Essay On Water Management

500 words essay on water management.

Water management refers to activities that plan, develop, distribute and manage the optimum use of water resources. Everyone can do this from local authorities to individuals at home. Good water management allows access to safe water for everyone. Through an essay on water management, we will go through it in detail.

essay on water management

Importance of Water Management

Water management impacts various aspects of our lives. As water is common, we do not think much of its management. But, if we ask the deprived people, they will know the importance of water management very well.

As we require drinking water, clean drinking water is a necessity. No human can survive without water. Further, we also need water management for cleaning and washing. For instance, we bathe, wash our clothes and utensils to maintain hygiene .

Further, agriculture requires water for growing the food that we eat every day. Thus, a good water supply becomes essential. Moreover, we also enjoy swimming, boating and other leisure activities in the water.

For instance, swimming pools and more. Thus, water needs to be managed so people can enjoy all this. Most importantly, water management ensures that our rivers and lakes do not contaminate. Thus, it helps maintain biodiversity.

Ways of Water Management

There are various ways available through which we can manage water. The major ways of water management include recycling and treating wastewater. When we treat wastewater , it becomes safe to be piped back to our homes.

Thus, we use it for drinking, washing and more. In addition, an irrigation system is a very good way of water management. It involves a good quality irrigation system which we can deploy for nourishing crops in drought-hit areas.

By managing these systems, we can ensure water does not go to waste and avoid unnecessarily depleting water supplies. Most importantly, conserving water is essential at every level.

Whether it is a big company or a small house, we all must practise water management. The big industries use gallons of water on a daily basis. At homes, we can conserve water by using it less.

Further, it also applies to our way of consumption of products. A large amount of water goes into the production of cars or a simple item like a shirt. Thus, we must not buy things unnecessarily but consciously.

It is also essential to care for natural supplies like lakes, rivers , seas and more. As you know, these ecosystems are home to a variety of organisms. Without its support, they will go extinct. Thus, water management becomes essential to ensure we are not polluting these resources.

It is also crucial to ensure that everyone gets access to enough water. Some parts of the world are completely deprived of clean water while some have it in abundance. This is unfair to those who do not get it which also causes many deaths. Thus, we need water management to avoid all this.

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Conclusion of the Essay on Water Management

If we look at the current situation of water depletion, it is evident that we are in dire need of water management. We must come together to do our best to ensure that everyone is getting access to safe water daily so that we can lead happy lives.

FAQ of Essay on Water Management

Question 1: What is meant by water management?

Answer 1: Water management refers to the control and movement of water resources for minimizing damage to life and property. Moreover, it is to maximize effective beneficial use.

Question 2: What are the ways of water management?

Answer 2: There are numerous ways of water management. Some of them are the treatment of wastewater, deploying good irrigation methods, conserving water whenever possible. Further, we must also care for natural sources of water like rivers, seas, lakes and more.

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Open Access

Peer-reviewed

Research Article

Water resource management: IWRM strategies for improved water management. A systematic review of case studies of East, West and Southern Africa

Roles Conceptualization, Formal analysis, Investigation, Methodology, Writing – original draft, Writing – review & editing

* E-mail: [email protected]

Affiliations Soil, Crop, and Climate Sciences, University of the Free State, Bloemfontein, South Africa, School of Engineering, University of KwaZulu-Natal, Pietermaritzburg, South Africa, Varmac Consulting Engineers, Scottsville, Pietermaritzburg, South Africa

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Roles Conceptualization, Formal analysis, Methodology, Writing – original draft, Writing – review & editing

Affiliation Department of Civil & Structural Engineering, Masinde Muliro University of Science and Technology, Kakamega, Kenya

Roles Conceptualization, Methodology, Supervision, Writing – review & editing

Affiliation Soil, Crop, and Climate Sciences, University of the Free State, Bloemfontein, South Africa

Roles Writing – review & editing

Affiliation Department of Agriculture and Engineering Services, Irrigation Engineering Section, Ministry of Agriculture and Natural Resources, Ilorin, Kwara State, Nigeria

  • Tinashe Lindel Dirwai, 
  • Edwin Kimutai Kanda, 
  • Aidan Senzanje, 
  • Toyin Isiaka Busari

PLOS

  • Published: May 25, 2021
  • https://doi.org/10.1371/journal.pone.0236903
  • Reader Comments

Table 1

The analytical study systematically reviewed the evidence about the IWRM strategy model. The study analysed the IWRM strategy, policy advances and practical implications it had, since inception on effective water management in East, West and Southern Africa.

The study adopted the Preferred Reporting Items for Systematic Review and Meta-analysis Protocols (PRISMA-P) and the scoping literature review approach. The study searched selected databases for peer-reviewed articles, books, and grey literature. DistillerSR software was used for article screening. A constructionist thematic analysis was employed to extract recurring themes amongst the regions.

The systematic literature review detailed the adoption, policy revisions and emerging policy trends and issues (or considerations) on IWRM in East, West and Southern Africa. Thematic analysis derived four cross-cutting themes that contributed to IWRM strategy implementation and adoption. The identified four themes were donor effect, water scarcity, transboundary water resources, and policy approach. The output further posited questions on the prospects, including whether IWRM has been a success or failure within the African water resource management fraternity.

Citation: Dirwai TL, Kanda EK, Senzanje A, Busari TI (2021) Water resource management: IWRM strategies for improved water management. A systematic review of case studies of East, West and Southern Africa. PLoS ONE 16(5): e0236903. https://doi.org/10.1371/journal.pone.0236903

Editor: Sergio Villamayor-Tomas, Universitat Autonoma de Barcelona, SPAIN

Received: July 12, 2020; Accepted: May 2, 2021; Published: May 25, 2021

Copyright: © 2021 Dirwai et al. This is an open access article distributed under the terms of the Creative Commons Attribution License , which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.

Data Availability: All relevant data are within the paper.

Funding: This study was supported by the National Research Foundation (NRF) in the form of a grant awarded to TLD (131377) and VarMac Consulting Engineers in the form of a salary for TLD. The specific roles of the authors are articulated in the ‘author contributions’ section. The funders had no additional role in the study design, data collection and analysis, decision to publish, or preparation of the manuscript.

Competing interests: The authors have read the journal’s policy and have the following potential competing interests: TLD is a paid employee of VarMac Consulting Engineers. This does not alter our adherence to PLOS ONE policies on sharing data and materials. There are no patents, products in development or marketed products associated with this research to declare.

1 Introduction

Integrated Water Resources Management (IWRM) is a concept that is meant to foster effective water resource management. GWP [ 1 ] defined it as “the process which promotes the coordinated development and management of water, land and related resources, to maximise the resultant economic and social welfare equitably without compromising the sustainability of vital systems”. A holistic approach, in the form of the Dublin statement on Water and Sustainable Development (DSWSD), emerged and it became the backbone of IWRM principles.

According to Solanes and Gonzalez-Villarreal [ 2 ] the Dublin priciples are: “ (1) Freshwater is a finite and vulnerable resource , essential to sustain life , development and the environment; (2) Water development and management should be based on a participatory approach , involving users , planners and policy-makers at all levels , (3) Women play a central part in the provision , management , and safeguarding of water , and (4) Water has an economic value in all its competing uses , and should be recognised as an economic good .” The seamless conflation of the DSWSD and the Agenda 21 at the United Nations Conference on Environment and Development (UNCED) in 1992 further strengthened the IWRM discourse and facilitated the policy approach of IWRM [ 3 , 4 ]. Since its inception the IWRM policy has been the holy grail of water resource management in Africa, Asia, and Europe to mention a few. For policy diffusion, countries were required to develop an IWRM policy blueprints for effective water use [ 5 ].

This review sought to unveil the innovative IWRM strategy approach by critically examining its genesis, implementation, adoption and the main drivers in in East, Southern and West Africa. Secondary to this, the study endeavoured to determine whether the IWRM implementation has been a success or failure. The choice of East, West and Southern Africa was influenced by the regional dynamics of Sub-Saharan Africa which have unique problems in water resources management and the hydropolitical diversity in this region. The isolated cases provide a holistic representation t the implementation dynamics of IWRM. In addition, sub-Sahara Africa was the laboratory for IWRM with Zimbabwe and South Africa being the early implementers [ 6 ]. Apart from the IWRM strategy being a social experiment in sub-Sahara, there exists a gap on an overarching review on the performance and aggregated outcomes of the IWRM adopters in the continent. The selection of the countries of interest was based on the authors geo-locations and their expert experiences with the IWRM strategy in their respective localities. The study sought to draw trends, similarities, and potential differences in the drivers involved in achieving the desired IWRM outcome.

IWRM strategy approach and implementation are ideally linked to individual country’s developmental policies [ 7 ]. Southern Africa (Zimbabwe and South Africa) is the biggest adopter of the water resource management strategy and produced differed uptake patterns [ 8 ]. In East Africa, Tanzania,Uganda and Kenya also adopted the IWRM strategy, whilst in West Africa, Burkina Faso latently adopted the IWRM strategy in 1992 [ 4 ] and in Ghana, customary and traditional water laws transformed into latent IWRM practices [ 9 ].

Various initiatives were put in place to aid the adoption of IWRM in sub-Sahara Africa. For example, Tanzania benefited from donor funds and World Bank programmes that sought to alleviate poverty and promote environmental flows. The World Bank radically upscaled and remodelled IWRM in Tanzania through the River Basin Management—Smallholder Irrigation Improvement Programme (RBM-SIIP) [ 10 ]. The government of Uganda’s efforts of liberalising the markets, opening democratic space and decentralising the country attracted donor funds that drove the IWRM strategy agenda. The long-standing engagement between Uganda and the Nordic Fresh Water initiative helped in the diffusion of IWRM strategy in the country. Finally, in West Africa, Burkina Faso and Ghana made significant strides in operationalising the IWRM strategy by adopting the West Africa Water Resources Policy (WAWRP). A massive sense of agency coupled with deliberate government efforts drove the adoption status of Burkina Faso.

Total policy diffusion can be achieved when the practice or idea has supporting enablers. Innovation is key in developing plocies that altersocietal orthodox policy paths that fuel hindrance and consequently in-effective water governance [ 11 ]. Acknowledging the political nature of water (water governance and transboundary catchments issues) is the motivation to legislate water-driven and people-driven innovative policy [ 12 ]. Water policy reform should acknowledge the differing interests’ groups of the water users and its multi-utility nature; thus, diffusion channels should be tailored accordingly, avoiding the ‘one size fits all’ fallacy. IWRM as an innovative strategy approach diffused from the global stage to Africa and each regional block adopted the approach at different times under different circumstances.

The rest of this paper is outlined as follows; section 2 presents the conceptual framework adopted and the subsequent methodology. Section 3 presents the results and discussion. The discussion is structured around innovation driver in each respective region. Thereafter, sub-section 3.4 presents the prospect of IWRM in the East, West and Southern Africa regions. Lastly, the paper presents the conclusion.

2 Methodology

2.1 conceptual framework and methodology.

The analytical framework applied in the study is based on the water innovation frames by the United Nations Department of Economic and Social Affairs (UNDESA) [ 13 ]. The UNDESA [ 13 ], classified water frames into three distinct categories namely water management strategies (e.g., IWRM), water infrastructure and water services. The former partly involves IWRM strategies and the latter encompasses economic water usage such as agriculture, energy production and industrial applications [ 12 ].

The literature review identified research gaps that informed the employed search strategy. The literature that qualified for inclusion was thoroughly analysed and discussed. The aggregated outcomes were used for excerpt extraction in the thematic analysis.

2.2 Literature handling

The study performed a systematic review as guided by the Arksey and O’Malley [ 14 ] approach. The approach details methods on how to scope, gather, screen and report literature. The study further employed a constructionist thematic analysis to extract common recurring themes amongst the regions.

2.2.1 Eligibility criteria.

Eligibility criteria followed an adapted SPICE (Setting, Perspective, Intervention, Comparison and Evaluation) structure ( Table 1 ). The SPICE structure informed the study’s search strategy ( Table 2 ) and the subsequent formulation of the inclusion-exclusion criteria ( Table 3 ). The evidence search was conducted from the following databases: Scopus, Web of Science, Google Scholar, UKZN-EFWE, CABI, JSTOR, African Journals Online (AJOL), Directory of Open Access Journals (DOAJ), J-Gate, SciELO and WorldCat for peer-reviewed articles, books, and grey literature. The study did not emphasize publication date as recommended by Moffa, Cronk [ 15 ]. Databases selection was based on their comprehensive and over-arching nature in terms of information archiving. It is worth mentioning that the search strategy was continuously revised by trial and error until the databases yielded the maximum number of articles for screening.

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2.2.2 Search strategy.

The search strategy or query execution [ 16 ] utilised Boolean operators ( OR & AND ). The dynamic nature of the search strategy required the authors to change the search terms and strategy, for example, if digital databases did not yield the expected search items the study would manually search for information sources. The search queries included a string of search terms summarised in Table 2 .

2.2.3 Selection process.

DistillerSR © software was used for article screening. Online data capturing forms were created in the DistillerSR © software and two authors performed the article scoring process that eventully led to article screening. The screening was based on the article title, abstract and locality. The study employed a two-phase screening process [ 17 ], the first phase screened according to title and the second phase screened according to abstract and keywords. During the screening process, studies that the matched information in the left column of Table 3 we included in the literature review syntheses, whilst those that matched the exclusion list were discarded.

2.3 Thematic analysis

The review also adopted the thematic analysis approach by Braun and Clarke [ 18 ] to extract, code, and select candidate converging themes for the systematic review. The selected lieterature was subjected to qualitative analysis to capture recurring themes amongst the selected regions (East, West and Southern Africa). Data extracts from the respective regional analysis were formulated into theoretical themes. Thereafter, the extracted data was coded according to the extracted patterns from the information source to constitute a theme. It is worth mentioning that the authors used their discretion to extract and code for themes.

3 Results and discussion

Data charting comprised of the PRISMA flow-chart ( Fig 1 ). The study utilised 80 out of 183 records (n = 37, 46%) for East Africa, (n = 37, 46%) for Southern Africa, and (n = 6, 8%) for West Africa.

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3.1 Case studies

The introduction of IWRM in the East African region was initiated in 1998 by the water ministers in the Nile basin states due to the need for addressing the concerns raised by the riparian states. These water sector reforms revolved around the Dublin principles initiated by the UN in 1992 [ 20 ]. In 1999, Kenya developed the national water policy and the enabling legislation, the Water Act 2002 was enacted [ 21 ]. The Act was replaced by the Water Act 2016 which established the Water Resources Authority (WRA) as the body mandated to manage water resources in line with the IWRM principles and Water Resource Users Association (WRUA) as the lowest (local) level of water management [ 22 ].

Similarly, Uganda developed the national water policy in 1999 to manage, and develop the available water resources in an integrated and sustainable manner [ 23 ]. The National Water Policy further provides for the promotion of water supply for modernized agriculture [ 24 ]. Tanzania’s water policy of 2002 espouses IWRM principles, and its implementation is based on a raft of legal, economic, administrative, technical, regulatory and participatory instruments [ 25 ]. The National Irrigation Policy (NIP), 2010 and the National Irrigation Act, 2013 provides the legal basis for the involvement of different actors on a private-public partnership basis [ 26 ].

West Africa possesses an unregistered IWRM strategy that is espoused in the West Africa Water Resources Policy (WAWRP) of 2008. The WAWRP is founded on the following legal principles; (a) “promote, coordinate and ensure the implementation of a regional water resource policy in West Africa, in accordance with the mission and policies of Economic Community of West African States (ECOWAS)and (b) “harmonization and coordination of national policies and the promotion of programmes, projects and activities, especially in the field of agriculture and natural resources”. The founding legal basis resonates with the Dublin principles.

The WAWRP design actors were ECOWAS, Union Economique et MonĂ©taire Ouest Africaine (UEMOA), and ComitĂ© Permanent Inter-État de Llutte Contre la SĂ©cheresse au Sahel (CILSS). CILSS is the technical arm of ECOWAS and UEMOA. The institutional collaboration was driven by the fact that West Africa needed a sound water policy for improved regional integration and maximised economic gains. ECOWAS established the Water Resources Coordination Centre (WRCC) to (a) oversee and monitor the region’s water resources and management activities and (b) to act as an executive organ of the Permanent Framework for Coordination and Monitoring (PFCM) of IRWM [ 27 ].

The inception and triggers of IWRM in West Africa can be traced back to the General Act of Berlin in 1885 which, among other things, dictated water resources use of the Congo and Niger rivers [ 28 ]. A multiplicity of agreements around shared watercourses in West Africa led to the realisation of the IWRM policy approach. For example, the Senegal River Basin (SRB) Development Mission facilitated collaboration between Senegal and Mauritania in managing the SRB. Another noteworthy agreement was Ruling C/REG.9/7/97, a regional plan to fight floating plants in the ECOWAS countries [ 28 ]. GWP (2003) categorised the West African countries according to the level of adoption into three distinct groups namely; (a) Group A comprised of countries with the capacity to develop and adopt the IWRM approach (Burkina Faso and Ghana), (b) Group B comprised of countries needing “light support” to unroll the IWRM plan (Benin, Mali, Nigeria, and Togo), and (3) Group C comprised of laggards which needed significant support to establish an IWRM plan (Cape Verde, Ivory Coast, Gambia, Guinea, Guinea Bissau, Liberia, Mauritania, Niger, Senegal and Sierra Leone).

Southern African Development Community (SADC) regional bloc has over 15 shared transboundary river basins (For detailed basin and catchment arrangement in SADC see [ 29 ]). SADC member states established the Protocol on Shared Water Systems (PSWS) which meant to encourage sustainable water resources utilisation and management. The PSWS was perceived to strengthen regional integration [ 30 ]. The regional bloc formulated the Regional Strategic Action Plans (RSAPs) that sought to promote an integrated water resources development plan. The action initiative mimicked IWRM principles and the shared water resources initiatives acted as a catalyst for the genesis of IWRM in Southern Africa [ 31 ]. SADC houses the Waternet and the GWP-SA research and innovation hubs upon which SADC’s IWRM adoption was anchored on. Besides the availability of trained water experts in the region who were willing to experiment with the IWRM policy approach, water scarcity fuelled by climate change prompted the region’s adoption of the IWRM policy approach at the local level.

3.2 Diffusion drivers of IWRM in East, West and Southern Africa

3.2.1 water scarcity..

The adoption of IWRM in East Africa was necessitated by water scarcity which is experienced by the countries in the region, which formed the need for adoption of prudent water resources management strategies as envisaged under the Dublin principles which was championed indirectly, according to Allouche [ 5 ], by the World Bank. Specifically, the need to give incentives and disincentives in water use sectors to encourage water conservation.

Kenya is a water-scarce country with per capita water availability of 586 m 3 in 2010 and projected to 393 m 3 in 2030 [ 32 ]. Uganda is endowed with water resources, however, it is projected that the country will be water-stressed by 2020 which could be compounded by climate variability and change, rapid urbanization, economic and population growth [ 33 ].

Using water scarcity was in essence coercing countries to adopt the IWRM principles with the irrigation sector, the contributor of the largest proportion of water withdrawals, becoming the major culprit [ 5 ]. The researchers opine that the effects of water scarcity in the region can be countered by adopting IWRM strategy, but adaptively to suit the local context and thus, persuasive rather than coercive, is the appropriate term. Indeed, as put forward by Van der Zaag [ 34 ], IWRM is not an option but it is a necessity and therefore, countries need to align their water policies and practices in line with it.

West African climatic conditions pose a threat on the utilisation of the limited water resource. Water resource utilisation is marred by erratic rainfalls and primarily a lack of water resources management know-how [ 27 ]. Countries in the Sahelian regions are characterised by semi-arid climatic conditions. Thus, dry climatic conditions account as an IWRM strategy driver to ensure maximised water use efficiency. Although the region acknowledges the need for adopting the IWRM strategy, they have varied adoption statuses (GWP, 2003).

Southern African countries also face serious water scarcity problems. Rainfall in South Africa is low and unevenly distributed with about 9% translating to useful runoff making the country one of the most water scarce countries in the world [ 35 ]. Generally, SADC countries experience water scarcity resulting in conflicts due to increasing pressure on the fresh water resources [ 36 ]. Thus, the researched opine that water scarcity pushed the region to adopt the IWRM strategy inorder to mitigate the looming effects of climate change on surface water availainility.

3.2.2 Trans-boundary water resources.

Water resources flow downstream indiscriminately across villages, locations, regions and nations/states and therefore necessitates co-operation. The upstream and downstream relationships among communities, people and countries created by the water is asymmetrical in that the actions upstream tend to affect the downstream riparian and not the other way round [ 34 ]. In East Africa, the Nile Basin Initiative (NBI) and the Lake Victoria Basin Commission (LVBC) plays a critical component in promoting the IWRM at regional level [ 20 ].

The Nile River system is the single largest factor driving the IWRM in the region. Lake Victoria, the source of the Nile River is shared by the three East African states of Kenya, Uganda and Tanzania. Irrigation schemes in Sudan and Egypt rely exclusively on the waters of River Nile and are therefore apprehensive of the actions of upstream states notably Ethiopia, Kenya, Uganda, Tanzania, Rwanda and Burundi. The source of contention is the asymmetrical water needs and allocation which was enshrined in the Sudan–Egypt treaty of 1959 [ 37 ]. All the riparian countries in the Nile basin have agricultural-based economies and thus irrigation is the cornerstone of food security [ 38 ]. Therefore, there was the need for the establishment of basin-wide co-operation which led to the formation of NBI in 1999 with a vision to achieve sustainable socio-economic development through the equitable utilisation of the Nile water resources [ 39 ].

The Mara River is another trans-boundary river which is shared between Tanzania and Kenya and the basin forms the habitat for the Maasai Mara National Reserve and Serengeti National Park in Kenya and Tanzania, respectively, which is prominent for the annual wildlife migration. Kenya has 65% of the upper part of the basin, any development on the upstream, such as hydropower or water diversion, will reduce the water quantities and therefore affect the Serengeti ecosystem and the livelihoods of people in Tanzania [ 40 ]. The LVBC, under the East African Community, developed the Mara River Basin-wide—Water Allocation Plan (MRB-WAP) to help in water demand management and protection of the Mara ecosystem [ 41 ]. The mandate of the LVBC is to implement IWRM in Lake Victoria Basin riparian countries [ 20 ].

Other shared water basins include the Malakisi-Malaba-Sio River basin shared between Uganda and Kenya and the Kagera River basin traversing Burundi, Rwanda, Tanzania and Uganda. The two river basins form part of the Upper Nile system and are governed through the LVBC and the NBI.

The universal transboundary nature of water creates dynamics that warrant cooperation for improved water use. West Africa has 25 transboundary watercourses and only 6 are under agreed management and regulation. The situation is compounded by the fact that 20 watercourses lack strategic river-basin management instruments [ 28 ]. Unregistered rules and the asymmetrical variations associated with watercourses warranted the introduction of the IWRM principle to set equitable water sharing protocols and promote environmental flows (e-flows). The various acts signed represent an evolutionary treaty development that combines th efforts of riparian states to better manage the shared water resources (for detailed basin configuration in West Africa see [ 42 ]). Hence, adoption of the IWRM strategy driven WAWRP of 2008 ensured the coordinanted and harmonised regional water usage mechanisms.

The SADC region has 13 major transboundary river basins which calls for development of agreements on how to handle the shared water resources with the contraints of varying levels of economic development and priorities among the member states. The multi-lateral and bi-lateral agreeements on shared water resources in the SADC is hampered by the hydropolitics where economic power dynamics favour South Africa as in the case of the Orange-Senqu basin [ 43 ].

3.2.3 Donor influence.

The World Bank has been pushing for IWRM principles in the East Africa through the NBI and by pressurising Egypt to agree to co-operate with the upstream riparian countries in the Nile basin [ 38 ]. In the early 1990s, the World Bank had aligned its funding policies to include sustainable water resources management [ 44 ].

In Tanzania, Norway, through NORAD, played a key role in implementing IWRM by promoting water projects including hydropower schemes [ 45 ]. Indeed the transformation of the agricultural sector in Tanzania through Kilimo Kwanza policy of 2009 which emphasised on the commercialization of agriculture including irrigation was driven by foreign donors such as the USAID and UK’s DFID [ 26 ].

In Uganda, however, the reforms in the water sector were initiated devoid of external influence [ 46 ]. However, this assertion is countered by Allouche [ 5 ] who pointed that Uganda had become a ‘darling’ of the donor countries in the early 1990s and that DANIDA helped to develop the Master Water Plan and the country was keen to show a willingness to develop policy instruments favourable to the donor. East African countries are developing economies and therefore most of their development plans are supported by external agencies, which to some extent come with subtle ‘conditions’ such as free-market economies. In fact imposition of tariffs and other economic instruments used to implement IWRM in water supply and irrigation is a market-based approach which was favoured by the World Bank and other development agencies.

Donor aid cannot be downplayed in pushing for IWRM diffusion in low-income aid-dependent countries of West Africa. GoBF [ 47 ] reported that from the period 1996–2001, more than 80% of water-related projects were donor funded. Cherlet and Venot [ 48 ] also found that almost 90% of the water investments in Mali were funded outside the government apparatus. It can, therefore, be argued that donor-aid plays a pivotal and central role in diffusing policy and innovation in aid-depended countries because of the incentive nature it provides for the low-income countries in the sub-Sahara region.

Southern Africa’s experience with western donors including the World Bank in terms of IWRM adoption favoured the urban areas and neglected rural areas (see [ 8 ]). The National Water Act drafting process in South africa was a multi-stakeholder and intersectoral activity that brought in international consultancies. Notable IWRM drivers were Department of International Development—UK (DFID), Danish Danida, and Deustsche Gesellschaft fur Zusammernarbeit (GIZ). The DFID was instrumental in water reform allocation law whilst the GIZ and Danida were active in experimental work in the catchments [ 3 ]. On the contrary, in Zimbabwe, a lack of access to international funding and fleeting donor aid exacerbated the policy uptake as such the anticipated implementation, operationalisation and continuous feedback mechanism for policy revision and administering process was never realised.

3.2.4 Government intervention and pro-active citizenry.

This was predomint in West Africa. For example the Burkinabe government exhibited political goodwill such that in 1995 the government brought together two separate ministries into one ministry of Environment and Water thus enabling coherent policy formulation and giving the ministry one voice to speak on water matters. The dynamic innovation arena (where policy players interact) allows continuous policy revision and redesign thus water policy reform diffusion, and policy frameworks are in a perpetual state of shifting. For example, in the 1990s the Burkinabe government was engaged in several water-related projects and was continuously experimenting with local governance and privatization (from donors) [ 1 ]. This policy shift according to Gupta [ 49 ] qualifies as an innovation driver.

Burkina Faso and Mali’s adoption story is accentuated by heightened agency, the individual enthusiasm on influencing the outcome facilitated policy diffusion and can be argued to be a potential innovation diffusion driver for the IWRM policy approach in the region. The individual policy diffusion fuelled by an enthusiastic citizenry was a sure method that effectively diffused awareness around the IWRM innovation and acted as a driver of the IWRM practices in the region. Individual strategies were honed in smallholder farming institutions to diffuse the IWRM practice and drawing from the Sabatier and Jenkins-Smith [ 50 ] advocacy coalition theory, having individuals with common agendas promoted the transfer and diffusion of water reforms in parts of West Africa.

3.2.5 Legal, political and institutional incoherence.

This was a major factor which dictated the pace of IWRM implementation in Southern Africa. For example, the Fast Track Land Reform (FTLR) programme in Zimbabwe disaggregated the large-scale commercial farms and created smallholder farming [ 51 ], consequently influencing and dictating IWRM policy path. The FTLR programme had a negative impact on the spread and uptake of IWRM. A series of poor economic performance and poor policy design compounded the limited diffusion and the adoption of IWRM practices at local levels in Zimbabwe. The FTLR programme compounded the innovation diffusion process as the Zimbabwe National Water Authority (ZINWA) lost account of who harvested how much at the newly created smallholder farms. Thus, water access imbalance ensured, and ecological sustainability was compromised.

Policy incoherence was a major factor in poor IWRM diffusion and adoption, for example, the government did not synchronise the land and water reforms thus it meant at any given point in time there was a budget for one reform agenda [ 8 ] and the land reform agenda would take precedence because of political rent-seeking. IWRM in its nature couples growth to the coordinated consumption of finite resources, hence the circular approach cannot be easily realised because finte resources are at the core of the strategy’s existence.

South Africa’s transition from Integrated Catchment Management (ICM) strategies to the IWRM strategy, hindered the operationalisation and diffusion of the IWRM strategy [ 52 ]. Despite acknowledging the “integration”, researchers argued that the word lacked a clear-cut definition thus failing to establish a common ground for water’s multi-purpose use [ 53 ]. For maximised adoption of a practice, incremental innovation is required, which was Danida’s agenda in the quest to drive IWRM in South Africa. According to Wehn and Montalvo [ 54 ] incremental innovation “is characterised by marginal changes and occurs in mature circumstances”,

Land reform in South Africa is characterised by (a) redistribution which seeks to transfer land from the white minority on a willing buyer willing seller basis, (b) restitution which rights the discriminatory 1913 land laws that saw natives evicted from their ancestral land, and (c) land tenure that provides tenure to the occupants of the homelands. This new pattern created a new breed of smallholder farmers that are, more often than not, excluded from diffusion and water governance channels [ 55 ]. In addition, researchers argue that a farm once owned by one white farmer is owned by multiple landowners with different cultural backgrounds and, more often than not, IWRM strategy is met with resistance [ 56 ]. Another challenge posed by multi-cultural water users is the interpretation and translation of innovations.

To foster water as an economic good aspect of IWRM the licensing system was enacted in South Africa. The phenomenon was described by van Koppen (2012) as paper water precedes water, thus the disadvantaged black smallholder farmers could not afford paper water which consequently limits access to water. The licensing system can be interpreted as stifling the smallholder sector and hence negative attitudes develop and hinder effective policy diffusion. Another issue that negatively impacted adoption was that issuing a license was subject to farmers possessing storage facilities. The smallholder farmers lack resources hence the requirement for obtaining a license excluded the small players in favour of the large-scale commercial farmers. This consequently maintains the historically skewed status-quo, where “big players” keep winning. Van Koppen [ 57 ] and Denby, Movik [ 58 ] argue the shift from local water rights system to state-based water system have created bottlenecks making it hard for smallholder farmers to obtain “paper water” and subsequently “wet water”. The state-based system is characterised by bureaucracies and local norms are in perpetual change, hence denying the IWRM innovation policy approach stability efficiency.

A lack of political will and pragmatism amplified the poor adoption and operationalisation of IWRM, a poorly performing economy and fleeing donor agencies resulted in less funding for water-related project. Political shenanigans created an imbalance that resulted in two forms of water i.e., water as an economic good vs. water as a social good [ 59 ]. Manzungu [ 60 ] argued post-colonial Zimbabwe continuously failed to develop a peoples-oriented water reform policy. In a bid to correct historical wrongs by availing subsidised water to the vulnerable and support the new social order, the initiative goes against the neo-liberalism approach that defines the “water as an economic good” [ 61 ] which is a founding principle of IWRM.

Water redistribution in South Africa has been fraught with political and technical issues, for example, the Water Allocation Reform of 2003 failed to reconcile the apartheid disparity hence the equity component of IWRM was compromised. IWRM suffered another setback caused by the governing party when they introduced radical innovations that sought to shift from the socialist to neoliberal water resource use approach. The radical innovation through the government benefited the large-scale commercial farmers at the expense of the black smallholder farming community [ 53 ].

3.3 Systematic comparison of findings on East, West and Southern Africa

Data extracts from the respective regional analysis were formulated into theoretical candidate themes. The thematic analysis extracted recurring themes common to all the three regions. An independent reviwer performed the subjective thematic analysis and the authors performed the review on the blind thematic analysis outcome. The analysis performed a data extraction exercise and formulated codes ( Fig 2 ). Themes were then generated from the coded data extracts to create a thematic map. It is worth mentioning that the data extracts were phrases/statement from with in the literature review.

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3.3.1 Donor aid and policy approach.

Donor activity invariably influenced the policy path that individual countries took. The three regions had significant support from donors to drive the IWRM strategy. Zimbabwe experienced a different fate. The political climate caused an exodus of donor support from the nation, which consequently caused a laggard. The absence of donor support was at the backdrop of the two formulated water acts namely National Water Act [ 62 ] and the Zimbabwe National Water Authority Act of 1998 [ 63 ], which were meant to promote equitable water provision amongst the population. This highlights the latent adoption of IWRM strategy. The 2008/2009 cholera outbreak raised alarm and facilitated the return of donor activity in Zimbabwe’s water sector. The availability of donor support motivated the redrafting of a water clause in the 2013 constitution that espoused the IWRM strategy to water management [ 64 ].

Whilst Mehta, Alba [ 64 ] argue that South Africa enjoyed minimal donor support it cannot be downplayed how much donor influence impacted the IWRM strategy adoption. For instance, the Water Allocation Reform (WAR) was drafted with the aid of the UK Department of International Development. The WAR fundamentals are informed by IWRM principles. The economic structural programmes spearheaded by The World Bank and the IMF were active in facilitating the diffusion of the IWRM strategy in Kenya and Uganda. Uganda made strides because of a long-standing relationship with donor nations. The Uganda—donor relationship dates back to early 1990 where Uganda was elected to be the NBI secretariat, this in itself evidence of commitment to water policy reform [ 4 , 65 ]. Donor aid acts as an incentive and augments the low African goverments’ budgets, as such proper accountability and usage of the funds ensures that more funds come in for projected water related projects.

3.3.2 Transboundary water resources.

The Nile River system is the single largest factor driving the IWRM in the region since it is shared across several upstream and downetream nations. Irrigation schemes in Sudan and Egypt rely exclusively on the waters of River Nile and are therefore apprehensive of the actions of upstream states notably Ethiopia, Kenya, Uganda, Tanzania, Rwanda and Burundi. The source of contention is the asymmetrical water needs and allocation which was enshrined in the Sudan–Egypt treaty of 1959 [ 37 ]. Over time, the upstream countried demanded equitable share of the Nile waters and this led to the establishment of NBI. In Eastern Africa, the Nile Basin Initiative (NBI) and the Lake Victoria Basin Commission (LVBC) plays a critical component in promoting the IWRM at regional level [ 20 ]. The LVBC is deeply intertwined with the East African Community (EAC) and thus has more political clout to implement policies regarding utilization of the Lake Victoria waters [ 66 ]. This, therefore, implies that for NBI to succeed, it must have a mandate and political goodwill from the member countries.

The conflicts around the utilization of the Nile water resources persists due to the treaty of 1959 which led to the signing of Cooperative Framework Agreement (CFA) by a number of the Nile basin countries, with the notable exceptions of Egypt, Sudan and South Sudan [ 67 ]. The CFA was signed between 2010 and 2011 and establishes the principle that each Nile Basin state has the right to use, within its territory, the waters of the Nile River Basin, and lays down some factors for determining equitable and reasonable utilization such as the contribution of each state to the Nile waters and the proportion of the drainage area [ 68 ]. The construction of the Grand Ethiopian Renaissance Dam has been a source of concern and conflict among the three riparian countries of Ethiopia, Sudan and Egypt [ 67 ]. The asymmetrical power relations (Egypt is the biggest economy) in the Nile Basin is a big hindrance to the co-operation among the riparian countries [ 69 ] and thus a threat to IWRM implementation in the shared watercourse. While Ethiopia is using its geographical power to negotiate for an equitable share in the Nile water resources, Egypt is utilizing both materials, bargaining and idealistic power to dominate the hydro politics in the region and thus the former can only succeed if it reinforces its geographical power with material power [ 70 ].

Therefore, IWRM implementation at the multi-national stage is complex but necessary to forestall regional conflicts and war. The necessity of co-operation rather than conflict in the Nile Basin is paramount due to the water availability constraints which is experienced by most countries in the region. The transboundary IWRM revolves around water-food- energy consensus where the needs of the riparian countries are sometimes contrasting, for example, Egypt and Sudan require the Nile waters for irrigation to feed their increasing population while Ethiopia requires the Nile waters for power generation to stimulate her economy. The upstream riparian States could use their bargaining power to foster co-operation and possibly force the hegemonic downstream riparian States into the equitable and sustainable use of Nile waters [ 71 ].

The SADC region has 13 major transboundary river basins (excluding the Nile and Congo) of Orange, Limpopo, Incomati, Okavango, Cunene, Cuvelai, Maputo, Buzi, Pungue, Save-Runde, Umbeluzi, Rovuma and Zambezi [ 72 ]. The Revised Protocol on Shared Watercourses was instrumental for managing transboundary water resources in the SADC. The overall aim of the Protocol was to foster co-operation for judicious, sustainable and coordinated management, the protection and utilization of shared water resources [ 73 ].

Ashton and Turton [ 74 ] argue that the transboundary water issues in Southern Africa revolved around the key roles played by pivotal States and impacted States and their corresponding pivotal basins and impacted basins. In this case, pivotal States are riparian states with a high level of economic development (Botswana, Namibia, South Africa, and Zimbabwe) and a high degree of reliance on shared river basins for strategic sources of water supply while impacted States are riparian states (Angola, Lesotho, Malawi, Mozambique, Swaziland, Tanzania, and Zambia) that have a critical need for access to water from an international river basin that they share with a pivotal state, but appear to be unable to negotiate what they consider to be an equitable allocation of water and therefore, their future development dreams are impeded by the asymmetrical power dynamics with the pivotal states. Pivotal Basins (Orange, Incomati, and Limpopo) are international river basins that face closure but are also strategically important to anyone (or all) of the pivotal states by virtue of the range and magnitude of economic activity that they support. Impacted basins (Cunene, Maputo, Okavango, Cuvelai, Pungué, Save-Runde, and Zambezi) are those international river basins that are not yet approaching a point of closure, and which are strategically important for at least one of the riparian states with at least one pivotal State.

The transboundary co-operation under IWRM in Southern Africa is driven mainly by water scarcity which is predominant in most of the SADC countries which may imply the use of inter-basin transfers schemes [ 74 ]. Further, most of the water used for agriculture, industry and domestic are found within the international river basins [ 75 ] which calls for collaborative water management strategies. The tricky feature hindering the IWRM is the fact that States are reluctant to transfer power to River Basin Commissions [ 76 ]. Indeed most of the River Basin Organizations (RBO) in Southern region such as the Zambezi Commission, the Okavango River Basin Commission, and the Orange-Sengu River Basin Commission have loose links with SADC and therefore lack the political clout to implement the policies governing the shared water resources [ 66 ]. Power asymmetry, like in Eastern Africa, is also a bottleneck in achieving equitable sharing of water resources as illustrated by the water transfer scheme involving Lesotho and South Africa [ 77 ]. The hydro-hegemonic South Africa is exercising control over any negotiations and agreements in the Orange-Senqu basin [ 43 ]. Limited data sharing among the riparian States is another challenge which affects water management in transboundary river basins e.g. in the Orange-Senqu basin [ 78 ].

West Africa has 25 transboundary watercourses and only 6 are under agreed management and regulation. The situation is compounded by the fact that 20 watercourses lack strategic river-basin management instruments [ 28 ]. Unregistered rules and the asymmetrical variations associated with watercourses warrant the introduction of the IWRM principle to set equitable water sharing protocols and promote environmental flows (e-flows). The various acts signed represent an evolutionary treaty development that combines the efforts of riparian states to better manage the shared water resources. It is important to note that evolutionary treaties are incremental innovation. Water Resources Coordination Centre (WRCC) was established in 2004 to implement an integrated water resource management in West Africa and to ensure regional coordination of water resource related policies and activities [ 79 ].

The Niger River basin covers 9 Countries of Benin, Burkina, Cameroon, Chad, Cîte d’Ivoire, Guinea, Mali, Niger and Nigeria. The Niger River Basin Authority (NBA) was established to promote co-operation among the member countries and to ensure basin-wide integrated development in all fields through the development of its resources, notably in the fields of energy, water resources, agriculture, livestock, forestry exploitation, transport and communication and industry [ 80 ]. The Shared Vision and Sustainable Development Action Programme (SDAP) was developed to enhance co-operation and sharing benefits from the resources of River Niger [ 81 ]. The Niger Basin Water Charter together with the SDAP are key instruments which set out a general approach to basin development, an approach negotiated and accepted not only by all member states but also by other actors who utilize the basin resources [ 82 ].

The main agreement governing the transboundary water resource in River Senegal Basin is the Senegal River Development Organization, OMVS (Organisation pour la mise en valeur du fleuve Sénégal) with its core principle being the equitably shared benefits of the resources of the basin [ 82 ]. The IWRM in the Senegal River Basin is hampered by weak institutional structures and lack of protocol on how shared waters among the States as well as conflicting national and regional interests [ 83 , 84 ]. The Senegal River Basin, being situated in the Sudan-Sahelian region, is faced by the threat of climate change which affects water availability [ 84 ] The Senegal River Basin States have high risks of political instability.

3.4 Prospects of IWRM Africa

The countries in the three regions are at different stages of implementation ( Table 4 ). In East Africa, Uganda and Kenya are at medium-high level while Tanzania is medium-low. Majority of the countries in the Southern Africa region are at medium low. Comoros Islands is the only country at low level of implementation in the region. West African countries are evenly spread between low, medium-low and medium-high levels of implementation. Generally, East Africa is ranked as medium-high level with average score of 54% while Southern Africa and West Africa are ranked as medium low-level at 46% and 42% respectively. However if you include, medium low countries of Rwanda, Burundi, Ethiopia and South Sudan and the low-level Somalia, then East Africa’s score drops to 39% (medium-low).

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The implementation of IWRM in the continent, and more so the inter dependent and multi purpose water use sectors, will continue to evolve amid implementation challenges. The dynamics of water policies, increased competition for finite water resources from rapid urbanization, industrialization and population growth will continue to shape IWRM practices in the region. Trans-boundary water resources management will possibly take centre stage as East African countries move towards full integration and political federation as envisaged in the four pillars of the EAC treaty. Decision support tools such as the Water—Energy—Food (WEF) nexus appraoch will be very relevant in the trans-boundary water resources such as the Nile system, Mara and Kagera river basins. The approach can potentially ameliorate the after effects of the devolved governance system in Kenya that consequently created a multiplicity of transboundary sectors.

Adoption of the IWRM policy in West Africa is fraught with many challenges. For example, despite having significant water resources, the lack of a collective effort by the governments to train water experts at national level presents a challenge for adoption. Unavailability of trained water experts (who in any case are diffusion media) results in a lack of diffusion channels that facilitate policy interpretation, translation and its subsequent implementation. Helio and Van Ingen [ 27 ] pointed out how political instability possesses a threat to current and future implantation initiatives. The future collaboration projects and objective outlined by ECOWAS, CILSS, and UEMO highlight a major effort to bring the region to speed with the IWRM policy approach. The WAWRP objectives can potentially set up the region on an effective IWRM trajectory which can be mimicked and upscaled in other regions. Positives drawn from the region are the deliberate institutional collaborations. Burkina Faso and Mali have the potential to operationalise and facilitate policy diffusion to other neighbouring states. Donor driven reform is essential and national ownership is critical in ensuring the water reform policies and innovation diffusion processes are implemented at the national level.

The IWRM policy approach and practice in South Africa was government-driven whereas in Zimbabwe external donors were the main vehicles for diffusion. For both countries, the water and land reform agenda has a multiplicity of overlapping functionaries; however, they are managed by separate government departments. The silo system at national level prevents effective innovation diffusion and distorts policy interpretation and the subsequent dissemination at the local level.i.

Water affairs are politicised and often, the water reform policy fails to balance the Dublin’s principles which form the backbone of the IWRM innovation policy approach. Failure by national governments to address unequal water access created by former segregationist policies is perpetuated by the lack of balance between creating a new social order and recognising the “water as an economic good” principle.

4 Conclusion

Africa as a laboratory of IWRM produced varied aggregated outcomes. The outcomes were directly linked to various national socio-economic development agendas; thus, the IWRM policy took a multiplicity of paths. In East Africa, Kenya is still recovering from the devolved system of government to the County system which created new transboundary sectors with the country. Water scarcity, trans-boundary water resource and donor aid played a critical role in driving the IWRM policy approach in the three regions. Southern Africa’s IWRM experience has been fraught with policy clashes between the water and land reforms. Similar to Africa, the transboundary issue in Europe and Asia and the subsequent management is a major buy-in for formulating water resources strategies that are people centric and ecologically friendly. Global water scarcity created fertile grounds for IWRM adoption in Asia, specifically India. Thus, we postulate that some of the drivers that influenced the uptake and diffusion in Africa are not only unique to the continent.

For the future, IWRM policy approach can be implemented in Africa and the continent has the potential to implement and adopt the practice. Endowed with a significant number of water bodies, Africa must adopt a blend of IWRM strategy and the water energy food nexus (WEF) for maximising regional cooperation and subsequent economic gains. WEF nexus will help combat a singular or silo approach to natural resources management. WEF nexus and IWRM is a fertile area for future research as it brings a deeper understanding of the trade-offs and synergies exsisting in the water sector across and within regions. In addition, the WEF nexus approach can potentially facilitate a shift to a circular approach that decouples over dependence on one finte resource for development.

Supporting information

S1 checklist..

https://doi.org/10.1371/journal.pone.0236903.s001

S1 Table. Data extracts with the applied codes.

https://doi.org/10.1371/journal.pone.0236903.s002

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Today, most countries are placing unprecedented pressure on water resources. The global population is growing fast, and estimates show that with current practices, the world will face a 40% shortfall between forecast demand and available supply of water by 2030. Furthermore, chronic water scarcity, hydrological uncertainty, and extreme weather events (floods and droughts) are perceived as some of the biggest threats to global prosperity and stability. Acknowledgment of the role that water scarcity and drought are playing in aggravating fragility and conflict is increasing.

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Feeding 10 billion people by 2050 will require a 50% increase in agricultural production , (which consumes 70% of the resource today), and a 15% increase in water withdrawals. Besides this increasing demand, the resource is already scarce in many parts of the world. Estimates indicate that over 40% of the world population live in water scarce areas, and approximately ÂŒ of world’s GDP is exposed to this challenge. By 2040, an estimated one in four children will live in areas with extreme water shortages . Water security is a major – and often growing –challenge for many countries today.

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Robust water resource management solutions to complex water issues incorporate cutting-edge knowledge and innovation, which are integrated into water projects to strengthen their impact. New knowledge that draws on the World Bank Group’s global experiences, as well as partner expertise, are filling global knowledge gaps and transforming the design of water investment projects to deliver results. Multi-year, programmatic engagements in strategic areas are designed to make dramatic economic improvements in the long term and improve the livelihoods of millions of the world’s poorest people.

The Water Security Diagnostic Initiative is an analytical framework that can be used to examine the status and trends related to water resources, water services, and water-related risks, including climate change, transboundary waters, and virtual water trade. The framework helps countries determine if and to what extent water-related factors impact people, the economy, and the environment, and determine if and to what extent water-related factors provide opportunities for development and well-being.

The World Bank is proactively working to address new global challenges, by adapting its operations to reach those that most need it today. Working across sectors is ensuring that water considerations are addressed in energy, the environment, agriculture, urban and rural development, and within new global challenges. The Bank also supports transformational engagements and initiatives, which seek to optimize spatial, green, and co-benefits among water and other infrastructure sectors. A large proportion of World Bank-funded water resources management projects include institutional and policy components.

Recent initiatives include:

  • Through the Federal Integrated Water Sector Project (INTERÁGUAS) , Brazil's federal government sought to integrate the water sector by improving coordination among and strengthening the capacity of the sector’s key federal institutions. In an ambitious innovation, the World Bank supported the government by helping to bring together the most important federal water sector agencies while supporting ongoing water reforms and institutional strengthening.
  • The integration of nature-based solutions in the Bank’s water infrastructure projects has helped place a spotlight on the world’s growing infrastructure crisis, driven by climate change and growing populations. Embedding nature-based solutions into project designs can help deliver infrastructure services with greater impact and lower cost, all the while reducing risks from disaster, boosting water security and enhancing climate resilience.
  • The publication of a National Framework for Integrated Urban Water Management in Indonesia , focuses on the potential for IUWM to address the severe and interrelated water security challenges faced by Indonesian cities.
  • The Second Public Employment for Sustainable Agriculture and Water Management Project (PAMP II) supported the Government of Tajikistan in improving water resource management at local, basin and national levels, and in increasing crop yields through improved irrigation management. Key to improved irrigation was rehabilitation of irrigation and drainage infrastructure and support to Water Users Associations, which are community-based organizations linking farmers with irrigation service provider.
  • The Water Management and Development Project in Uganda improved the integration of water resources planning, management and development, as well as access to water and sanitation services in priority urban areas. More than 1.01 million people received access to improved water sources, and 25,000 piped household water connections were rehabilitated from 2012-2018.

With 263 international rivers in the world, support for cooperative transboundary water management can make an important contribution towards improving the efficient and equitable management of water resources. The Bank supports transboundary waters through Multi-Donor Trust Funds (MDTF), knowledge pieces, and its lending portfolio:

  • Central Asia Water & Energy Program ( CAWEP ) is a MDTF administered by the World Bank and financed by the European Commission, the Swiss State Secretariat for Economic Affairs, UK AID, and DFID. The MDTF is building energy and water security by leveraging the benefits of enhanced cooperation in Central Asia, including all five Central Asian countries plus Afghanistan.
  • The Cooperation for International Waters in Africa (CIWA) is a MDTF administered by the World Bank and financed by Denmark, European Commission, the Netherlands, Norway, Sweden, and the United Kingdom. The trust fund finances upstream work in African International Rivers, 75% of which go to four priority basins – Nile, Niger, Volta, and Zambezi.
  •  The South Asia Water Initiative (SAWI) is a MDTF administered by the World Bank and financed by the governments of the United Kingdom, Australia, and Norway in South Asia. The trust fund provides recipient executed grants to initiatives in the major Himalayan River systems – the Indus, the Ganges, and the Brahmaputra.
  • In the Mekong River Basin, the Bank is supporting riparian states such as Cambodia , the Lao People’s Democratic Republic , and Vietnam in strengthening their integrated water resource management and disaster risk management capacities, cooperating closely with the basin-wide Mekong River Commission.
  • The Bank is also investing in knowledge pieces such as ROTI ( Retooling Operations with Transboundary Impacts ) to identify tools that promote riparian country coordination aimed at mitigating transboundary harm and leveraging benefits of investments in transboundary basins.

The Bank follows an integrated flood management agenda, which includes well-functioning early warning systems, infrastructure, and institutional arrangements for coordinated action to address increased variability and changes to runoff and flooding patterns.  In addition, a new perspective, referred to as an "EPIC Response," is offered to better manage hydro-climatic risks: This perspective looks at floods and droughts not as independent events but rather as different ends of the same hydro-climatic spectrum that are inextricably linked. The EPIC response provides a comprehensive framework to help national governments lead a whole-of-society effort to manage these risks.

Water scarcity is also addressed in:  

  • The Water Scarce Cities Initiative , initially focusing on the Middle East and North Africa ( MENA ) region, seeking to bolster the adoption of integrated approaches to managing water resources and service delivery in water scarce cities as the basis for water security and climate resilience.
  • Small Island States . The challenges and innovations of water management in small island states can be particularly vivid. These countries warrant particular attention not only because they are often neglected, but also because they provide an opportunity to focus on intensive reuse and non-conventional water resources development, which will be increasingly important knowledge for implementation in megacities and extremely water scarce settings. A scoping study is proposed on the state-of-the-art and the Bank’s portfolio.

Sustainable groundwater management is also a priority of the World Bank, and central to water security in many countries.

  • Recognizing that groundwater is being depleted faster than it is replenished in many areas, the World Bank has collaborated with key global partners through years of consultations to develop a framework for groundwater governance. The 2030 Vision and Global Framework for Action represents a bold call for collectively responsible action among governments and the global community to ensure sustainable use of groundwater.

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Water Resource Management: How to Save Water Resources Essay

Water management is an important of pollution control and environmental management policies. The domestic regimes for maritime law and policy arise from a number of disparate sources including relevant international treaties and instruments, the Constitution, the Offshore Constitutional Settlement and our sectoral-based approach to marine management. As a result of our system of government, there are a number of government departments and agencies which have an interest in pollution, dumping and maritime accidents in the marine environment. Since there are no national borders in the atmosphere, pollutants disperse over the entire Earth although taking a long time to create damage. Thus the distantly intimate link today between Japan and Argentina. In this regard, the issue of ozone layer depletion makes us aware of the importance of the planetary interest. It is indispensable for us to have international frameworks in order to sustainably utilize the atmosphere, oceans and natural resources without polluting water, without exhausting resources and without destabilizing the ecological balance of the planet. In this regard, the Montreal Protocol is a valuable legal document since it lays down ways to reduce or abolish the production of specific substances in a concrete manner, allows for the reduction schedule to differ between developed and developing countries and stipulates ways of channeling financial support. Water si renewable resource but it requires time to purify and sanitize it.

In order to address the environmental problem, which is becoming increasingly globalized, we must grasp internationally the reality of the problem, set up measures that take into account technical and economic capacities, provide legal frameworks and follow-up and review measures. To this end, I hope that international environmental organizations such as UNEP will be strengthened further. We are now facing environmental problems which transcend national borders, while we still have an international system based on the sovereign nation-state. We need to address the difficult problems of evaluating and protecting the global commons, which are complicated and interrelated while maintaining the free trade systems of the world. The planetary interest concept will be useful in helping us to realize this goal in the twenty-first century (Arlosoroff, 1995).

A rough assessment of the four major human requirements shows that the current appropriation of natural resources and services already exceeds Earth’s long-term carrying capacity. Agriculture already occupies 4.8 billion hectares (3.3 billion hectares of pasture and 1.5 billion hectares of cropland). Sustainable production of the current round-wood harvest, including firewood, would require a productive forest area of 1.7 billion hectares. To sequester the excess co 2 released by fossil fuel combustion, a further 3.1 billion hectares of carbon-sink land would need to be set aside. This totals 9.6 billion hectares, some 30% above what is available today, and 10% above all potential land. The “sustainability deficit” or “ecological deficit” is a measure of overshoot (van der Straaten, 1994). The “global ecological deficit”, unlike “national ecological deficits”, cannot be subsidized through trade and draw-down from other surplus countries. It depends instead on the liquidation of natural capital stock. It cannot be spatial, imposing the burden on other areas at a single point in time. It can only be temporal, imposing the burden on future generations. The current generation, then, is drawing down on Earth’s natural resource base at an unprecedented rate. If this continues, today’s inhabitants of Earth will leave a degraded planet for future generations—possibly to an irretrievable degree. Without a concerted effort today to reduce material throughput, the generations of the twenty-first century will be left to satisfy their needs from a much-diminished stock of natural capital From this work it is clear that the ecological footprint of the North exceeds its fair “EarthShare” by a factor of two to three. If all humanity maintained the same consumption pattern, three planets would be required to satisfy aggregate demand, on current technology. In the words of the authors (van der Straaten, 1994).

Sustainability turns equally on each of these factors. But the international community has not yet demonstrated an equal commitment to each. The term “sustainable development” tends to prioritize development overconsumption. While the UN conference at Rio addressed development (along with the environment) and Cairo stressed population (along with development), no global conference has to date focused on consumption. The result is a lack of clarity over the global limits to Earth’s carrying capacity and an implicit political premise that there is no limit or that the constraints are considerably elastic. Two decades ago we experienced the Green Revolution—a breakthrough in the rice yield and at the same time a significant increase in the use of water, insecticides and pesticides. Productivity increased by a factor of two. It was just as well for this also allowed us to keep pace with the population growth which doubled in this period and yet people did not starve. A more important conflict has shown up recently (Lee, 1994). On the one hand, there is a lucrative shrimp culture in the bay areas along the coastlines which are resulting in the depletion of the naturally occurring post-larvae of shrimp. On the other hand, this is resulting in brackish water pools along our southern coasts, thus destroying the more environment-friendly paddy fields and resulting in massive land degradation of coastal areas. Consequently, open water, as well as marine fishery management systems, have to be considered in careful detail with a view to increased productivity and sustainability involving the fish population dynamics (Björnlund and McKay 2006).

Artesian water has its own problems. There is arsenic poisoning in the ground around the wells and the sub-soil water is drained off to support irrigation for modern agriculture. People dig deeper but the concentration of arsenic in the water has risen to dangerous levels already resulting in fatal diseases. And in the southwestern part of the country, there is a different problem with the soil. We could further develop the Sundarbans, the world’s largest mangrove forest in the Ganges delta (Bateman et al 2005). Thanks to UNESCO for its belated inclusion in the list of world heritage. But the Sundarbans already suffer from “top-dying”—the leaves at the top of the trees are dying away due to the increased salinity of the soil resulting from the massive withdrawal of the water at the upper reaches of the Ganges. More recently, however, some flood control projects have upset the natural balance, in many cases resulting in man-made flash flooding and other ecological imbalances. On top of the surface water system management which had its own shortcomings, severe depletion of the groundwater resource in Bangladesh resulted from irrigation water needs for the HYVS. These two apparently distinct yet interrelated areas of surface water and groundwater systems have already seriously impacted the environmental aspects of Bangladesh (Andreoni, 1990).

Expressed differently, the international community can realize hope for the planet’s future only by subjecting excessively selfish interests to the vital planetary interest. This will take care of Earth’s environmental integrity as each nation-state, in turn, takes care of its own environmental integrity. Excessively affluent consumption styles to be found in industrialized countries have been, until recently, basically selfish. But the acceptance by the same countries of some system of a just distribution of wealth in the interests of poorer countries is a step forward towards global environmental conservation (Amin, 1994). Equally, excessive dependence on over-grazing, deforestation and surface water erosion in the developing countries is environmentally extractive and scarcely survivalist. Kenya is a signatory to the UN declarations and action programs that address the environment and development. It has been argued that the North should contribute more towards the costs of rectifying the damage to the planet from air and water pollution. And it has been argued that no sustainable development can take place in a world sharply divided into the affluent North and the deprived South (Allan and Karshenas 1995). Kenya’s national policies have revolved around the alleviation of poverty, the attainment of high educational standards, modest population growth, health for all including clean drinking water by the year 2000 and, now, industrialization. The National Development Plan, 1997-2001, contains four policy objectives central to sustainable development. In the agricultural sector, budgetary increases will ensure increased productivity, additional storage and processing plants and intensification of extension services in an effort to achieve food security. In population, it contains measures to accelerate the decline in the fertility rate. In health, policies for the alleviation of past constraints of underfunding, low staffing and uneven distribution of personnel by 1999. In the shelter, the attainment of adequate housing for all while ensuring sustainable rural settlement and urbanization (Allan 1995).

In sum, water is a renewable resource but it cannot restore in a short period of time. In order, to save water resources and the planet it is crucial to introduce strict policies and protection measures against water pollution.

List of References

Allan, J.A. 1995. The political economy of water: reasons for optimism but long term caution. Nature (1995:33-58).

Allan, J.A. & M. Karshenas 1995. Managing environmental capital: the case of water in Israel, Jordan, the West Bank and Gaza, 1947-1995. Nature 32, 25.

Amin, A. 1994. Corporate concentration and interdependence in Europe. Environmental Protection 1994: 85-91).

Andreoni, J. 1990. Impure altruism and donations to public goods: a theory of warm-glow-giving. Economic Journal 100 , 464-77.

Arlosoroff, S. 1995. Managing scarce water-recent Israeli experience. Economic Journal (1995:21-8).

Bateman, I., I. Langford, A. Graham 2005. A survey of non-users’ willingness to pay to prevent saline flooding in the Norfolk Broads . Working Paper GEC 95-11, CSERGE, University of East Anglia.

Björnlund, H. & J. McKay 2006. Can water trading achieve environmental goals? Water , 31-4.

Lee, F. 1994. Administered prices. Environmental Protection 1994: 4-9.

Randall, A. 1981. Property entitlements and pricing policies for a maturing water economy. Australian Journal of Agricultural Economics 25 (3), 195-220.

Van der Straaten, J. 1994. The distribution of environmental costs and benefits: the case of acid rain . Paper 94.09.037/2, Work and Organization Research Centre, University of Tilburg.

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Essay on Water Resources

Students are often asked to write an essay on Water Resources in their schools and colleges. And if you’re also looking for the same, we have created 100-word, 250-word, and 500-word essays on the topic.

Let’s take a look


100 Words Essay on Water Resources

What are water resources.

Water resources are sources of water that are useful or potentially useful to humans. They include groundwater, rivers, lakes, and collected rainwater.

Importance of Water Resources

Water resources are essential for survival. They provide drinking water, irrigation for crops, and power for industries. Without water resources, life as we know it would not exist.

Threats to Water Resources

Water resources are under threat from pollution, overuse, and climate change. This can lead to water scarcity, affecting people, animals, and plants.

Conserving Water Resources

It’s crucial to conserve water resources. This can be done by reducing water usage, recycling water, and protecting water sources from pollution.

Also check:

  • 10 Lines on Water Resources
  • Speech on Water Resources

250 Words Essay on Water Resources

Introduction.

Water resources refer to the supply of groundwater and surface water in a given area. They are fundamental to life, ecosystems, and economies, playing a vital role in agriculture, industry, household chores, and maintaining biodiversity.

Significance of Water Resources

Water resources are essential for sustaining life and promoting development. They contribute to food security by providing water for irrigation, enabling crop production. Moreover, they facilitate various industrial processes, including cooling, dilution, and transportation.

Challenges to Water Resources

Despite their importance, water resources are under threat due to overuse, pollution, and climate change. Over-extraction for agriculture and industry is depleting groundwater reserves, while pollution from human activities is contaminating both surface and groundwater. Climate change is exacerbating these issues, altering precipitation patterns and increasing the frequency of extreme weather events.

Water Resource Management

Effective management of water resources is critical. This involves balancing the competing demands of different sectors, ensuring equitable access, and protecting the natural environment. Strategies include water conservation, pollution control, and the use of technology to enhance water efficiency.

In conclusion, water resources are invaluable, underpinning a wide range of social, economic, and environmental functions. However, they are under increasing pressure, and their sustainable management is a pressing global challenge. Through collective action and innovative solutions, we can ensure the continued availability of these vital resources for future generations.

500 Words Essay on Water Resources

Water resources are an essential aspect of our planet, playing a crucial role in supporting life and maintaining ecological balance. These resources, including rivers, lakes, oceans, and groundwater, serve multiple purposes, from being a source of drinking water to supporting agriculture and industry.

The Importance of Water Resources

Water resources are fundamental to human survival and development. They provide water for drinking, sanitation, and food production, making them indispensable for human health and food security. Moreover, water resources are crucial for energy production, as hydropower is a significant source of renewable energy.

Challenges Facing Water Resources

Despite their importance, water resources face numerous challenges. Overexploitation, pollution, and climate change are the primary threats. Overuse of water resources, especially for irrigation, often leads to water scarcity. Pollution, mainly from industrial and agricultural activities, affects the quality of water, making it unsafe for consumption and damaging aquatic ecosystems. Climate change exacerbates these challenges by altering precipitation patterns, leading to either droughts or floods.

Conservation of Water Resources

Given these challenges, conserving water resources is paramount. This conservation can be achieved through sustainable water management practices. These include efficient water use, reducing water pollution, and implementing measures to mitigate the impacts of climate change. For instance, promoting water-efficient technologies in agriculture and industries can substantially reduce water use. Similarly, stringent regulations can help minimize water pollution.

The Role of Technology in Water Resource Management

Technology plays a significant role in managing water resources. Advanced technologies, such as remote sensing and Geographic Information Systems (GIS), are used to monitor water resources, assess their status, and predict future trends. These technologies enable the identification of areas of water scarcity, helping to target interventions effectively. Furthermore, technological innovations, such as water recycling and desalination, can help to augment water supplies, especially in water-scarce regions.

In conclusion, water resources are vital for human survival and socio-economic development. However, they face significant challenges, including overexploitation, pollution, and climate change. Therefore, there is an urgent need for sustainable water management practices, which can be facilitated by leveraging technology. By doing so, we can ensure the availability and sustainable management of water resources for present and future generations.

That’s it! I hope the essay helped you.

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Home — Essay Samples — Environment — Water — The Importance of Water: The Vital Essence

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The Importance of Water: The Vital Essence

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Published: Sep 7, 2023

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Table of contents

Water and human health, environmental balance, agriculture and food security, industrial and economic significance, challenges of water scarcity and pollution, responsible water management.

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Essay on Water Conservation: Samples in 150, 200, 250 Words

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Essay on Water Conservation

What makes you curious to write an essay on water conservation? This life-saving resource is essential for all forms of life on Earth. Water is the essential natural resource present on Earth. Out of the total water present on Earth, 97.5% is salt water and 2.5% is fresh water. 70% of the human body is made of water. But, with the growing population , and climatic crisis , we are facing the urgent need to conserve water.

essay on water resources management

Water conservation is a hot topic, if you need a sample essay on water conservation then, you are at the right place. In this blog post, we have covered essays on water conservation in 100, 200, and 250 words. So, stay tuned and read further to get some ideas about water conservation!

Table of Contents

  • 1 Essay on Water Conservation in 100 Words
  • 2 Essay on Water Conservation in 200 Words
  • 3.1 Water Scarcity
  • 3.2 Ways to Conserve Water

Also Read: World Water Day

Essay on Water Conservation in 100 Words

Water is crucial for all components of life which makes it a necessary resource for day-to-day activities. We use water for domestic activities like cooking, bathing, drinking, washing, etc. So, ultimately the consumption of water is very high. This makes it necessary to conserve water. Just as air, water is also important for life. Besides, water consumption, water pollution, and water scarcity are also some of the major water-related issues that need attention so that we can conserve water.

Every year we celebrate World Water Day on 22 March. This day is celebrated to spread awareness about the importance of water and run campaigns to conserve water on Earth. There are several ways to conserve water such as switching to showers, turning off taps when not in use, don’t pollute water bodies, storing rainwater, etc.

Also Read: Essay on Water Pollution

Essay on Water Conservation in 200 Words

Water is one of the Earth’s most precious resources. But the world is facing water scarcity. As per the SDA report 2022, around 2 billion people worldwide are lacking safe drinking water. This means they are more vulnerable to diseases and unhealthy life. 

Apart from the increasing population, climatic change is also hampering the quality of water. Floods and Droughts are more frequent due to the vulnerability of climate, thereby increasing the need to conserve water.

Water conservation is vital to meet the growing global demand for fresh water. Water consumption is very high for agriculture, industry, and households. By conserving water, we can ensure that there is a surplus amount of water to use and avoid conflicts over this limited resource.

Water conservation helps to maintain a balance in the ecosystem because every living thing on this planet is directly associated with the use of water. Reducing water consumption reduces the energy footprint associated with water supply.

The best ways of water conservation are rainwater harvesting , installing water plants, reusing water for gardening purposes, turning off taps when not in use, proper irrigation, installing automatic tap shut-off devices, not polluting water sources, and many more.

If we don’t want to witness the world die due to water scarcity then, it’s high time to conserve water and save the planet and future generations.

Also Read: Essay on Save Water

Also Read: Speech on Save Water

Water Conservation Essay 250 Words

Water conservation is a crucial step in protecting the environment. It is an important compound that supports life on Earth. The world has been facing water-related disasters due to scarcity of freshwater. 70% of the earth as well as the human body is composed of water, but there is a limited amount of freshwater to use. Owing to the ever-increasing population, climatic changes, global warming, and pollution, the need for the conservation of water is increasing. To do so, it is our fundamental duty to conserve water by planting more trees, managing water plants, storing rainwater, and making smart use of water. 

Water Scarcity

Water scarcity is a critical global issue that needs strict attention when the demand for freshwater exceeds the available supply of water. It can manifest in various ways, including a lack of access to clean drinking water, inadequate water for agriculture and industrial processes, and stressed or depleted natural water sources. 

Here are some factors that contribute to water scarcity:

  • Climate change
  • Growing population
  • Global warming
  • Inefficient water management
  • Water pollution
  • Increasing demand
  • Poor irrigation techniques
  • Wastage of water, and much more.

Ways to Conserve Water

Conserving water is crucial to help address water scarcity and ensure a sustainable water supply for both present and future generations. You can contribute individually by taking small measures to conserve water like turning off the tap. Likewise, here are some ways to conserve water:

  • Drip irrigation technique
  • Soil management
  • Plantation of drought-tolerant crops
  • Apply Mulching
  • Recycle and reuse water
  • Rainwater harvesting
  • Desalination
  • Spread awareness to conserve water
  • Donate to the water cleaning campaign
  • Implement proper water management techniques.

Also Read: Types of Water Pollution

Related Articles:

Water conservation is the individual or collective practice of efficient use of water. This helps in protecting the earth from the situation of water scarcity. We can individually contribute to water conservation by not wasting water, reducing the over-consumption of water, rainwater harvesting, etc. Water conservation is an important call because there is a limited amount of fresh water available on earth.

Here are 10 ways to save water. 1. Rainwater harvesting 2 Install water plants 3. Reuse water 4. Maintain proper water management plans 5. Fix the irrigation system 6. Use a bucket 7. Turn off the tap when not in use 8. Keep a regular check on pipe leakage 9. Do not pollute water bodies 10. Participate in water cleaning campaigns

Here are 5 points on the importance of water conservation: It helps the ecosystem; Water conservation is necessary for drought-prone areas; It helps reduce costs; Water conservation improves the quality of water; and Maintains the health of the aquatic ecosystem.

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Water Resources Management Essays

Water resources and the ongoing regional droughts, floods, and fires, popular essay topics.

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Integrated Water Resources Management Essay Example

Integrated Water Resources Management Essay Example

  • Pages: 2 (486 words)
  • Published: December 6, 2016
  • Type: Case Study

Water is a key driver of economic and social development while it also has a basic function in maintaining the integrity of the natural environment. However water is only one of a number of vital natural resources and it is imperative that water issues are not considered in isolation. Managers, whether in the government or private sectors, have to make difficult decisions on water allocation. More and more they have to apportion diminishing supplies between ever-increasing demands.

Drivers such as demographic and climatic changes further increase the stress on water resources. The traditional fragmented approach is no longer viable and a more holistic approach to water management is essential. This is the rationale for the Integrated Water Resources Management (IWRM) approach that has now been accepted internationally as the way forward for efficient, equitable and sus

tainable development and management of the world's limited water resources and for coping with conflicting demands.

There are great differences in water availability from region to region - from the extremes of deserts to tropical forests. In addition there is variability of supply through time as a result both of seasonal variation and inter-annual variation. All too often the magnitude of variability and the timing and duration of periods of high and low supply are not predictable; this equates to unreliability of the resource which poses great challenges to water managers in particular and to societies as a whole.

Most developed countries have, in large measure, artificially overcome natural variability by supply-side infrastructure to assure reliable supply and reduce risks, albeit at high cost and often with negative impacts on the environment and sometimes o

human health and livelihoods. Many less developed countries, and some developed countries, are now finding that supply-side solutions alone are not adequate to address the ever increasing demands from demographic, economic and climatic pressures; waste-water treatment, water recycling and demand management measures are being introduced to counter the hallenges of inadequate supply.

Stages in IWRM planning and implementation In addition to problems of water quantity there are also problems of water quality. Pollution of water sources is posing major problems for water users as well as for maintaining natural ecosystems. In many regions the availability of water in both quantity and quality is being severely affected by climate variability and climate change, with more or less precipitation in different regions and more extreme weather events.

In many regions, too, demand is increasing as a result of population growth and other demographic changes (in particular urbanization) and agricultural and industrial expansion following changes in consumption and production patterns. As a result some regions are now in a perpetual state of demand outstripping supply and in many more regions that is the case at critical times of the year or in years of low water availability. Sources: Status Report on Integrated Water Resources Management and Water Efficiency Plans. UN-Water. 2008 Roadmapping for Advancing Integrated Water Resources Management (IWRM) Processes.

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essay on water resources management

An International Journal - Published for the European Water Resources Association (EWRA)

Impact of Climate Change on Water Diversion Risk of Inter‑Basin Water Diversion Project

essay on water resources management

Single-Objective and Multi-Objective Flood Interval Forecasting Considering Interval Fitting Coefficients

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essay on water resources management

Uncertainty Analysis of Optimal Instruction for WDN Pipes Repair and Replacement Using Fuzzy α-cut - hydraulic Simulation Approach

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essay on water resources management

Hybrid Approach for Streamflow Prediction: LASSO-Hampel Filter Integration with Support Vector Machines, Artificial Neural Networks, and Autoregressive Distributed Lag Models

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essay on water resources management

Navigating Reservoir Deposition Challenges: Evaluation of Reservoir Desilting Strategy Through a 4-Stage Life Cycle Assessment Approach

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essay on water resources management

Integrated Sustainability Index for Assessing the Performance of Water Distribution Network

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Impact of Climate Change on Regional Water Availability and Demand for Agricultural Production: Application of Water Footprint Concept

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essay on water resources management

Spatiotemporal Assessment Model for Manual Operation Systems' Technical Performance in Surface Water Distribution Under Water Scarcity Scenarios

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essay on water resources management

Predicting the Water Inflow Into the Dam Reservoir Using the Hybrid Intelligent GP-ANN- NSGA-II Method

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essay on water resources management

Groundwater Resource Assessment by Applying Long-Term Trend Analysis of Spring Discharge, Water Level, and Hydroclimatic Parameters

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  • Takahiro Hosono
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essay on water resources management

Forecasting Future Groundwater Recharge from Rainfall Under Different Climate Change Scenarios Using Comparative Analysis of Deep Learning and Ensemble Learning Techniques

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  • Sayantan Ganguly
  • Shashwat Kushwaha

essay on water resources management

Assessing Water Management Strategies in Data-Scarce Mountain Regions under Uncertain Climate and Socio-Economic Changes

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essay on water resources management

Numerical Investigation of Confluence Flow in a Degraded Bed under Different Hydraulic Parameters, Using SSIIM 2.0

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essay on water resources management

Modeling Predictors of Water Conservation-Friendly Behavior Among the General Public: Structural Equation Modeling

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Improving Evapotranspiration Estimation in SWAT-Based Hydrologic Simulation through Data Assimilation in the SEBAL Algorithm

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essay on water resources management

Improving Water Efficiencies in Rural Agriculture for Sustainability of Water Resources: A Review

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  • B. B. Vashisht
  • Gurjeet Singh

essay on water resources management

Assessment of Climate Change-Induced Water Scarcity Risk by Using a Coupled System Dynamics and Bayesian Network Modeling Approaches

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  • Alireza Massah Bavani

essay on water resources management

The Potential of Stormwater Management Strategies and Artificial Intelligence Modeling Tools to Improve Water Quality: A Review

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essay on water resources management

Investigating the Economic Impacts of Inter-Basin Water Transfer Projects with a Water- Embedded Multi - Regional Computable General Equilibrium Approach

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  • Babolla Hayati

essay on water resources management

Simultaneous Minimization of Water Age and Pressure in Water Distribution Systems by Pressure Reducing Valves

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Nonlinear Segmental Runoff Ensemble Prediction Model Using BMA

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essay on water resources management

Comparison of Hybrid LSTAR-GARCH Model with Conventional Stochastic and Artificial-Intelligence Models to Estimate Monthly Streamflow

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  • Farshad Fathian
  • Survey D. Sharma

essay on water resources management

Modeling the Role of Novel Ecosystems in Runoff and Soil Protection: Native and Non-native Subtropical Montane Forests

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  • Ezequiel ArĂĄoz

essay on water resources management

A Flood Season Division Model Considering Uncertainty and New Information Priority

essay on water resources management

Use of Artificial Intelligence Modelling for the Dynamic Simulation of Urban Catchment Runoff

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  • Tanveer Choudhury

essay on water resources management

Strategic Placement of In-line Turbines for Optimum Power Generation and Leakage Reduction in Water Supply Networks

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  • Ruchi Khare

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Analysis of Flow and Ambient Sound Data to Identify the Microcomponents of Domestic Water Consumption for Large Households

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  • Enda O’Connell

essay on water resources management

Enhancing Equitable Water Distribution in Agriculture: A Novel Optimal Framework for Irrigation Equity Index Improvement Under Diverse Adaptation Strategies

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  • Song Xueqian
  • Majid Amani-Beni

essay on water resources management

Uncertain Benefits of Using Remotely Sensed Evapotranspiration for Streamflow Estimation—Insights From a Randomized, Large-Sample Experiment

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  • Tam V. Nguyen

essay on water resources management

Multifractal Description of the Agricultural and Meteorological Drought Propagation Process

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  • Zhilan Wang

essay on water resources management

On the Evolution and Determinants of Water Efficiency in the Regions of Spain

  • Asensio BuendĂ­a HernĂĄndez
  • Francisco Javier AndrĂ©
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essay on water resources management

Developing a National-Scale Hybrid System Dynamics, Agent-Based, Model to Evaluate the Effects of Dietary Changes on the Water, Food, and Energy Nexus

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  • Omid Bozorg-Haddad
  • Hugo A. LoĂĄiciga

essay on water resources management

Study on the Influence of Temporal and Spatial Resolution of Rainfall Data on Watershed Flood Simulation Performance

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  • Qingyuan Guo

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Enhancing Water Cycle Restoration through LID Practices Considering Climate Change: A Study on Permeable Pavement Planning by an Iterative MCDM Model

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essay on water resources management

Correlation Between Water Erosion and Hydraulics of Slope–Gully Systems According to Check Dam Siltation Depth

essay on water resources management

Prioritization of Sub-Watersheds Susceptible to Soil Erosion using Different Combinations of Objective Weighting and MCDM Techniques in an Ungauged River Basin

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essay on water resources management

A Multi-step Data Assimilation Framework to Investigate the Effect of Measurement Uncertainty in the Reduction of Water Distribution Network Model Errors

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  • Mario Castro-Gama
  • Leonardo Alfonso

essay on water resources management

A Qualitative-Risk-Based Model to Assess Group Decisions for Planning the Maintenance-Renewal Works of Water Pipelines with Unreliable Operational Data

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essay on water resources management

Reservoir Risk Operation of 'Domestic-Production-Ecology' Water Supply Based on Runoff Forecast Uncertainty

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essay on water resources management

Effective Hydraulic Head Control Rule Identification for Unrecoverable Subsidence Mitigation

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Incorporating Spatio-Temporal Changes of Well Irrigation into a Distributed Hydrologic Model to Improve Groundwater Anomaly Estimations for Basins with Expanding Agricultural Lands

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essay on water resources management

Application of Machine Learning Approaches in Particle Tracking Model to Estimate Sediment Transport in Natural Streams

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  • Habib Ahmari

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Investigating the Impacts of Seasonal Temperature Variations on the Hysteresis Response of Groundwater in the Aquitard in a Plain Reservoir area

  • Chaoqi Wang

essay on water resources management

A Novel Coupled Model for Monthly Rainfall Prediction Based on ESMD-EWT-SVD-LSTM

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essay on water resources management

Analyzing the Role of Changing Climate on the Variability of Intensity-Duration-Frequency Curve Using Wavelet Analysis

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  • Hamza Farooq Gabriel
  • Khalil Ur Rahman

essay on water resources management

Enhancing Flood Susceptibility Modeling: a Hybrid Deep Neural Network with Statistical Learning Algorithms for Predicting Flood Prone Areas

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  • Masumeh Ahmadipari

essay on water resources management

Relevance of Intuitionistic Fuzzy Optimization Approach in Planning of a Multi–Objective Water Resource System

  • Sangita Pawar
  • Premlal Patel
  • Ashwini B. Mirajkar

essay on water resources management

D-vine Copula Quantile Regression for a Multidimensional Water Expenditures Analysis: Social and Regional Impacts

  • El Hannoun Wafaa
  • Zoglat Abdelhak
  • El Adlouni Salah-Eddine

essay on water resources management

Generalized Structure of Group Method of Data Handling: Novel Technique for Flash Flood Forecasting

  • Isa Ebtehaj
  • Hossein Bonakdari

essay on water resources management

Regional Water Environmental Carrying Capacity: Changing Trends and Direction, Obstacle Factors, and Implications

essay on water resources management

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    1 Introduction. Integrated Water Resources Management (IWRM) is a concept that is meant to foster effective water resource management. GWP [] defined it as "the process which promotes the coordinated development and management of water, land and related resources, to maximise the resultant economic and social welfare equitably without compromising the sustainability of vital systems".

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