2022
DOI: 10.1016/j.desal.2021.115489
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Magnesium recovery from desalination reject brine as pretreatment for membraneless electrolysis

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Cited by 27 publications
(5 citation statements)
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“…When brine from RO plants was tested as a source of industrial water in the copper mining industry, the removal of and reduction in the calcium and magnesium ion concentration were also required to improve the copper recovery in the flotation process [19]. Magnesium and calcium removal in sequence was also studied in the pretreatment of desalination brine before subjecting it to electrolysis [20,21]. In the concentration of SWRO brines by electrodialysis, a calcium removal of 94-96% as carbonate with simultaneous magnesium removal higher than 60% at 60 • C was obtained by Casas et al [22].…”
Section: Introductionmentioning
confidence: 99%
“…When brine from RO plants was tested as a source of industrial water in the copper mining industry, the removal of and reduction in the calcium and magnesium ion concentration were also required to improve the copper recovery in the flotation process [19]. Magnesium and calcium removal in sequence was also studied in the pretreatment of desalination brine before subjecting it to electrolysis [20,21]. In the concentration of SWRO brines by electrodialysis, a calcium removal of 94-96% as carbonate with simultaneous magnesium removal higher than 60% at 60 • C was obtained by Casas et al [22].…”
Section: Introductionmentioning
confidence: 99%
“…During electrolysis of brine, the base (OH – ) is generated at the porous flow-through cathode by the reduction of H 2 O through the hydrogen evolution reaction (HER, eq ), while the oxygen evolution reaction (OER, eq ) and/or chlorine evolution reaction (CER, eq ) occurs at the counter electrode. Since the current study is focused on porous cathodes for the HER, brine solutions comprised of Na 2 SO 4 with similar ionic conductivity as reject brine were used to avoid complications associated with undesirable CER at the counter electrode. , normalc athode ( HER ) : 0.25em 4 normalH 2 O + 4 e 2 H 2 + 4 OH goodbreak0em1em⁣ E ° = 0.00 V 0.25em vs 0.25em RHE normala node ( OER ) : 2 normalH 2 O 4 H + + O 2 + 4 e goodbreak0em1em⁣ E ° = 1.23 0.25em normalV 0.25em vs 0.25em RHE or: normala node ( CER ) : 0.25em 2 Cl Cl 2 + 2 e goodbreak0em1em⁣ ...…”
Section: Introductionmentioning
confidence: 99%
“…Desalination offers an approach to address freshwater shortages, with some countries in arid regions of the world relying on desalinated water to meet water demands for more than half of their water needs. , However, conventional desalination technologies present major environmental concerns due to the cogeneration of concentrated reject brine streams that contain various organic compounds, metals, and other contaminants. Electrochemical treatment of brine through electrolysis or electrodialysis creates an opportunity to generate hydrogen (H 2 ) fuel, sodium hydroxide (NaOH), and hydrochloric acid (HCl) and convert environmentally unfriendly reject brine into value-added products while simultaneously reducing the salinity of the brine.…”
Section: Introductionmentioning
confidence: 99%
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“…Benefited by the advantages of the high purity of separated gas, ion exchange membrane electrolysis [ 11 , 12 ] is now the most common used technology in the brine electrolysis process, even though its electrolytic efficiency depends largely on the performance of the ion membrane. Since there are all kinds of ions with various concentrations in saline wastewater, the pores of the ion membrane might be blocked, resulting in higher tank voltage and lower electrolysis efficiency [ 13 , 14 ]. Therefore, it is necessary to explore the suitable concentrations of impurity ions during saline wastewater electrolysis to ensure a stable and economic electrolytic performance with minimal damage to the ion membrane.…”
Section: Introductionmentioning
confidence: 99%