Morocco's Phosphate Industry in the Khouribga Region

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Morocco's Phosphate Industry in the Khouribga Region Hydrol. Earth Syst. Sci., 24, 4727–4741, 2020 https://doi.org/10.5194/hess-24-4727-2020 © Author(s) 2020. This work is distributed under the Creative Commons Attribution 4.0 License. A Water-Energy-Food Nexus approach for conducting trade-off analysis: Morocco’s phosphate industry in the Khouribga region Sang-Hyun Lee1, Amjad T. Assi2, Bassel Daher2,3,4, Fatima E. Mengoub5,6, and Rabi H. Mohtar2,7,8 1Research Institute for Humanity and Nature, Kyoto, Japan 2Department of Biological and Agricultural Engineering, Texas A&M University, College Station, TX 77843-2117, USA 3Texas A&M Energy Institute, Texas A&M University, College Station, TX 77843, USA 4Institute for Science Technology and Public Policy, Bush School of Government and Public Service, Texas A&M University, College Station, TX 77845, USA 5Policy Center for the New South, Suncity Complex, Building C, Angle of Addolb Boulevard and Albortokal Street, Rabat, Morocco 6Mohammed VI Polytechnic University, Lot 6620, Hay Moulay Rachid 43150, Ben Guerir, Morocco 7Zachry Department of Civil and Environmental Engineering, Texas A&M University, College Station, TX 77843-3136, USA 8Department of Agricultural and Food Sciences, American University of Beirut, Beirut, Lebanon Correspondence: Rabi H. Mohtar ([email protected]) Received: 28 April 2020 – Discussion started: 18 May 2020 Revised: 11 August 2020 – Accepted: 24 August 2020 – Published: 5 October 2020 Abstract. The study objective was to develop and use the creased from 5:8 × 106 to 5:2 × 106 m3. Dynamic manage- Water-Energy-Food Nexus Phosphate (WEF-P) Tool to eval- ment of the phosphate industry can also save 143 MWh uate the impact of Morocco’s phosphate industry on water, (megawatt-hour) of electricity annually and can bring a re- energy, and food sectors of Khouribga, which is the repre- duction of 117 t of CO2 emissions. Making water available at sentative phosphate mining region of Morocco. The devel- the correct season and location requires analysis of complex oped WEF-P Tool enabled a trade-off analysis based on in- scientific, technical, socioeconomic, regulatory, and political tegrating supply-chain processes, transportation, and water– issues. The WEF-P Tool can assist by assessing user-created energy footprints of the region. Field data from the mining to scenarios; thus, it is an effective management-decision aid transportation processes were collected and applied to pos- for ensuring more sustainable use of limited resources and sible supply-chain scenarios in accordance with the type of increased reliability of water resources for both agricultural product (phosphate rock and slurry). The potential impacts and industrial use. This study on the applications of WEF of the scenarios were considered in terms of the water sup- Nexus to the phosphate industry offers a roadmap for other ply in the agricultural areas. The analysis of the positive im- industrial application for which trade-offs between the pri- pacts of dynamic management suggests that seasonal man- mary resources must be considered. agement of phosphate production (less during the irrigated season, more during wetter or rainier seasons) is more ef- fective. Additionally, while the transport of raw phosphate slurry through a pipeline increased the total water required to 1 Introduction 34:6 × 106 m3, which is an increase of 76 % over the “busi- ness as usual” (BAU) scenario, it also resulted in an energy Nexus thinking emerged from the understanding that nat- savings of nearly 80 % over BAU: slurry transport requires ural resource availability can limit and is limited by eco- only 40:5×106 L of fossil fuel instead of the 204×106 L re- nomic growth and other goals associated with human well- quired to transport rocks. During the dry or “water-scarce” being (Hoff, 2011; Keulertz et al., 2016). The innovative as- irrigation season (May to July), total groundwater use de- pect of nexus thinking is its more balanced view of the issues linking resources (Al-Saidi and Elagib, 2017). Thus, nexus Published by Copernicus Publications on behalf of the European Geosciences Union. 4728 S.-H. Lee et al.: WEF-P Nexus Tool for Morocco’s phosphate industry frameworks identify key issues in food, water, and energy water and energy, which in turn leads to issues of downscal- securities through a lens of sustainability and seek to pre- ing water or energy securities. dict and protect against future risks and resource insecuri- The nexus framework is dependent on the stakeholders, ties (Biggs et al., 2015). The 2015 World Economic Forum system boundary, and analytical tools. In considering the ap- identified water, food, and energy shocks as primary future plication of the nexus as a platform, an integrated model- risks, calling for increased efficiency in water use across all ing approach is essential. These issues manifest in very dif- sectors and the implementation of integrated water resources ferent ways across each sector, but their impacts are often management. Various conceptual frameworks relating to the closely related in terms of trade-offs. In particular, the sub- nexus approach were developed: the Dubois et al. (2014) em- nexus needs to be effectively conceptualized and a theoretical phasized the role of the nexus in food security, and the In- sub-nexus developed. Private-sector water, energy, and food- ternational Renewable Energy Association (Ferroukhi et al., supply-chain players are the key stakeholders to address cur- 2014) applied the nexus approach in transforming conven- rent contradictions arising as a consequence of attempts to tional energy systems to renewable systems. develop a grand nexus approach (Allan et al., 2015). Accord- The demand for water, energy, and food is expected to in- ingly, we must consider the “specialized” nexus of multi- crease due to drivers such as population growth, economic stakeholders, such as agriculture, industry, and urban areas, development, urbanization, and changing consumer habits for which water, energy, and food are treated as subsystems. (Terrapon-Pfaff et al., 2018). The interlinkages across key Current nexus frameworks often focus on macrolevel drivers natural resource sectors and improving their production ef- of resource consumption patterns (Biggs et al., 2015), but ficiency offer a win-win strategy for environmental sustain- major nexus challenges are faced at local levels (Terrapon- ability for current and/or future generations (Ringler et al., Pfaff et al., 2018). Thus, “larger-scale” extraction and con- 2013). Accordingly, application of the Water-Energy-Food sumption of natural resources may lead to depletion of natu- (WEF) Nexus concept or approach is expected to make im- ral capital stocks and increased climate risk with no equitable plementation of the Sustainable Development Goals (SDGs) share of the benefits (Hoff, 2011; Rockström et al., 2009). Al- more efficient and robust (Brandi et al., 2014; Yumkella and Saidi and Elagib (2017) showed the importance of exploring Yillia, 2015). The SDGs are classic examples of the neces- driving forces and interactions at different scales in the con- sity to acknowledge multidimensional nexus interlinkages ceptual development of the nexus, emphasizing more case- and trade-offs, particularly as governments are challenged study-based recommendations in the reality of institutions, to maximize benefits and invest limited resources. Infras- bureaucracies, and environmental stakeholders. tructure and capital are needed to achieve national SDG tar- Morocco’s phosphate and agriculture industries offer an gets, and the nexus concept is now used to highlight inter- example of increasing resource pressures attributable to near- dependencies between resources and the need for integrated, and medium-term growth across these sectors (Taleb, 2006). sustainable governance and management of those resources A holistic approach that considers the needs of all stake- (Pahl-Wostl, 2019). holders is necessary to resolve resource allocation pressures. The debate surrounding effectively addressing water and Between 1990 and 2016, Morocco’s population grew from food security challenges stems from questions about whether 25 million to 35 million people (World Bank, 2019a). Both the water–food crisis is due to a poor understanding of the crop production and total cultivated land significantly in- resources or to their improper management (Mohtar et al., creased since 1971; half of Morocco’s arable land receives 2015; Keulertz and Mohtar, 2019). One long-standing chal- less than 350 mm of rainfall annually, and nearly 87.3 % of lenge to water management lies in the lack of integration Morocco’s total water withdrawals are used for agriculture among the multiple sectors that interact with the water sec- (FAO, 2015). Per capita consumption of electric power in- tors across geographical areas or within large, transboundary, creased from 358 kWh (1990) to 901 kWh (2014); energy basins (Mohtar and Lawford, 2016). Projections about avail- use by oil equivalent per capita increased from 306 to 553 kg ability and quality of water, food, energy, or soil resources are during the same period (World Bank, 2019b). Proper man- often alarming. A fundamental shift is needed away from tra- agement of water, energy, and food resources is critical to ditional “silo” approaches and toward more integrative sys- economic, social, and environmental wellbeing. tems approaches (Daher and Mohtar, 2015). Energy and wa- Globally, phosphates lie at the heart of agriculture and soil ter are crucial for economic growth, especially in industrial- enhancement. More than 75 % of global phosphate reserves, ized areas (Flörke et al., 2013; Cai et al., 2016), making the representing 30 % of the global market share, are found in rapid increase in demand for these resources a serious issue Morocco, positioning that country at a leading role in global for both economics and the environment. While technology food security (OCP, 2013). Phosphate mining and its chem- to reduce industrial demand for water and energy is impor- ical processing require considerable water, energy, land, and tant, we must also understand the relationship between eco- other resource inputs.
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