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Thursday, February 21, 2019

Fresh Water Essay

1. IntroductionFresh weewee is an indispensable re line of descent for humans livelihood, agricultural irrigation and economic development (Brooks, 2007). However, collectible to the rapid macrocosm ingathering and the limited reserves, increasing regions check faced skillful scarcity of re fairful wet (Williamson, 2010). Saudi-Arabian-Arabian Arabia is champion of the driest countries in the world (CIA, 2011). According to sphere Bank (2011), the world average fresh peeing consumption is near 7000m/year/person, while the pissing resource per capita in Saudi Arabia is slight than 1200m/year/person. In order to satisfy the demand for peeing, Saudi Arabia presently supplies fresh peeing via deep drilling of fossil ground pissing (UNESCO, 2009).Nevertheless, society more and more recognises that those water supply resources are non-renewable and are liable to be reduced by the overexploited boreholes and wells. Thus Saudi Arabia needs to find alternative and sustai nable methods to settle these issues. Since there is abundant sea water around Saudi Arabia, large desalinization could be the ideal solution to water scarcity. However, the expensive greet and the detrimental influence on the environment might limit the outstrip and sustainability of this method. Due to the cheap appeal and the minor environmental damage, wastewater employ is regarded as another potential solution. However, it seems to have a low brotherly sufferance.Therefore, this report will compare the feasibility of desalinization and water re cultivate in terms of cost, social acceptance and environmental impacts, thereby exploring the most suitable method to deal with the scarcity of water in Saudi Arabia.2. BackgroundSaudi Arabia is located in the Middle East, bordering the Persian disjuncture and the Red Sea (CIA, 2011). It is famous for the abundant reserves of oil color and gas. However, the fresh water resources in Saudi Arabia are very limited. According to piece Bank (2011), there is no one river and lake with perennial water throughout this country. Furthermore, due to the influence of the subtropical climate, the annual precipitation is only rough 100 mm and the climate is hot and dry (ibid.). Additionally, rapid population growth has caused higher increase of demand for water (Abderrahman, 2000). Shortages of water have constrained the development of agriculture and economy (Williamson, 2010).Since the underground water is estimated to be able to hand over for 320 years, the underground water is still the principal source of water at present (UNESCO, 2009 100). However, with the increasing awareness of defects of this method, the focus of the prospective development of water provide has shifted to other sustainable water technologies. In order to deal with fresh water shortages, desalinization has received long investments. According to Abu-Arabi (2007), in 2004 the number of desalinisation industries r each(prenominal) ed 30 and they can supply 1.1 million cubic metres of fresh water per year. sewer water reuse is regarded as another future means of water provision. According to Bashitialshaaer et al (2009), in 2009 there were 33 wastewater treatment plants with a capacity of 748 billion cubic metres per year.3. RequirementsCost should be the principal consideration of water provision because an expensive cost might limit the scale of application of methods. This to a fault includes the cost of nothing consumption.Social acceptance plays a significant economic consumption in the development of water supply technologies. If the water cannot be received by society, it will lead to very little consumption.Environment has a profound influence on human beings. In order to disallow water supply technology undermining the environment, its impacts on the environment should be considered.4. origination of options4.1 DesalinationDesalination is a particular treatment process to bump off minerals fr om saline water to purify for drinking water and irrigation (Al-Sahlawi, 1999). Sometimes this process is used to take salinity and other pollutants from wastewater. The general method of desalinization is reverse osmosis or multi-stage flash distillation (Lone hint Chapter of the Sierra Club, 2008).4.2 pee Reuse urine reuse means treating wastewater to a specific quality, and then using treated or reclaimed water from one application for another application (McKenzie, 2005 Asano, 2006). The resources for wastewater reuse are sundry(a) according to Asano (2006), they could be domestic wastewater, industrial sewage, municipal sewage or agricultural wastewater.5. Comparison of Options5.1 CostAlthough the cost of desalination has decreased dramatically in the past three decades, it is still expensive to use in large scale. Alghariani (2003) points out that the expenditure of desalination consists of initial investment for equipment, runway costs (including staff and primary(preno minal)tenance), as well as chemicals or specialize parts. At present, according to the Third man urine Assessment insure (UNESCO, 2009 155), the average cost of desalination is between $0.60/m and $0.80/m. Moreover, Owens and Brunsdale (2000, cited in Alghariani, 2003 5) claim that the cost of desalination in Florida can even be less than $0.55/m, which is one-tenth of the cost price in 1979.However, as Wright (2009) points out, this cost is still higher than other water supply technologies. apart(predicate) from expenditure, desalination is generally considered a high-cost process due to the enormous energy consumption (Abu-Arabi, 2007). Nevertheless, this does not seem to be a problem for Saudi Arabia. According to the CIA (2010), the proven oil and gas reserves in Saudi Arabia are respectively the first and fifth in the world. As Abu-Arabi (2007) points out, in Saudi Arabia the annual solar energy received by each square kilometre of land is equivalent to 1.5 million barrels of approximative oil. Abundant energy may lead to a low price.Nevertheless, oil is non-renewable and oil reserves are estimated to last less than one century (World Energy Council, 2010), so the consumption of energy should be taken into storey as a considerable cost. Moreover, the treatment of the waste gas come coverd by desalination also increases the cost (Al-Sahlawi, 1999).The cost of water reuse is influenced by various factors such(prenominal) as treatment level, intended reuse options, repair of treatment, wastewater collection and transportation. According to Qadir et al (2009), the average cost of cycle water is approximately $1.79 per cubic metre. However, compared to desalination, wastewater reuse has the advantage of cost. fryer (2010) demonstrates that the relative marginal cost of seawater desalination is higher than water recycling, and amounts to up to $2000 per acre-foot. The water recycling represented a general mutant pattern between approximately $300 an d $1000 per acre-foot ( frier, 2010). until now so, water recycling appears cheaper than desalination.5.2 Social acceptanceWhile both options can generate safe water, desalination seems to have higher social acceptance. Sloane (2009) investigated the acceptance of desalination and water reuse at Nourieh Palms. As shown in Table 2, in all areas but particularly drinking water, the approval rate for desalination is higher than water reuse. This reflects that more batch trust the quality of water which is generated by desalination.Source Sloane (2009 128)For most uses, reclaimed water tends to have set about social acceptance than desalination. There are various reasons why people do not trust reclaimed water. First, most people do not understand the difference between treated and untreated water (McKenzie, 2005). Secondly, they are often concerned about the type of wastewater, treatment levels and the accessibility of instruction (Qadir, 2009). There are particular concerns with the wastewater produced by the oil color industry, brought to the surface when drilling oil.This kind of wastewater is difficult to treat due to the high content of oil (Asatekin and Mayes, 2009). Therefore, though reclaimed water undergoes a very thorough treatment process which makes it entirely safe to drink, the globe are reluctant to drink treated sewage. However, it is not impossible that people will accept drinking such treated sewage. For example, Singapore has successfully used reclaimed water, a product named NEWater, to supply drinking water (Tortajada, 2006). This reflects that treated wastewater could become widely accepted through commonplace education.5.3 Influence on environmentThere are some environmental disadvantages of desalination. Since Saudi Arabia is rich in oil and gas, clean energy such as solar energy tends to be used less than fossil energy (Al-Sahlawi, 1999). The overuse of fossil energy may cause unplayful environmental taint. For instance, oil mig ht generate large quantities of carbon dioxide, which is the main factor leading to global warming (Al-Aza, 2005). Furthermore, the gas emissions from oil could debauch the ozone layer and cause acid rain (ibid.). In addition to environmental pollution caused by fossil energy, brine discharge is another serious problem. After desalination, the brines generally have a higher tightness of salt, nearly twice that of natural seawater (Tsiourtis, 2002). The brines are generally discharged back to the same place where the seawater comes from. This might lead to increased concentration of salt in the sea, which is a potential threat to aquatics.In wrinkle with the desalination, wastewater reuse is regarded as an eco-friendly way to supply fresh water. recycle water can maximise the use of rainfall and other menstruation water resources so that the limited underground water resources can be conserved (Miller, 2005). In the meantime, decreased energy consumption could reduce the pollution caused by the use of fossil energy (Ghermandi et al, 2007). Therefore, recycled water is a sustainable and eco-friendly method to supply good quality fresh water.6. ConclusionFrom the information given above, the following conclusions can be drawn1) Both desalination and wastewater reuse are feasible water supply technologies.2) The cost of desalination has decreased dramatically, but is still far more than water reuse. Desalination requires more capital and energy.3) Reclaimed water has low common acceptance, especially for drinking water.4) Desalination could undermine the environment, while water reuse is eco-friendly.7. RecommendationConsidering the cost and the impact on the environment, wastewater reuse is recommended to be used as the main water supply technology. Although the public acceptance of recycled water is lower than desalination, the example of Singapore has proven that reclaimed water could be accepted in daily life. Desalination is a expensive water supply tech nology. Furthermore, it needs a vast amount of energy. Even if Saudi Arabia has abundant oil and gas reserves, as these resources are non-renewable, desalination is not suitable for sustainable water supply. Additionally, it has detrimental influences upon the environment. Therefore, Saudi Arabia should purify the ratio of wastewater reuse in the whole fresh water supply system.8. ReferencesAbderrahman, W. (2000). Urban Water Management in Developing desiccated Countries. Water Resources nurture 16 (1) pp7-20.Abu-Arabi, M. (2007). Status and Prospects for Solar Desalination in the Mena Region. In Rizzuti, L., Ettouney, H., and Cipollina, A. (eds.) Solar Desalination for the 21st Century A come off of Modern Technologies and Researches on Desalination Coupled to Renewable Energies (pp163-178). Dordrecht Springer.Al-Aza, M. (2005). anoint pollution and Its Environmental Impact in the Arabian Gulf Region. Boston Elsevier.Alghariani, S. (2003). Water Transfer Versus Desalination in North Africa Sustainability and Cost Comparison. capital of the United Kingdom instruct of Oriental and African Studies.Al-Sahlawi, M. (1999). Seawater Desalination in Saudi Arabia scotch Review and Demand Projections. Desalination (123) pp143-147.Asano, T. (2006). Water Reuse Issues, Technologies and Applications. New York McGraw Hill.Asatekin, A. And Mayes, A. (2009). Oil Industry Wastewater Treatment with Fouling Resistant Membranes Containing Amphiphilic Comb Copolymers. Evrion. Sci. Technol. 43 (12) pp. 4487-4492.Bashitialshaaer, R., Persson, K., and Larsson, M. (2009). Estimated incoming Production of Desalinated Seawater in the MENA Countries and Consequences for the Recipients. Dubai IDA World Congress.Brooks, D. (2007). Fresh Water in the Middle East and North Africa. In Lipchin, C., Pallant, E., Saranga, D. And Amster, A. (eds.) Water Resources Management and earnest in the Middle East (pp. 33-64). Dordrecht Springer.CIA (2011). Saudi Arabia. Retrieved 5 April 2011 fr om https//www.cia.gov/library/publications/the-world-factbook/geos/sa.htmlFryer J. (2010). An Investigation of the Marginal Cost of Seawater Desalination in California. Retrieved 5 April 2011 from http//r4rd.org/wp-content/uploads/2009/07/Cost_of_Seawater_Desalination__Final_3-18-09.pdfGhermandi, A., Bixio, D. And Thoeye, C. (2007). The Role of Free Water Constructed Wetlands As Polishing Step in Municipal Wastewater Reclamation and Reuse. Science of the Total Environment. 380 (1-3) pp. 247-258.Lone Star Chapter of the Sierra Club (2008). Desalination Is It Worth the Salt?. Retrieved 5 April 2011 from http//texas.sierraclub.org/ tender/Desalination.pdfMcKenzie, C. (2005). Wastewater Reuse Conserves Water and Protects Waterways. On Tap winter 44 (4) pp46-51.Miller, G. (2005). Integrated Concepts in Water Reuse Managing spherical WaterNeeds. Desalination 187 (1-3) pp. 65-75.Tsiourtis, N. (2002). Desalination and the Environment. Desalination. 141 (3) pp. 223-236.UNESCO (2009). The Un ited Nations World Water Development Report, 3 Water in a Changing World. Paris and London Earthscan.Qadir, M., Bahri, A., Sato, T., and Al-Karadsheh, E. (2009). Wastewater Production, Treatment and Irrigation in the Middle East and North Africa. Biomedical and demeanor Science 24 (1-2) pp37-51.Sloane, T. (2009). Water Provision A Comparative Analysis. London Sage.Tortajada, C. (2006). Water Management in Singapore. International Journal of Water Resources Development (22) pp. 227-240.Williamson, F. (2010). Water Management Traditional and Alternative Approaches. International Resource Management. 15(2) pp. 227-231.World Bank (2011). Saudi Arabia. Retrieved 5 April 2011 from http//data.worldbank.org/country/saudi-arabiaWorld Energy Council (2010). Issues. Retrieved 5 April 2011 from http//worldenergy.org/IssuesWright, G. (2009). The Economic Feasibility of Desalination for Water Supply to Arid Regions. Global Water Issues 13 (2) pp202-206.

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