Heading into the Unknown? Exploring Sustainable Drought Management in the Mediterranean Region
Abstract
:1. Introduction
1.1. The Mediterranean Region
1.2. Identification of Drought Framework
2. Methods and Data
2.1. Approach
2.2. Data and Criteria for Selecting the Documents
- Institutional information: Policy documents from the European Commission, European Environment Agency, European Parliament and Council, United Nations (UN Convention to Combat Desertification, UN Development Programme, UN Office for Disaster Risk Reduction, UN Food and Agriculture Organisation, UN Secretariat of the International Strategy for Disaster Reduction), Organisation for Economic Co-operation and Development (OECD), and World Meteorological Organization (WMO).
- Time span: 10 years.
- Peer reviewed papers: Publications with the highest number of citations have been selected from the Journal Citation Reports.
- Sample size in bibliometric analysis: To analyze bibliometric data, a minimum of 50 documents is required [24].
- The main criteria used in this analysis for selecting the documents are specific terms to the field of drought, publication period, document type, language, and area of knowledge.
2.3. Limitations
3. Results
3.1. Quantification and Analysis of the Studies
3.2. Building from the Extraordinary Efforts of Drought Management in the Mediterranean Region
- (a)
- Societal barriers: Many regulations specifically applying to the use of water are not legally binding [116]. In addition, binding rules rely on local legislation, allowing wide national interpretation. The rules cannot be policed and enforced effectively in the field, and they do not apply to many users that compete for water.From a social point of view, the information suggests some aspects that that could be more clearly incorporated into drought management policies at the institutional level:
- Well-defined resource system boundaries: the boundaries of the resource system lack clear and precise definition.
- Progressive penalty system: individuals who infringe upon established rules may not receive appropriate penalties that vary in severity based on the gravity and context of their actions, whether from accountable authorities or fellow community members.
- Efficient conflict resolution mechanisms: access to cost-effective and timely local platforms for resolving disputes among users or between users and authorities is limited.
- Hierarchical resource management structures: resource allocation, supply, enforcement, conflict resolution, and governance functions are organized in hierarchical structures.
- Removing incentives that make water use harmful to social and environmental targets in the long run.
- (b)
- Individual barriers: The need for education on the natural and social services of water is a crucial element for moving towards more sustainable drought management. From an individual behavior point of view, the information suggests some aspects that that could be more clearly incorporated into drought management:
- Well-defined resource ownership limits: clearly outlining the demarcations that specify which individuals or households have the authority to gather resource units.
- Inclusive decision-making structures: a substantial portion of the individuals influenced by rules governing resource harvesting and protection are part of the collective capable of altering these rules.
- Incremental penalty system: those who breach established operational regulations are expected to encounter graduated penalties, contingent on the gravity and circumstances of the transgression, imposed by fellow users, officials answerable to these users, or a combination of both.
- Clearly defining the cost of using water during drought to each individual user.
- Removing incentives that make water use harmful to social and environmental targets in the long run.
- Accounting for the true value and true costs of water production by sector, promoting a life cycle assessment.
- (c)
- Economic barriers: The need for clearly showing the costs and benefits of sustainable drought management and poor drought management is a crucial element for moving towards a more sustainable drought management. From an economic point of view, the information suggests some aspects that that could be more clearly incorporated into drought management:
- Balanced correlation of benefits and costs: Regulations define the quantity of resource products a user receives in line with local conditions and the prerequisites involving labor, materials, and/or financial contributions.
- Accounting for the true value and true costs of water production by sector, promoting a life cycle assessment.
- (d)
- Technological barriers: The effective implementation of sound practices in water resource management can be hindered by a range of technological obstacles.
- Monitoring. A technological impediment is the insufficiency of clean and reliable data. Accurate, current information on water resources, encompassing aspects like water quality, quantity, and usage patterns, is indispensable for competent management. Overcoming this obstacle involves committing resources to enhance data collection and monitoring technologies, alongside establishing frameworks for the sharing and collaboration of data among stakeholders. Furthermore, it is essential to build the capacity for data analysis and interpretation.
- One of the significant challenges is outdated infrastructure. Effective water management necessitates the provision of public goods, meaning services like storage infrastructure, and amenities such as roads, electricity, and information and communication technologies. However, the cost and complexity of upgrading such infrastructure can be a barrier, especially in areas with limited financial resources.
- (e)
- Natural environment barriers: Overcoming natural environment barriers requires a holistic approach that considers the interconnectedness of ecosystems, climate, and water resources.
- Climate change. Changing climate patterns, with variations in rainfall and temperature, can cause water scarcity and more frequent severe droughts, disrupting the supply of clean water. Additionally, climate change can result in intensified extreme weather phenomena like floods and storms, harming water infrastructure and polluting water sources, adding complexity to water resource management [122].
- Deterioration of freshwater ecosystems. The degradation of wetlands, deforestation within watershed areas, and pollution from agricultural and industrial activities, as well as from extreme weather events, can undermine the natural environment’s capacity to store and cleanse water. Preserving and rehabilitating these ecosystems is of the utmost importance to uphold robust and sustainable water resources [123].
3.3. A Framework That Focuses on the Idea of Managing Common Resources
3.4. Looking into the Future
4. Discussion
- The potential benefits: This is the most common aspect included in the current drought management plans, since it provides a convincing argument for stakeholders to support the policy proposal.
- The risk and gain of sustainable drought management choices: [126] Conducting a risk-gain analysis enables water stakeholders to assess and contrast various drought management approaches, aiding in the identification of options that yield the highest benefit for their systems. While stakeholders comprehend the impact of drought on aspects such as water quality, quantity, and social and environmental demand, determining the risks and evaluating the relative advantages of diverse drought management practices poses a challenge. Research is essential to equip stakeholders with tools to estimate these risks and gains, facilitating informed decisions in the selection of appropriate drought management strategies.
- The future scenarios: [11] All efforts for sustainable drought management include unconditionally future climate change scenarios. In spite of this indisputable evidence of a future increase in drought in the Mediterranean Region, some of the current plans still lack this long-term vision of future climate change scenarios and social demands.
5. Conclusions
- This paper recommends integrating lessons from managing common resources and risk, shifting from reactive to proactive strategies, and creating a regional code on drought management. It also encourages to identify barriers, including societal, economic, technological, and environmental factors that impede sustainable drought management.
- This research emphasizes the need for measuring benefits, incorporating future scenarios, and demonstrating long-term gains to promote sustainable drought management.
- It also advocates for a shift towards dynamic and adaptive drought plans that blend long-term strategies with immediate solutions: shifting from a reactive to a proactive approach.
- This work highlights the importance of voluntary measures, farmer participation, clear responsibilities, defining drought, and investing in knowledge and public policies.
- The authors propose the establishment of a Technical Secretariat to centralize information, coordination, and collaboration in drought management efforts.
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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Mediterranean Region: Main Information Provided | Scientific Publications (SP): | Policy Documents (PD): |
---|---|---|
Technical aspects (T.A): | [14,25,26,27,28,29,30,31,32,33,34,35,36,37,38,39,40,41,42,43] | [2,44,45,46,47,48,49,50,51,52,53] |
T.A. General aspects | [14,30,32,34,37] | [2,44,46,47,49,51,52,53] |
T.A. Climatic and environmental aspects | [25,27,31,33,38,42,43] | [48] |
T.A. Economic evaluation | [26,29,36] | [45] |
T.A. Indicators | [28,35,39,40,41] | [50] |
Risk management (R.M): | [13,54,55,56,57,58,59,60,61,62,63,64,65,66,67] | [68,69,70,71,72] |
R.M. General aspects | [13,60,63,66] | [69] |
R.M. Environmental aspects | [54,55,67] | [68] |
R.M. Statistical analysis | [56,59,62,65] | [70] |
R.M. Conceptual framework | [61,64] | [71,72] |
R.M. Case studies | [58] | |
R.M. Indicators | [57] | |
Policy implementation (P.I): | [1,3,4,6,7,58,73,74,75,76,77,78,79,80,81,82,83,84,85,86] | [5,50,87,88,89,90,91,92,93,94,95,96] |
P.I. General aspects | [3,74,77,80,83,86] | [50,87,88,89,92,95,96] |
P.I. Environmental aspects | [1,6,7,75,79,85] | [50,87,89,90,93,94] |
P.I. Conceptual framework | [4,78] | [5] |
P.I. Evolution review | [76] | [91] |
P.I. Case studies | [4,73,81,84] |
Other Regions: Main Information Provided | Area of Study | Scientific Publications |
---|---|---|
Technical aspects | OECD countries | [45,91] |
Global | [97] | |
Australia | [98] | |
Europe: | ||
Northern Europe | [99,100] | |
Central Europe | [101] | |
UK | [102,103,104] | |
Denmark | [105] | |
Bulgaria | [106] | |
Risk management | Global | [23,107] |
USA | [108] | |
Sweden | [109] | |
Policy implementation | Global | [110] |
USA | [111,112,113,114] |
Mediterranean Region | Scientific Publications | Policy Documents | |||
---|---|---|---|---|---|
Main Information Provided | No. of Publications | % In Each Category | No. of Documents | % In Each Category | |
Technical aspects | General aspects | 6 | 29% | 8 | 73% |
Climatic and environmental aspects | 7 | 33% | 1 | 9% | |
Economic evaluation | 3 | 14% | 1 | 9% | |
Indicators | 5 | 24% | 1 | 9% | |
Total: | 21 | 11 | |||
Risk management | General aspects | 4 | 27% | 1 | 20% |
Environmental aspects | 3 | 20% | 1 | 20% | |
Statistical analysis | 4 | 27% | 1 | 20% | |
Indicators | 2 | 7% | 2 | 0% | |
Conceptual framework | 1 | 13% | 40% | ||
Case studies | 1 | 7% | 0% | ||
Total: | 15 | 5 | |||
Policy implementation | General aspects | 6 | 30% | 7 | 58% |
Environmental aspects | 6 | 30% | 6 | 50% | |
Conceptual framework | 2 | 10% | 1 | 8% | |
Case studies | 1 | 20% | 2 | 17% | |
Evolution review | 4 | 5% | 0% | ||
Total: | 20 | 12 | |||
Overall | 56 | 28 |
Individual Actors Affected Directly by Drought Impacts | Collective Actors Influencing Drought Management Policy | Actors Arbitering the Operational Decisions That Affect Individuals and Collective Groups | |
---|---|---|---|
Positions | Short term, individual | Normative actions | Supporting advice and operational decisions |
Allowable actions | Very limited | Low, mostly financial | Very large |
Control over choice | Dependent on information and cognitive barriers | High | High |
Information available | Low | Low | Owners, high |
Cost and benefits of actions and outcomes | High | Low | High |
Understanding the Outcome of the Following Choice | Individual Stakeholder Preferences | Collective Stakeholder Preferences |
---|---|---|
Demonstration of the effectiveness of management actions | Very high | Medium |
Demonstration of potential losses without management actions | Medium | Very high |
Capacity of the user to act upon the information given | Essential | Low |
Cost of management action | Medium | Very high |
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© 2023 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/).
Share and Cite
Martin-Candilejo, A.; Martin-Carrasco, F.J.; Iglesias, A.; Garrote, L. Heading into the Unknown? Exploring Sustainable Drought Management in the Mediterranean Region. Sustainability 2024, 16, 21. https://doi.org/10.3390/su16010021
Martin-Candilejo A, Martin-Carrasco FJ, Iglesias A, Garrote L. Heading into the Unknown? Exploring Sustainable Drought Management in the Mediterranean Region. Sustainability. 2024; 16(1):21. https://doi.org/10.3390/su16010021
Chicago/Turabian StyleMartin-Candilejo, Araceli, Francisco J. Martin-Carrasco, Ana Iglesias, and Luis Garrote. 2024. "Heading into the Unknown? Exploring Sustainable Drought Management in the Mediterranean Region" Sustainability 16, no. 1: 21. https://doi.org/10.3390/su16010021
APA StyleMartin-Candilejo, A., Martin-Carrasco, F. J., Iglesias, A., & Garrote, L. (2024). Heading into the Unknown? Exploring Sustainable Drought Management in the Mediterranean Region. Sustainability, 16(1), 21. https://doi.org/10.3390/su16010021