drahota A. Introduction to systematic reviews: online learning module Cochrane training. 2016.
Xiao Y, Watson M. Guidance on conducting a systematic literature review. J Plan Educ Res. 2019;39(1):93–112.
Poonia T, Singh G. Watershed management and development—a review. Agric Rev. 2004;25(2):147–51.
Worku T, Tripathi SK. Watershed management in highlands of Ethiopia: a review. Open Access Libr J. 2015;2(6):1–11.
Abebaw WA. Review on the role of integrated watershed management for rehabilitating degraded land in Ethiopia. Environment. 2019. https://doi.org/10.7176/JBAH/9-11-02 .
Zhang J, et al. Analysis on common problems of the wastewater treatment industry in urban China. Chemosphere. 2022;291: 132875.
Ellis F. Rural livelihoods and diversity in developing countries. Oxford: Oxford University Press; 2000.
Scoones I. Sustainable rural livelihoods: a framework for analysis. Brighton: Institute of Development Studies; 1998.
Kumar V, Wankhede K, Gena H. Role of cooperatives in improving livelihood of farmers on sustainable basis. Am J Educ Res. 2015;3(10):1258–66.
Bingen J, Serrano A, Howard JJFP. Linking farmers to markets: different approaches to human capital development. Food Policy. 2003;28(4):405–19.
Solesbury W. Sustainable livelihoods: a case study of the evolution of DFID policy. London: Overseas Development Institute; 2003.
Chambers R, Conway G. Sustainable rural livelihoods: practical concepts for the 21st century. Brighton: Institute of Development Studies; 1992.
DfID, U.J.L.D. Sustainable livelihoods guidance sheets . 1999;445.
Rakodi C. A capital assets framework for analysing household livelihood strategies: implications for policy. Dev Policy Rev. 1999;17(3):315–42.
Katz EG. Social capital and natural capital: a comparative analysis of land tenure and natural resource management in Guatemala. Land Econ. 2000;76:114–32.
Ninan K, Lakshmikanthamma S. Social cost-benefit analysis of a watershed development project in Karnataka, India. Ambio. 2001;30:157–61.
Dessalegn M, Ashagrie E. Determinants of rural household livelihood diversification strategy in South Gondar Zone, Ethiopia. J Agric Econ Ext Rural Dev. 2016;4(8):548–60.
Mengistu F, Assefa E. Enhancing livelihood assets of households through watershed management intervention program: case of upper Gibe basin, Southwest Ethiopia. Environ Dev Sustain. 2020;22(8):7515–46.
Yehun TS. Impact of watershed development on livelihood of rural farm households; in case of Burie zuria district, North West Ethiopia. 2020.
Chot G, Moges A, Shewa A. Impacts of soil and water conservation practices on livelihood: the case of watershed in Gambela region, Ethiopia. Afr J Environ Sci Technol. 2019;13(6):241–52.
Mulugeta S, Krishnaiah P. Community based watershed development from sustainable livelihood perspective: a case analysis in north Gondar zone. ZENITH Int J Multidiscip Res. 2015;5(5):18–31.
Teka K, et al. Can integrated watershed management reduce soil erosion and improve livelihoods? A study from northern Ethiopia. Int Soil Water Conserv Res. 2020;8(3):266–76.
Chisholm N, Woldehanna T. Managing watersheds for resilient livelihoods in Ethiopia. Dis Colon Rectum. 2012. https://doi.org/10.1787/dcr-2012-15-en .
Scoones I. Livelihoods perspectives and rural development. J Peasant Stud. 2009;36(1):171–96.
Tyler SR, IDR Centre. Communities, livelihoods and natural resources: action research and policy change in Asia. Ottawa: International Development Research Centre; 2006.
Emery M, Gutierrez-Montes I, Fernandez-Baca E. Sustainable rural development: sustainable livelihoods and the community capitals framework. London: Taylor & Francis; 2016.
MEA. Millennium ecosystem assessment . Ecosystems; 2003.
Adger WN. Social capital, collective action, and adaptation to climate change. Der klimawandel: Sozialwissenschaftliche perspektiven; 2010. p. 327–45.
Dasgupta P. An inquiry into well-being and destitution. Oxford: Clarendon Press; 1993.
Pretty J, Ward H. Social capital and the environment. World Dev. 2001;29(2):209–27.
World Bank. Sustainable land management: challenges, opportunities, and trade-offs. Washington DC: The World Bank; 2006.
Bhattacherjee A. Social science research: principles, methods, and practices. Tampa: University of South Florida; 2012.
Narendra BH, et al. A review on sustainability of watershed management in Indonesia. Sustainability. 2021;13(19):11125.
Nugroho HYSH, et al. Toward water, energy, and food security in rural Indonesia: a review. Water. 2022;14(10):1645.
Descheemaeker K, et al. Effects of integrated watershed management on livestock water productivity in water scarce areas in Ethiopia. Phys Chem Earth Parts A/B/C. 2010;35(13–14):723–9.
Mengistu F, Assefa E. Towards sustaining watershed management practices in Ethiopia: a synthesis of local perception, community participation, adoption and livelihoods. Environ Sci Policy. 2020;112:414–30.
Alemu B, Kidane D. The implication of integrated watershed management for rehabilitation of degraded lands: case study of Ethiopian highlands. J Agric Biodivers Res. 2014;3(6):78–90.
Carswell G. Agricultural intensification and rural sustainable livelihoods: a think piece. Brighton: Institute of Development Studies Brighton; 1997.
Romer PM. Human capital and growth: theory and evidence. Cambridge: National Bureau of Economic Research Cambridge; 1989.
Bernstein H. Modernization theory and the sociological study of development. J Dev Stud. 1971;7(2):141–60.
Sen A. Development as freedom. Oxford: Oxford University Press; 1999.
Becker GS, Murphy KM. A theory of rational addiction. J Polit Econ. 1988;96(4):675–700.
Stevens RD, Jabara CL. Agricultural development principles: economic theory and empirical evidence. Baltimore: Johns Hopkins University Press; 1988.
Aredo D. Agricultural development: theory, policy, and practice. 2011.
Turton C. Enhancing livelihoods through participatory watershed development in India. London: Overseas Development Institute London; 2000.
Fisher M, Chaudhury M, McCusker B. Do forests help rural households adapt to climate variability? Evidence from southern Malawi. World Dev. 2010;38(9):1241–50.
Mondal B, Loganandhan N. Employment generation potential of watershed development programmes in semi-arid tropics of India. Afr J Agric. 2013;8(23):2948–55.
Dile YT, et al. The role of water harvesting to achieve sustainable agricultural intensification and resilience against water related shocks in sub-Saharan Africa. Agr Ecosyst Environ. 2013;181:69–79.
Kohun PJ, Waramboi JG. Integrating crops with livestock to maximise output of smallholder farming systems. Food Secur P N G. 2001;11:656.
Ratna Reddy V, et al. Participatory watershed development in India: can it sustain rural livelihoods? Dev Change. 2004;35(2):297–326.
Adimassu Z, Langan S, Barron J. Highlights of soil and water conservation investments in four regions of Ethiopia, vol. 182. Colombo: International Water Management Institute (IWMI); 2018.
Tilahun G, Bantider A, Yayeh D. Impact of adoption of climate-smart agriculture on food security in the tropical moist montane ecosystem: the case of Geshy watershed, Southwest Ethiopia. Heliyon. 2023;9(12): e22620.
Palanisami K, Kumar DS. Impacts of watershed development programmes: experiences and evidences from Tamil Nadu. Agric Econ Res Rev. 2009;22:387–96.
Kerr J. Watershed development, environmental services, and poverty alleviation in India. World Dev. 2002;30(8):1387–400.
Hope R. Evaluating social impacts of watershed development in India. World Dev. 2007;35(8):1436–49.
Hassan M, et al. A review of watershed management in Bangladesh: options, challenges and legal framework. J Mater Environ Sci. 2024;15(2):225, 241.
Ibrahim AZ, et al. Examining the livelihood assets and sustainable livelihoods among the vulnerability groups in Malaysia. Indian-Pac J Account. 2017;1(3):52–63.
Surya B, et al. Natural resource conservation based on community economic empowerment: perspectives on watershed management and slum settlements in Makassar City, South Sulawesi, Indonesia. Land. 2020;9(4):104.
Herrera D, et al. Upstream watershed condition predicts rural children’s health across 35 developing countries. Nat Commun. 2017;8(1):811.
Norton A, et al. Harnessing employment-based social assistance programmes to scale up nature-based climate action. Philos Trans R Soc B. 2020;375(1794):20190127.
Adeniran A, Daniell KA, Pittock J. Water infrastructure development in Nigeria: trend, size, and purpose. Water. 2021;13(17):2416.
Mello I, et al. Sustainable land management with conservation agriculture for rainfed production: the case of Paraná III watershed (Itaipu dam) in Brazil. Rainfed systems intensification and scaling of water and soil management: four case studies of development in family farming; 2023. p. 99–126.
Bremer LL, et al. Who are we measuring and modeling for? Supporting multilevel decision-making in watershed management. Water Resour Res. 2020;56(1): e2019WR026011.
Ferraro PJ. Regional review of payments for watershed services: sub-Saharan Africa. J Sustain For. 2009;28(3–5):525–50.
Tesfaye A, et al. Assessing the costs and benefits of improved land management practices in three watershed areas in Ethiopia. Int Soil Water Conserv Res. 2016;4(1):20–9.
Gebregziabher G, et al. An assessment of integrated watershed management in Ethiopia. Addis Ababa: International Water Management Institute (IWMI); 2016.
Tansey G, Worsley A. The food system. London: Routledge; 2014.
Maxwell S, Frankenberger T. Household food security: concepts, indicators, measurements . A Technical; 1992.
Wani SP, Sudi R, Pathak P. Sustainable groundwater development through integrated watershed management for food security. Bhu-Jal News Q J. 2009;24(4):38–52.
Degefa T. Household seasonal food insecurity in Oromiya zone: causes. organization for social science research in eastern and southern Africa (OSSREA) research report. 2002(26).
Limaye SD. Watershed management for sustainable water supply and food security. International journal of hydrology. 2019; 3(1):1. DOI: 10.15406/ijh.2019.03.00153
Dar WD, Wani SP. Improving livelihoods and resilience through community watersheds. Rural 21 Int J Rural Dev. 2012;21(4):1–4.
Wani S, Garg K. Restoring lands and livelihoods in rain fed areas through community watershed management. In: Living land. New York: UNCCD; 2015. p. 97–100.
Wani SP, Rockstroma J. Watershed development as a growth engine for sustainable development of rainfed areas. 2011.
Pande CB. Watershed management and development. In: Sustainable watershed development. Cham: Springer; 2020. p. 13–26.
Kato E, et al. Sustainable land management and its effects on water security and poverty: evidence from a watershed intervention program in Ethiopia, vol. 1811. Washington DC: Intl Food Policy Res Inst; 2019.
Gebregziabher G, et al. An assessment of integrated watershed management in Ethiopia. Working paper 170. Colombo: International Water Management Institute (IWMI); 2016.
Naji TA, AbiTeka M, Alemu EA. The impact of watershed on household food security: a comparative analysis. J Agric Food Res. 2024;15: 100954.
Katusiime J, Schütt B. Linking land tenure and integrated watershed management—a review. Sustainability. 2020;12(4):1667.
Tyagi S, Datta P, Singh R. Need for proper water management for food security. Curr Sci. 2012;102:690–5.
Sam AS, et al. Flood vulnerability and food security in eastern India: a threat to the achievement of the sustainable development goals. Int J Disaster Risk Reduct. 2021;66: 102589.
Asefa K. Farm household opinions of productive safety net program of integrated watershed management and its effect on food security in Beyeda Woreda: a case of Key Amba micro-watershed, north western Ethiopia. 2022, uog.
Healy T. Social capital: old hat or new insight? Ir J Sociol. 2004;13(1):5–28.
Uphoff N. Understanding social capital: learning from the analysis and experience of participation. Soc Cap Multifaceted Perspect. 2000;6(2):215–49.
Agidew A-MA, Singh K. Factors affecting farmers’ participation in watershed management programs in the Northeastern highlands of Ethiopia: a case study in the Teleyayen sub-watershed. Ecol Process. 2018;7(1):1–15.
Bagherian R. Community participation in watershed management programs. J Soc Sci. 2009;5(3):251–6.
Indrawati D, et al. Community participation in soil and water conservation as a disaster mitigation effort. In: IOP conference series: earth and environmental science. IOP Publishing; 2022.
Naji TA, Abi Teka M, Alemu EA. Level of communities’ participation in the watershed development and management practices in the central highlands of Ethiopia. Rev Socio-Econ Res Dev Stud. 2023;7(2):36–60.
Pretty JN. Participatory learning for sustainable agriculture. World Dev. 1995;23(8):1247–63.
Mukerjee A. Lake watershed management in developing countries through community participation: a model. In: Proceedings of the 11th World Lakes conference—proceedings. 2006.
Bewket W, Sterk G. Farmers’ participation in soil and water conservation activities in the Chemoga watershed, Blue Nile basin, Ethiopia. Land Degrad Dev. 2002;13(3):189–200.
Pandey HP, Pokhrel NP. Formation trend analysis and gender inclusion in community forests of Nepal. Trees For People. 2021;5: 100106.
Baral D, et al. Participation of community in prevention and control of dengue fever in Dharan Sub Metropolitan City of Province No 1, Nepal. J Nobel Med College. 2020;9(2):28–33.
Hinchcliffe F, et al. The economic, social and environmental impacts of participatory watershed development. Gatekeeper Series. 1995;50.
Ostrom E. Governing the commons: the evolution of institutions for collective action. Cambridge: Cambridge University Press; 1990.
Ostrom E. Background on the institutional analysis and development framework. Policy Stud J. 2011;39(1):7–27.
Agrawal A. Accountability in decentralization: a framework with South Asian and West African cases. J Dev Areas. 1999;33(4):473–502.
Baland J-M, Platteau J-P. Halting degradation of natural resources: is there a role for rural communities? Rome: Food & Agriculture Org; 1996.
Cleaver F. Paradoxes of participation: questioning participatory approaches to development. J Int Dev J Dev Stud Assoc. 1999;11(4):597–612.
Armitage D, Marschke M, Plummer R. Adaptive co-management and the paradox of learning. Glob Environ Change. 2008;18(1):86–98.
Lamichhane P. Resilience and adaptation to climate change in smallholder agriculture in Nepal. Geelong: Deakin University; 2021.
Lebel L, et al. Governance and the capacity to manage resilience in regional social-ecological systems. Ecol Soc. 2006;11(1):21.
Hassan R, Scholes R, Ash N. Ecosystems and human well-being: current state and trends. Washington, DC: Island Press; 2005.
Tiwari KR, et al. Determinants of farmers’ adoption of improved soil conservation technology in a middle mountain watershed of central Nepal. Environ Manag. 2008;42:210–22.
Bandiera O, Rasul I. Social networks and technology adoption in northern Mozambique. Econ J. 2006;116(514):869–902.
Bezu S, Holden S. Are rural youth in Ethiopia abandoning agriculture? World Dev. 2014;64:259–72.
Davis K, et al. Impact of farmer field schools on agricultural productivity and poverty in East Africa. World Dev. 2012;40(2):402–13.
Roba Gamo B, et al. Determinants of community participation in a watershed development program in southern Ethiopia. Community Dev. 2022;53(2):150–66.
Oyetunde-Usman Z, Olagunju KO, Ogunpaimo OR. Determinants of adoption of multiple sustainable agricultural practices among smallholder farmers in Nigeria. Int Soil Water Conserv Res. 2021;9(2):241–8.
Mengistu F, Assefa E. Community participation in watershed management: analysis of the status and factors affecting community engagement in the upper Gibe basin, South West Ethiopia. J Environ Plan Manag. 2021;64(2):252–88.
Robbins P. Political ecology: a critical introduction. Hoboken: John Wiley & Sons; 2019.
Peet R, Watts M. Liberation ecologies: environment, development and social movements. London: Routledge; 2004.
Lejano R. Frameworks for policy analysis: merging text and context. London: Routledge; 2013.
Montgomery DR, Grant GE, Sullivan K. Watershed analysis as a framework for implementing ecosystem management 1. J Am Water Resour Assoc. 1995;31(3):369–86.
Pambudi AS. Watershed management in Indonesia: a regulation, institution, and policy review. Jurnal Perencanaan Pembangunan: Indones J Dev Plan. 2019;3(2):185–202.
Gebregergs T, et al. Status and challenges of integrated watershed management practices after-project phased-out in Eastern Tigray, Ethiopia. Model Earth Syst Environ. 2021;8:1–7.
Bruch C, et al. From theory to practice: An overview of approaches to involving the public in international watershed management. Public participation in the governance of international freshwater resources. 2005;3.
Sharma BR, Scott CA. Watershed management challenges: introduction and overview . Watershed management challenges. 2005. p. 1.
Kalantari K, Maknoon R, Karimi D. Developing sustainable legal framework for the establishment of integrated water resources management in Iran. Int J Environ Res. 2018;12:223–31.
Mireku O, Mensah A. Policy interventions in watershed management: the case of the Inchaban Watershed, Ghana. Int J Water Resour Environ Eng. 2015;7(3):38–49.
Ajai O. Law, water and sustainable development: framework of Nigerian law. Law Env’t Dev J. 2012;8:89.
Bjornlund H, McKay J. Elements of an institutional framework for the management of water for poverty reduction in developing countries. In: Water development and poverty reduction. Cham: Springer; 2003. p. 87–110.
Wani SP, Ramakrishna Y. Sustainable management of rainwater through integrated watershed approach for improved rural livelihoods. 2005.
Wani SP, et al. Enhancing agricultural productivity and rural incomes through sustainable use of natural resources in the Semi Arid Tropics. J Sci Food Agric. 2012;92(5):1054–63.
Yoganand B, Gebremedhin TG. Participatory watershed management for sustainable rural livelihoods in India. 2006.
Habtu S. Revitalizing key conditions and integrated watershed management approach to sustain water availability and agriculture in semi-arid regions . 2023.
Download references
The authors declare that there was no funding to conduct this study.
Authors and affiliations.
Center for Food Security, College of Development Studies, Addis Ababa University, Addis Ababa, Ethiopia
Temesgen Argaw Naji & Meskerem Abi Teka
Center for Rural Development, College of Development Studies, Addis Ababa University, Addis Ababa, Ethiopia
Esubalew Abate Alemu
You can also search for this author in PubMed Google Scholar
Temesgen Argaw Naji: conceptualization, investigation, data collection, formal analysis, methodology, software, and writing of the original draft. Meskerem Abi Teka (Ph.D.): resources, supervision, writing—review and editing, and validation. Esubalew Abate Alemu (Ph.D.): resources, supervision, writing—review and editing, and validation.
Correspondence to Temesgen Argaw Naji .
Competing interests.
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this study.
Publisher's note.
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Literatures’ title, authors, and date | Region | Main findings |
---|---|---|
Sustainable management of rainwater through integrated watershed approach for improved rural livelihoods S. Wani, Y. Ramakrishna 2005 | India | Rain-filled areas struggle with water shortages, poor soil, and inefficient water use. ICRISAT’s watershed approach tackles these issues using sustainable methods to boost farm yields and improve lives in rural areas. Their model focuses on water scarcity, poverty, and water use efficiency to create a more productive and secure food supply for these regions |
Development, integration and dissemination of resource conservation options through community watershed approach S. Wani, T. Sreedevi, P. Joshi, B. Venkateswarlu 2009 | India | Watershed approach can be applied in all rainfed areas with suitable modifications to upgrade economically beneficial agriculture. Adopting a community watershed management approach can unlock the potential of rainfed agriculture through various strategies like linking farmers to markets and enhancing community participation. Capacity building is crucial for scaling up watershed programs, and a national strategy with quality service providers is recommended |
Watershed management and development—a review T. C. Poonia, G. D. Singh 2004 | India | Key findings include the importance of local participation in watershed management, the need for cost-effective and sustainable technologies through client involvement, and the transition towards community-driven strategies |
Watershed management for sustainable water supply and food security S. Limaye 2019 | India | Well-maintained and well-forested watersheds are essential for providing a resilient interface between climate and water resources, and field-level actions should start in the watershed of a first-order stream with community involvement |
The impact of watershed development and management practices on rural livelihoods: a structural equation modelling approach T. Argaw, M. Abi and E. Abate 2023 | Ethiopia | Putting watershed management plans into action led to several positive outcomes. These included a boost in farm yields and incomes for the community, creation of new jobs, and upgrades to social services and infrastructure |
Participatory watershed management for sustainable rural livelihoods in India B. Yoganand, T. Gebremedhin 2006 | India | The main findings include the shift in international development goals towards poverty reduction and environmental protection, the challenges posed by natural resource degradation and population pressure in developing countries leading to food insecurity and environmental degradation, and the proposal of a participatory watershed management approach as an effective solution |
A watershed approach to upgrade rainfed agriculture in water scarce regions through Water System Innovations: an integrated research initiative on water for food and rural livelihoods in balance with ecosystem functions J. Rockström, C. Folke, L. Gordon, N. Hatibu, G. Jewitt, F. P. De Vries, et al. 2004 | Tanzania, South Africa | The research program "Smallholder System Innovations in Integrated Watershed Management" (SSI) aims to address the challenges of increasing food production, improving rural livelihoods, and safeguarding critical ecological functions through an integrated approach to agricultural water management. The program focuses on analysing the interactions between the adoption of water system innovations, increased water use in agriculture, and water flows to sustain ecological functions in order to deliver critical ecosystem services to humans |
Efficient management of water resources for improving the livelihoods through integrated watershed management approach Z. Li, Y. Dixin, Z. Yingcui, Z. Hongye, Y. Guangyuan, T. Rego, et al. 2005 | China | The study emphasizes the importance of watershed management in addressing soil erosion, water scarcity, and land degradation in Southwest China, as part of the West Development Strategy |
Improving livelihoods and resilience through community watersheds W. Dar, S. Wani 2012 | India | Watershed programmes with active rural participation can ensure food security, contribute to economic growth, and help conserve natural resources in dryland tropics. The ICRISAT programme in India exemplifies a science-led, knowledge-based approach in this field |
Improving livelihoods through watershed interventions: a case study of SABMiller India project R. N. Rajesh Nune, C. S. Rao, R. Sudi, S. Wani, K. Garg and D. Rao 2018 | India | The main finding is the importance of water in addressing water scarcity, land degradation, and improving crop and livestock productivity in the semiarid tropical region |
Community watersheds for food security and coping with impacts of climate change in rain-fed areas S. Wani, T. Wangkahart, D. Y. Dixin Yin, L. Z. Li Zhong and N. Thang 2010 | India, China, Thailand, Vietnam | The community watershed approach has resulted in increasing agricultural productivity by 2 to 3 folds, doubling the family incomes, and reducing runoff up to 66% and soil loss by 2/3 rd |
Restoring lands and livelihoods in rain fed areas through community watershed management S. Wani and K. Garg 2015 | India, China, Thailand | The main findings include the challenge of ensuring food security and reducing poverty for a growing global population, the necessity of increased food production from limited resources, and the acute water scarcity in developing countries |
Watershed development as a growth engine for sustainable development of rainfed areas S. P. Wani and J. Rockstroma 2011 | Africa, South Asia | The urgent challenge of achieving food security while balancing development and sustainability is highlighted. Agriculture will remain crucial for economies in Africa and South Asia despite changing factors like growing incomes and urbanization |
Enhancing agricultural productivity and rural incomes through sustainable use of natural resources in the semi arid tropics S. P. Wani, Y. Dixin, Z. Li, W. D. Dar and G. Chander 2012 | Thailand, India | Enhanced productive transpiration improved rainwater use efficiency, watershed interventions increased net returns from crop production, and household incomes substantially increased |
A new paradigm in watershed management: a must for development of rainfed areas for inclusive growth S. P. Wani, P. Joshi, Y. Ramakrishna, T. Sreedevi, P. Singh and P. Pathak 2008 | India | Watershed management can significantly increase agricultural productivity and rural family income, requiring new approaches, policies, and investments to achieve sustainable development goals and establish India as a leader in the field |
Watershed management programs for increasing land productivity and appropriate withdrawal strategies for long term sustainability in rain fed lands of India G. Sastry, O. Prakash, Y. Reddy and H. Singh 2002 | India | Watershed management increases and sustains land productivity without damaging natural resources, emphasizing decentralization, flexibility, and community involvement for sustainability. Sustaining watershed management post withdrawal is crucial for optimal land productivity |
Community based watershed development from sustainable livelihood perspective: a case analysis in north Gondar zone S. Mulugeta and P. Krishnaiah 2015 | Ethiopia | Community-based watershed development has led to improvements in natural resources in the area |
Watershed-based development for rural prosperity—evidence from Kerala K. J. Thomas, K. S. Babu and E. Thomas 2009 | Kerala, India | The watershed development program in the Elanad watershed in Kerala resulted in increased adoption of soil conservation and water-harvesting techniques, leading to improved water resources, groundwater recharge, and higher crop productivity and farm income |
Sustainable groundwater development through integrated watershed management for food security S. P. Wani, R. Sudi and P. Pathak 2009 | India | Integrated watershed development is crucial for sustainable development in dry land areas, managing rainwater effectively improves groundwater availability, and increased water availability positively impacts women’s welfare and the environment |
Integrated watershed management for natural resource conservation and livelihood security in semiarid tropics of India D. Palsaniya, R. Singh, R. Tewari, R. Yadav and S. Dhyani 2012 | India | The integrated watershed management interventions led to improvements in water storage, reduced soil loss, increased crop productivity and fodder availability, and decreased migration rates due to enhanced employment opportunities |
Community watersheds for sustainable development and improved livelihoods in dryland areas of Asia S. Wani, T. Sreedevi, T. Wangkahart and Y. Dixin 2009 | India, Asia | The importance of the watershed approach in India is emphasized by substantial investments, while the assessment revealed the necessity for community watersheds to address multiple aspects for sustainable development |
The impact of watershed on household food security: a comparative analysis T. A. Naji, M. Abi Teka and E. A. Alemu 2024 | Ethiopia | WDMPs can significantly improve household food security compared to households not engaged in these practices. This finding highlights the potential of WDM as a strategy to address food insecurity challenges |
An assessment of integrated watershed management in Ethiopia G. Gebregziabher, D. Abera, G. Gebresamuel, M. Giordano and S. Langan 2016 | Ethiopia | Integrated watershed management in Ethiopia increases farmers’ food security and incomes by approximately 50% on average. The impact of watershed management can vary significantly between different programs. Recommendations include tailoring interventions to the local context, combining conservation and livelihood activities, and providing additional support to watershed committees |
The implication of integrated watershed management for rehabilitation of degraded lands: case study of Ethiopian highlands B. Alemu and D. Kidane 2014 | Ethiopia | – Participatory watershed management is crucial for increasing agricultural production, conserving natural resources, and reducing poverty in the Ethiopian highlands – Integration of biological and mechanical soil and water conservation measures has multiple benefits such as enhancing soil fertility, increasing crop yield, providing forage for animals, and serving as a source of fuel wood and construction materials – Challenges in watershed management in Ethiopia include insufficient capacity at different administrative levels, emphasizing the importance of implementing sustainable approaches to address intervention needs |
Assessment of livelihood benefits of community-based watershed development in northwestern highlands of Ethiopia Z. Siraw, W. Bewket and M. Adnew Degefu 2018 | Ethiopia | CBWD has shown significant livelihood benefits in terms of overall livelihood capital indices, with variations in the improvement of different livelihood capitals across different micro watersheds |
Watershed management in highlands of Ethiopia: a review T. Worku and S. K. Tripathi 2015 | Ethiopia | The soil and water conservation program initiated in 1970 in the Ethiopian highlands had limited success due to various reasons, leading to the implementation of a community-based integrated watershed management program by the present government to address these shortcomings |
The implications of watershed management for reversing land degradation in Ethiopia T. Gashaw 2015 | Ethiopia | Watershed management in Ethiopia has led to reduced soil erosion, increased vegetation cover, and improved crop production and productivity |
Effects of integrated watershed management on livestock water productivity in water scarce areas in Ethiopia K. Descheemaeker, E. Mapedza, T. Amede and W. Ayalneh 2010 | Ethiopia | – Protecting 40% of rangelands increased water productivity of feed by approximately 20% – Water harvesting structures provided year-round water availability, reducing energy used for walking to drinking points – Both interventions improved the efficient use of scarce water resources for biomass and livestock production |
Can integrated watershed management reduce soil erosion and improve livelihoods? A study from northern Ethiopia K. Teka, M. Haftu, M. Ostwald and C. Cederberg 2020 | Ethiopia | Integrated watershed management resulted in a 50% reduction in soil loss, increased crop productivity, water availability, fodder availability, and household income, with a higher percentage of households able to cover their annual expenditure demands |
Level of communities’ participation in the watershed development and management practices in the Central Highlands of Ethiopia T. A. Naji, M. Abi Teka and E. A. Alemu 2023 | Ethiopia | The study indicates a moderate level of community participation (approximately 65%) in WDMPs within the central highlands of Ethiopia. This suggests there’s room for improvement in engaging communities more fully in these initiatives |
Managing watersheds for resilient livelihoods in Ethiopia N. Chisholm and T. Woldehanna 2012 | Ethiopia | The integrated watershed management project in Ethiopia led to the regeneration and enhancement of natural resources, improved incomes, food security, and social benefits. The project improved people’s resilience to climate change and contributed to carbon sequestration. The successful approach of the project has been scaled up to the national level, influencing important national policies like the Productive Safety Net Programme and Ethiopia’s Green Economy Strategy |
Review on the role of integrated watershed management for rehabilitation degraded land in Ethiopia W. A. Abebaw 2019 | Ethiopia | Integrated watershed management is crucial for managing natural resources, positive outcomes were observed in the Tigray region, and lack of capacity at government levels is a significant challenge |
Towards sustaining watershed management practices in Ethiopia: a synthesis of local perception, community participation, adoption and livelihoods F. Mengistu and E. Assefa 2020 | Ethiopia | Local communities are aware of watershed degradation, ecological benefits are perceived better in upper areas, and challenges in adoption and community participation exist |
Assessing the costs and benefits of improved land management practices in three watershed areas in Ethiopia A. Tesfaye, R. Brouwer, P. van der Zaag and W. Negatu 2016 | Ethiopia | The study found that implementing soil conservation measures significantly increases productivity and food security in rural Ethiopia, with the benefits outweighing the costs |
Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/ .
Reprints and permissions
Naji, T.A., Teka, M.A. & Alemu, E.A. Enhancing watershed management in developing countries: insights from Ethiopia. Discov Sustain 5 , 131 (2024). https://doi.org/10.1007/s43621-024-00334-y
Download citation
Received : 26 March 2024
Accepted : 20 June 2024
Published : 27 June 2024
DOI : https://doi.org/10.1007/s43621-024-00334-y
Anyone you share the following link with will be able to read this content:
Sorry, a shareable link is not currently available for this article.
Provided by the Springer Nature SharedIt content-sharing initiative
IMAGES
VIDEO
COMMENTS
This paper aims to understand the current research scenario through published studies on corporate sustainability, emphasizing the environmental approach. Methodologically, this research develops a systematic literature review based on papers published in the Web of Science database in the last ten years. As a result, there was an upward evolution of research on the searched topic, with one ...
Abstract. This study aims to analyze the state-of-the-art of sustainable human resources management and to identify key elements, trends and research gaps. A systematic literature review was carried out using Scopus database, covering the period from 2001 to 2018, which resulted in a corpus of 115 scientific articles.
The content analysis helped identify themes like determinants of sustainability, relationship between sustainability and firm performance, and sustainability compliance levels. Future studies may assess the impacts of sustainability on factors other than financial performance, such as earnings management, cost of capital, and market risk, and ...
When reviewing the literature, it is obvious that various definitions of sustainable project management already exist. Tam (2010, p. 176) defines sustainable project management as "the promoting of positive and minimizing of negative sustainability impacts (economic; environmental; and social) within the process by which projects are defined, planned, monitored, controlled and delivered such ...
The pursuit of sustainable development goals (SDGs) extends beyond governmental responsibility, demanding active engagement from businesses and managers. This study systematically reviews SDG-related research within the fields of business and management to elucidate their roles in advancing this global agenda.
Sustainability integration in project portfolio management helps shape strategic, organizational, and project-based contexts. The authors conducted a structured literature review from 2000 to 2021 and developed a novel integrative framework presenting a holistic view highlighting three substantive research themes: sustainability mindset, sustainability assessment, and sustainability ...
The aim of this systematic review is to inspect the recent literature on sustainability management and performance and synthesize the insights it articulates on the urban corporate economy. ... . 2020. "Sustainability Management and Performance in the Urban Corporate Economy: A Systematic Literature Review" Sustainability 12, no. 18: 7705 ...
A systematic extensive literature review was performed to investigate the relationship between stakeholder pressure and sustainable management practices. This literature review shows that organizational factors are more widely covered than the individual and macro-level factors as moderating variables, and suggests more organizational ...
The literature and business practice review has identified a wide range of examples of mechanisms and solutions that can contribute to business model innovation for sustainability.
The objective of this article is to review, from a global perspective, the existing literature regarding sustainable supply chain management (SSCM) in emerging economies. For this purpose, a systematic literature review was performed, analyzing 56 articles from the year 2010 to April 2020 from a descriptive and content approach.
3.1. Sustainable Management The findings of the literature review indicate that the TBL approach is not sufficient to illustrate the sustainable entrepreneurship model. In theory, sustainable management is a vital contributor to sustainable development efforts in general and, therefore, presents
Building on sustainable management theory, 'sustainable human resource management' concept receives significant interest from management, academicians and scholars. ... Materla T., Cudney E. A., & Antony J. (2017). The application of Kano model in the healthcare industry: A systematic literature review. Total Quality Management and Business ...
This article is a literature review in the area of sustainable construction management. This analysis was conducted in three phases, as shown in Fig. 1: quantitative analysis, a stage of meta-analysis where the articles are filtered and clustered for manual bibliometric and VOSviewer analysis, and in the last stage, qualitative analysis was carried out, where two different activities were ...
Design/methodology/approach. The paper presents a comprehensive review of the literature on food sustainable supply chain management (FSSCM). Using systematic review methods, relevant studies published from 1997 to early 2021 are explored to reveal the research landscape and the gaps and trends.
From a similar yet more expansive viewpoint, Tachizawa and Wong investigate the literature on multi-tier SCs and sustainability management of sub-suppliers. Knowledge from 39 studies is consolidated to configure an SSCG framework in which lead firms ground on seven contingency variables to select the appropriate governance mode(s) among ...
s, we identified the areas of impact of sustainability on project management. It appeared t. at considering sustainability impacts project management on different levels. Considering sustainability implies, firstly, a shift of scope in the management of projects: from managing tim. , budget and quality, to managing social.
Keywords Sustainable project management · Systematic literature review · Sustainability · Project management ... 1 Corporate Sustainability Management, University of Erlangen-Nuremberg, Findelgasse 7, 90402 Nuremberg, Germany. 32 K. Friedrich 1 3 1 Introduction The concept of sustainable development is widely accepted as one of the most
This study contributes to the existing literature on sustainable HR and supply chain management by emphasising the importance of integrating environmental considerations into HR and supply chain strategies to enhance operational outcomes. Policymakers are encouraged to utilise these findings to develop frameworks that promote environmentally ...
This extended into the year 2021 to consider all the relevant and updated literature. We targeted, primarily, the peer-reviewed journal articles (original, review, published, and in press) written in English, with a focus on stakeholder pressure and the adoption of sustainable management practices.
The review aims to identify which factors are most important in the literature for Sustainability Organizational Performance in health services, namely Outcome, Leadership, Culture, Innovation, Human Resource Management, Knowledge Management, Strategy, Organization, Evaluation and Competitiveness which influence each other. Purpose: The purpose of this research is to explain the variables that ...
This paper aims to provide a brief review of the sustainable supply chain management literature. Supply chain management involves the extraction, production, transportation, and recycling of materials and products, which all have major impacts on the multiple dimensions of sustainable development—economic, environmental and social. Sustainable
In the discussion section, different critical factors of SSMP adoption covering farmers' perceptions, climate change, policy impact and the use of ICT are discussed. These findings and identified research gaps are useful for further research and the development of sustainable soil management policies, programmes and projects.
In order to better promote the theoretical research and management practice of sustainable leadership, we searched the literature related to sustainable leadership in databases such as Web of Science, EBSCO and CNKI. ... Systematic literature review on sustainable human resource management. J. Clean. Prod. 208 806-815. 10.1016/j.jclepro.2018. ...
The sustainability balanced scorecard - Linking sustainability management to business strategy: Conceptual/Literature review: Miscellaneous: Applications: 2: Hardjono and De Klein: 2004: Journal of Business Ethics (3) Introduction on the European Corporate Sustainability Framework (ECSF) Conceptual/Literature review: Miscellaneous: Applications ...
The first step of the literature review was to select a method and to generate a literature classification sheet. Inspired by Barratt et al. (2011), a classification sheet was created and distributed to all authors, along with five articles chosen for a calibration review.After this calibration round, the authors met to discuss the review of individual articles, the review process, and the ...
A comprehensive literature review informs these models and strategies, identifying opportunities for sustainable banner management. A case study approach is employed to present the transformation of banners into functional raincoats using Gemini X20 Pattern Designer software. The study emphasizes the optimization of resources and adherence to ...
Background. Early childhood caries (ECC) is a multifactorial disease in which environmental factors could play a role. The purpose of this scoping review was to map the published literature that assessed the association between the Sustainable Development Goal (SDG) 11, which tried to make cities and human settlements safe, inclusive, resilient and sustainable, and ECC.
The sustainable use of natural resources is becoming an increasingly urgent concern globally, as many of these resources face the threat of depletion [1, 2].The depletion of natural resources can profoundly affect human beings and jeopardize the sustenance and welfare of those who rely on these resources [3, 4].Indeed, farmers in developing countries' highlands depend on natural resources ...