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A pretreatment process for brackish water and brine desalination -

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dc.contributor.author Korban, Lea Georges
dc.date.accessioned 2017-08-30T14:12:24Z
dc.date.available 2017-08-30T14:12:24Z
dc.date.issued 2015
dc.date.submitted 2015
dc.identifier.other b1838240x
dc.identifier.uri http://hdl.handle.net/10938/10781
dc.description Thesis. M.S.E.S. American University of Beirut. Interfaculty Graduate Environmental Sciences Program, (Environmental Technology), 2015. ET:6319
dc.description Advisor : Dr. George Ayoub, Professor, Civil and Environmental Engineering ; Members of Committee : Dr. Makram Suidan, Professor, Civil and Environmental Engineering ; Dr. Mahmoud Al-Hindi, Assistant Professor, Chemical Engineering ; Dr. Majdi Abou Najm, Assistant Professor, Civil and Environmental Engineering.
dc.description Includes bibliographical references (leaves 103-112)
dc.description.abstract In response to the increasing demand for fresh water worldwide, water reuse and desalination have been successfully employed as alternative methods of freshwater supply over the last few decades (Elimelech and Phillip, 2011). Specifically, reverse osmosis (RO) has gained significant appeal as one of the major processes for desalination, representing up to 80percent of the total number of installed desalination plants globally (Greenlee et al., 2009; Valavala et al., 2011). Due to technological enhancements and reduction in cost requirements, RO is viewed as an energy-efficient process, especially for the desalination of brackish water (Lauer, 2006; Elimelech and Phillip, 2011). Nonetheless, the RO process has several limitations, the most hindering of which is membrane fouling due to particulate and colloidal matter, inorganic compounds, organic substances, and biological growth (Prihasto et al., 2009; Valavala et al., 2011). Not only does membrane fouling reduce the efficiency and lifetime of the RO membrane, but it also incurs additional costs to operate the system due to increased energy demand and frequent cleaning (Bodzek et al., 2011; Valavala et al., 2011). To prevent such drawbacks to the process, conventional as well as non-conventional pretreatment methods have been used, namely coagulation- flocculation, sedimentation, granular media filtration, dissolved air flotation, ultrafiltration, microfiltration, and nanofiltration (Prihasto et al., 2009; Valavala et al., 2011). Within this context, precipitation softening is a conventional pretreatment process that contributes to the removal of a number of scale-producing and fouling pollutants, such as magnesium, calcium, silica, and strontium. The proposed research aims at assessing the effectiveness of precipitation softening as a pretreatment process for brackish water reverse osmosis. This was achieved by selecting the optimal softening chemicals and dosages, followed by examining the removal efficiency of a number of scaling and fouling contaminants under differen
dc.format.extent 1 online resource (xvii, 119 leaves) : color illustrations ; 30cm
dc.language.iso eng
dc.relation.ispartof Theses, Dissertations, and Projects
dc.subject.classification ET:006319
dc.subject.lcsh Saline water conversion.
dc.subject.lcsh Water -- Purification.
dc.subject.lcsh Seawater -- Analysis.
dc.subject.lcsh Reverse osmosis.
dc.subject.lcsh Multidisciplinary design optimization.
dc.title A pretreatment process for brackish water and brine desalination -
dc.type Thesis
dc.contributor.department Interfaculty Graduate Environmental Sciences Program (Environmental Technology)
dc.contributor.faculty Maroun Semaan Faculty of Engineering and Architecture
dc.contributor.institution American University of Beirut


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