The Kingdom of Bahrain, situated in an arid region, faces extreme water scarcity, which is expected to be exacerbated by climate change. The water management system in the Kingdom is modeled using the Water Evaluation and Planning (WEAP) dynamic model to assess its sustainability in terms of financial, economic, and environmental costs. The associated costs of the current management system were estimated under climate change impacts for 2022-2035, while the effectiveness of various management interventions in reducing these costs was evaluated both individually and in combination for the same period. The findings reveal that implementing these interventions has the potential to reduce municipal water demand by 30% by 2035, resulting in cumulative financial savings of approximately $1.25 billion. This reduction would also yield significant environmental benefits, including a cumulative reduction of 12,615 million tons of carbon dioxide (CO2) emissions and 2,383 million cubic meters of desalination brine discharge to the marine environment. Additionally, enhancing treated wastewater utilization through strategies such as afforestation and managed aquifer recharge could further mitigate environmental impacts and support Bahrain’s goal of achieving carbon neutrality by 2060. These results provide critical insights for policymakers to enhance the sustainability of Bahrain’s water management system, ensuring continued socio-economic development while reducing environmental impacts. Future modeling should address uncertainties related to population growth and spatial demographics using stochastic approaches. Furthermore, addressing data gaps on agricultural water consumption and cropping patterns is essential for simulating the agricultural sector and supporting effective decision-making.
References
[1]
Al-Zubari, W.K., El-Sadek, A.A., Al-Aradi, M.J. and Al-Mahal, H.A. (2018) Impacts of Climate Change on the Municipal Water Management System in the Kingdom of Bahrain: Vulnerability Assessment and Adaptation Options. Climate Risk Management, 20, 95-110. https://doi.org/10.1016/j.crm.2018.02.002
[2]
Al-Zubari, W. (2014) The Costs of Municipal Water Supply in Bahrain. Energy, Environ Research (Produced as Part of the Valuing Vital Resources in the Gulf Series). Chatham House. https://www.chathamhouse.org/sites/default/files/field/field_document/20141216MunicipalWaterBahrainAlZubari.pdf
[3]
Bates, B.C., Kundzewicz, Z.W., Wu, S. and Palutikof, J.P. (2008) Climate Change and Water. Technical Paper of the Intergovernmental Panel on Climate Change. IPCC Secretariat.
[4]
Al-Zubari, W., Al-Turbak, A., Zahid, W., Al-Ruwis, K., Al-Tkhais, A., Al-Muataz, I., et al. (2017) An Overview of the GCC Unified Water Strategy (2016-2035). Desalination and Water Treatment, 81, 1-18. https://doi.org/10.5004/dwt.2017.20864
[5]
Supreme Council for the Environment (SCE) (2020) Bahrain’s Third National Communication under the United Nations Framework Convention on Climate Change.
[6]
Al-Zubari, W.K., Khater, A.R., Al-Noaimi, M.A. and Al-Junaid, S.S. (1997) Spatial and Temporal Trends in Groundwater Salinity in Bahrain. Arabian Journal for Science and Engineering, 22, 81-94.
[7]
Ministry of Sustainable Development (2023) Bahrain SDGs 2030. https://www.sdgs.gov.bh/Goal/?ID=SAg/9rL2rwS19IITVAf7nw==
[8]
Ministry of Works (MOW) (2022) Cost of TSE Production in Bahrain. Unpublished Confidential Document.
[9]
Zubari, W.K. (2018) Development of the National Water Strategy and Implementation Plan for the Kingdom of Bahrain (2017-2030).
[10]
Information & eGovernment Authority (2020) Documents Resource Center. Bahrain Open Data Portal. https://data.gov.bh/pages/homepage/
[11]
Electricity and Water Authority (EWA) (2021) EWA STATISTICS [E-Book]. https://www.ewa.bh/en/AboutUs/AnnualReport/EWAStatistics2021.pdf
[12]
Ministry of Works (MOW) (2022) Internal MOW Reports. Unpublished Confidential Document.
[13]
Eryani, I.G.A.P., Jayantari, M.W. and Wijaya, I.K.M. (2022) Sensitivity Analysis in Parameter Calibration of the WEAP Model for Integrated Water Resources Management in Unda Watershed. CivilEngineeringandArchitecture, 10, 455-469. https://doi.org/10.13189/cea.2022.100206
[14]
Swedish Meteorological and Hydrological Institute (SMHI) and United Nations Economic and Social Commission for Western Asia (ESCWA) (2021) Future Climate Projections for the Mashreq Region: Summary Outcomes. RICCAR Technical Report. Beirut. https://www.unescwa.org/sites/default/files/pubs/pdf/riccar-future-climate-mashreq-english_3.pdf
[15]
Cooperation Council for Arab States of the Gulf Secretariat General (GCC SG) (2015) Development of Unified Water Sector Strategy and Implementation Plan for the Gulf Cooperation Council for Arab Member States for the Years 2015-2035. Final Report.
[16]
Frère, Q., Hammadou, H. and Paty, S. (2011) The Range of Local Public Services and Population Size: Is There a “Zoo Effect” in French Jurisdictions? RechercheséconomiquesdeLouvain, 77, 87-104. https://doi.org/10.3917/rel.772.0087
[17]
Peterson, E.W.F. (2017) The Role of Population in Economic Growth. SAGE Open, 7, 1-15. https://doi.org/10.1177/2158244017736094
[18]
Chowdhury, S., Al-Zahrani, M. and Abbas, A. (2016) Implications of Climate Change on Crop Water Requirements in Arid Region: An Example of Al-Jouf, Saudi Arabia. JournalofKingSaudUniversity-EngineeringSciences, 28, 21-31. https://doi.org/10.1016/j.jksues.2013.11.001
[19]
Mohan, S. and Ramsundram, N. (2014) Climate Change and Its Impact on Irrigation Water Requirements on a Temporal Scale. Irrigation & Drainage Systems Engineering, 3, Article 118.
[20]
Kadhem, G.M. and Zubari, W.K. (2020) Identifying Optimal Locations for Artificial Groundwater Recharge by Rainfall in the Kingdom of Bahrain. EarthSystemsandEnvironment, 4, 551-566. https://doi.org/10.1007/s41748-020-00178-2
[21]
Mishra, S., Kumar, R. and Kumar, M. (2023) Use of Treated Sewage or Wastewater as an Irrigation Water for Agricultural Purposes-Environmental, Health, and Economic Impacts. TotalEnvironmentResearchThemes, 6, Article 100051. https://doi.org/10.1016/j.totert.2023.100051