D.A. Vermaas
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25 records found
1
Zero-gap alkaline water electrolysis (AWE) is a promising route to affordable green hydrogen at industrially relevant current density, with commercially available square woven stainless steel meshes as electrodes. Improving how the architectures of these mesh electrodes—that is, the geometry of the woven wires, their surface properties, and the arrangement of one or more mesh layers—manage bubbles and ionic transport is essential to making zero-gap AWE economically viable. However, performance differences between architectures are governed by interlinked activation, ohmic, and bubble-induced transport losses, which existing studies rarely separate, particularly for square woven meshes. This thesis presents an experimental study of square woven stainless steel (AISI 304) mesh electrodes in a custom zero-gap AWE cell with four integrated reference electrodes, enabling the decoupling of activation, ohmic, and bubble-induced transport losses. Five single-layer meshes with varying mesh numbers (38 mesh, 60 mesh, 100 mesh, 150 mesh and 200 mesh), two of them also with a hydrophilic coating, and four multilayer configurations, including identical stacks, a fine-to-coarse gradient (150-60-38), and its reverse, were tested in 30 wt% KOH at room temperature and up to 1 A cm⁻². The single-layer measurements show that the cell voltage decreases with mesh fineness up to an optimum at the 150 mesh (Ecell ≈ 2.86 V at 0.8 A cm⁻²), reflecting the balance between higher reactive area on finer meshes and bubble trapping inside the finer structure. A fitted transport resistance, Rtr, scales linearly with the pore-width-to-wire-diameter ratio wa/dw, attributed to gas shielding at the diaphragm-facing electrode surface. A hydrophilic coating lowered the cell voltage by 50 and 70 mV on the 150-mesh and 200-mesh electrodes, respectively, acting mainly on the activation term, but coating durability during operation could not be independently verified and the benefit is reported as indicative rather than systematic. Identical stacking raised the cell voltage despite the additional surface area, as the extra layers obstructed gas escape and roughly doubled the diaphragm drop. The fine-to-coarse gradient stack was the best-performing configuration of the study (Ecell ≈ 2.70 V at 0.8 A cm⁻²), reducing both activation and transport terms simultaneously. Inverting the layer order raised the cell voltage by about 150 mV at 0.8 A cm⁻² while keeping total surface area, material, and intrinsic kinetics unchanged, showing that this improvement is architectural and driven by layer ordering. Together, these findings identify bubble management at the diaphragm-facing electrode surface through deliberate mesh architecture as the key to improving zero-gap AWE performance. Increasing the reactive surface area near the diaphragm while reducing gas-film formation and promoting gas escape through mesh geometry and layer ordering reduces bubble-induced transport losses. ...
Zero-gap alkaline water electrolysis (AWE) is a promising route to affordable green hydrogen at industrially relevant current density, with commercially available square woven stainless steel meshes as electrodes. Improving how the architectures of these mesh electrodes—that is, the geometry of the woven wires, their surface properties, and the arrangement of one or more mesh layers—manage bubbles and ionic transport is essential to making zero-gap AWE economically viable. However, performance differences between architectures are governed by interlinked activation, ohmic, and bubble-induced transport losses, which existing studies rarely separate, particularly for square woven meshes.
This thesis presents an experimental study of square woven stainless steel (AISI 304) mesh electrodes in a custom zero-gap AWE cell with four integrated reference electrodes, enabling the decoupling of activation, ohmic, and bubble-induced transport losses. Five single-layer meshes with varying mesh numbers (38 mesh, 60 mesh, 100 mesh, 150 mesh and 200 mesh), two of them also with a hydrophilic coating, and four multilayer configurations, including identical stacks, a fine-to-coarse gradient (150-60-38), and its reverse, were tested in 30 wt% KOH at room temperature and up to 1 A cm⁻².
The single-layer measurements show that the cell voltage decreases with mesh fineness up to an optimum at the 150 mesh (Ecell ≈ 2.86 V at 0.8 A cm⁻²), reflecting the balance between higher reactive area on finer meshes and bubble trapping inside the finer structure. A fitted transport resistance, Rtr, scales linearly with the pore-width-to-wire-diameter ratio wa/dw, attributed to gas shielding at the diaphragm-facing electrode surface. A hydrophilic coating lowered the cell voltage by 50 and 70 mV on the 150-mesh and 200-mesh electrodes, respectively, acting mainly on the activation term, but coating durability during operation could not be independently verified and the benefit is reported as indicative rather than systematic.
Identical stacking raised the cell voltage despite the additional surface area, as the extra layers obstructed gas escape and roughly doubled the diaphragm drop. The fine-to-coarse gradient stack was the best-performing configuration of the study (Ecell ≈ 2.70 V at 0.8 A cm⁻²), reducing both activation and transport terms simultaneously. Inverting the layer order raised the cell voltage by about 150 mV at 0.8 A cm⁻² while keeping total surface area, material, and intrinsic kinetics unchanged, showing that this improvement is architectural and driven by layer ordering.
Together, these findings identify bubble management at the diaphragm-facing electrode surface through deliberate mesh architecture as the key to improving zero-gap AWE performance. Increasing the reactive surface area near the diaphragm while reducing gas-film formation and promoting gas escape through mesh geometry and layer ordering reduces bubble-induced transport losses.
Mass transfer in Direct Air Capture sorbents
Modeling adsorption and desorption of carbon dioxide and water in typical solid sorbents
This thesis addresses the challenges in modeling adsorption and desorption processes in solid-sorbent Direct Air Capture, focusing on the complexities introduced by the porous structures of sorbent materials and the effects of humidity. Current models fail to incorporate the full spectrum of mass transfer processes, or do not consider the significant effects of humidity on the process. To bridge this gap, a detailed mass transfer and reaction kinetics model at the particle scale was developed, aiming to provide a more accurate framework for predicting the performance of amine-functionalized sorbents in DAC applications. The model was developed on a particle scale, and subsequently included in contactor models of a packed-bed and a monolith. The study considered all relevant transport mechanisms, finding that pore diffusion and reaction kinetics are critical in governing sorbent uptake dynamics. The contactor model effectively compares the performance of packed-bed and monolith reactors, highlighting a tradeoff between productivity and energy efficiency, with significant potentials for energy savings offered by the monolith. ...
This thesis addresses the challenges in modeling adsorption and desorption processes in solid-sorbent Direct Air Capture, focusing on the complexities introduced by the porous structures of sorbent materials and the effects of humidity. Current models fail to incorporate the full spectrum of mass transfer processes, or do not consider the significant effects of humidity on the process. To bridge this gap, a detailed mass transfer and reaction kinetics model at the particle scale was developed, aiming to provide a more accurate framework for predicting the performance of amine-functionalized sorbents in DAC applications. The model was developed on a particle scale, and subsequently included in contactor models of a packed-bed and a monolith. The study considered all relevant transport mechanisms, finding that pore diffusion and reaction kinetics are critical in governing sorbent uptake dynamics. The contactor model effectively compares the performance of packed-bed and monolith reactors, highlighting a tradeoff between productivity and energy efficiency, with significant potentials for energy savings offered by the monolith.
Exploring electrochemical disinfection for decentralized drinking water production
From Laboratory Research to Field Application in Ghana
disinfection for the treatment of surface water. Laboratory experiments were conducted to evaluate the performance of an RuO2/IrO2 and a Magneli-phase reactor for the disinfection of a bacteria species, Escherichia Coli, and a virus species, ΦX174. The two reactors are characterised in terms of distinct anodic properties and their performance is assessed by promoting different electrochemical reactions for the generation of various disinfectant agents within the electrochemical cell, with specific focus on the formation of chlorine and Reactive
Oxygen Species (ROS). Chlorine-based disinfection proved to be the primary agent in the removal of both pathogens; a 4 log removal for E. Coli was achieved at an energy use of 0.41 kWh/m3 for RuO2/IrO2 and of 0.31 kWh/m3 forMagneli, and a 5 log removal for ΦX174 was achieved at 2.88 kWh/m3 for RuO2/IrO2 and for 1.18 kWh/m3 for Magneli.
To further assess the viability for the treatment of surface waters in decentralized settings, the RuO2/IrO2 was also tested in a field setting in Ghana making use of different water types to compare the utility in using an electrochemical reactor to produce chlorine for disinfection as compared to traditional disinfection methods. Seawater, lagoon and river water were tested, achieving an energy use per gram of produced chlorine of 0.007, 0.046 and 0.066 kWh/gchlorine for a produced chlorine dose of 35 mg/L for seawater and 5 mg/L for the lagoon and river water. With these results, chlorine can be produced from river water at an equivalent dosage to traditional chlorine tablets, and at a cost that is 40 times lower. ...
disinfection for the treatment of surface water. Laboratory experiments were conducted to evaluate the performance of an RuO2/IrO2 and a Magneli-phase reactor for the disinfection of a bacteria species, Escherichia Coli, and a virus species, ΦX174. The two reactors are characterised in terms of distinct anodic properties and their performance is assessed by promoting different electrochemical reactions for the generation of various disinfectant agents within the electrochemical cell, with specific focus on the formation of chlorine and Reactive
Oxygen Species (ROS). Chlorine-based disinfection proved to be the primary agent in the removal of both pathogens; a 4 log removal for E. Coli was achieved at an energy use of 0.41 kWh/m3 for RuO2/IrO2 and of 0.31 kWh/m3 forMagneli, and a 5 log removal for ΦX174 was achieved at 2.88 kWh/m3 for RuO2/IrO2 and for 1.18 kWh/m3 for Magneli.
To further assess the viability for the treatment of surface waters in decentralized settings, the RuO2/IrO2 was also tested in a field setting in Ghana making use of different water types to compare the utility in using an electrochemical reactor to produce chlorine for disinfection as compared to traditional disinfection methods. Seawater, lagoon and river water were tested, achieving an energy use per gram of produced chlorine of 0.007, 0.046 and 0.066 kWh/gchlorine for a produced chlorine dose of 35 mg/L for seawater and 5 mg/L for the lagoon and river water. With these results, chlorine can be produced from river water at an equivalent dosage to traditional chlorine tablets, and at a cost that is 40 times lower.
Anion Exchange Membrane optimization
Applying AC electric field to create "Ion highways"
The low ion conductivity of the Anion Exchange Membrane (AEM) is found to be one of the major limitations of AEMWE. In this thesis, the AEM is aligned while casting using an alternating current electric field to improve the ion conductivity of AEMs. The stability of the electrically aligned membrane is tested using various characterisation techniques. The electrically aligned membranes showed a 300% increase in ion conductivity, with a slight decrease in mechanical stability. ...
The low ion conductivity of the Anion Exchange Membrane (AEM) is found to be one of the major limitations of AEMWE. In this thesis, the AEM is aligned while casting using an alternating current electric field to improve the ion conductivity of AEMs. The stability of the electrically aligned membrane is tested using various characterisation techniques. The electrically aligned membranes showed a 300% increase in ion conductivity, with a slight decrease in mechanical stability.
The objective of this thesis is to explore ways to improve the selectivity of carbon monoxide (CO) in a bicarbonate electrolyser. In this experimental study, focus is also placed on the stability of the process, characterising the selectivity over time. Causes of selectivity decline are examined as well as methods of improvement. Furthermore, the effect of pH on CO selectivity and stability is given special consideration. Literature in the field of (bi)carbonate electrolysis was reviewed to gather understanding on the process, to clarify recent advances made and to find areas for improvement. Based on the findings from the literature review the experimental study was designed.
Experiments were conducted in a membrane electrode assembly (MEA) flow-cell in constant current fashion, applying a current of 100 mA/cm2. The membrane chosen was a bipolar membrane (BPM) as it offers the possibility of operating with distinct electrolyte environments, separating the 3M bicarbonate catholyte from the 1M potassium hydroxide anolyte. Gas diffusion electrodes (GDE) were prepared by spray-coating silver nanoparticles on the surface, using Nafion ionomer as binding material. An interdigitated catholyte flow plate was used which ensured the bicarbonate would pass through the GDE due to its discontinuous channels forcing the flow through.
By introducing a catalyst-membrane gap through inserting a hydrophilic porous spacer between the GDE and the BPM, CO selectivity was improved from 50% to 78% in peak production, recording 55%
averaged over 3 hour operation. This enhancement in selectivity can be explained by the defined pH gradient resulting from the gap, permitting a low pH at the BPM for protons to react with the bicarbonate, liberating i-CO2; and a higher pH at the catalyst for CO2 conversion to CO while suppressing the hydrogen evolution reaction (HER). An optimum gap was found to be 135 - 270 μm. These results compare with the previously highest reported CO selectivity values from the literature at ambient conditions and 100 mA/cm2. While improving the selectivity, the stability of CO was not improved by the catalyst-membrane gap. The pH was found to affect both the selectivity and stability of CO, with higher bicarbonate pH leading to reduced selectivity but improved stability. This behaviour is explained by the reduced i-CO2 liberation and increased carbonation reactions taking place at higher pH levels…
...
The objective of this thesis is to explore ways to improve the selectivity of carbon monoxide (CO) in a bicarbonate electrolyser. In this experimental study, focus is also placed on the stability of the process, characterising the selectivity over time. Causes of selectivity decline are examined as well as methods of improvement. Furthermore, the effect of pH on CO selectivity and stability is given special consideration. Literature in the field of (bi)carbonate electrolysis was reviewed to gather understanding on the process, to clarify recent advances made and to find areas for improvement. Based on the findings from the literature review the experimental study was designed.
Experiments were conducted in a membrane electrode assembly (MEA) flow-cell in constant current fashion, applying a current of 100 mA/cm2. The membrane chosen was a bipolar membrane (BPM) as it offers the possibility of operating with distinct electrolyte environments, separating the 3M bicarbonate catholyte from the 1M potassium hydroxide anolyte. Gas diffusion electrodes (GDE) were prepared by spray-coating silver nanoparticles on the surface, using Nafion ionomer as binding material. An interdigitated catholyte flow plate was used which ensured the bicarbonate would pass through the GDE due to its discontinuous channels forcing the flow through.
By introducing a catalyst-membrane gap through inserting a hydrophilic porous spacer between the GDE and the BPM, CO selectivity was improved from 50% to 78% in peak production, recording 55%
averaged over 3 hour operation. This enhancement in selectivity can be explained by the defined pH gradient resulting from the gap, permitting a low pH at the BPM for protons to react with the bicarbonate, liberating i-CO2; and a higher pH at the catalyst for CO2 conversion to CO while suppressing the hydrogen evolution reaction (HER). An optimum gap was found to be 135 - 270 μm. These results compare with the previously highest reported CO selectivity values from the literature at ambient conditions and 100 mA/cm2. While improving the selectivity, the stability of CO was not improved by the catalyst-membrane gap. The pH was found to affect both the selectivity and stability of CO, with higher bicarbonate pH leading to reduced selectivity but improved stability. This behaviour is explained by the reduced i-CO2 liberation and increased carbonation reactions taking place at higher pH levels…
However, our findings reveal that the assembled cell performs poorly, mostly because of significant overpotentials brought on by increasing resistance, along with other drawbacks including salt formation and exceeding the legal gas crossover limit. Some of these issues regarding performance are still poorly understood and therefore need further investigation. ...
However, our findings reveal that the assembled cell performs poorly, mostly because of significant overpotentials brought on by increasing resistance, along with other drawbacks including salt formation and exceeding the legal gas crossover limit. Some of these issues regarding performance are still poorly understood and therefore need further investigation.
This study focused on optimizing BPMED for the recovery of ammonia and citric acid from ammonium citrate scrubber effluents. The impact of current density, membrane configuration, feed solution characteristics (pH and initial N concentration), and temperature on recovery efficiency, current efficiency, and energy consumption of a BPMED system was evaluated. The limiting current density (LCD), a key factor in the normal operating range of the system, was determined using the Cowan and Brown method, yielding a critical value of 1.01 A/m2.
Comparative experiments conducted on three BPMED configurations, including 3-chamber BPMED (BPCA), 2-chamber base BPMED (BPC), and 2-chamber acid BPMED (BPA), revealed the superior performance of the BPC in terms of current efficiency, energy consumption, and running time. The optimal operating time of BPC was determined to be 120 minutes, achieving a recovery efficiency of 55.9%, a current efficiency of 44.2%, and an energy consumption of 8.4 kWh/kg-N.
Moreover, regression models were established using Box-Behnken design (BBD) from response surface methodology (RSM) to optimize operating conditions (pH, initial N concentration, and temperature), maximize recovery efficiency, current efficiency, and minimize energy consumption. Verified by analysis of variance, normal probability plot, and residual analysis, the model showed high accuracy and significance.
Univariate analysis elucidated that pH and initial N concentration were found to be important variables, while temperature was not. Increasing pH (3–7) enhanced recovery and current efficiency while decreasing energy consumption. Higher initial N concentrations (2–10 g/L) improved current efficiency, decreased energy consumption, but reduced recovery efficiency, emphasizing the need for a careful balance. Temperature variations (20–40°C) had no significant impact on BPMED. Critical factors limiting ammonia recovery efficiency, current efficiency, and energy consumption were identified, including solution conductivity, H+ ion leakage, water migration, and NH3 diffusion.
Furthermore, the study revealed non-significant interactions between these variables through 3D response surface plots and 2D contour plots. Adjusting operational variables proved feasible for optimizing performance indicators. The optimized conditions (pH 6.05, initial N concentration 6.67 g/L, temperature 30°C) were experimentally verified, and the predicted values were in good agreement with the actual values, confirming the reliability of the optimization model. Specifically, the recovery efficiency was 52.9%, the current efficiency was 45.4%, and the energy consumption was 7.0 kWh/kg-N.
Energy evaluation of the BPMED system in BPC configuration under optimal conditions showed significant energy efficiency. Based on the comparison with the available literature, the integration of BPMED with air stripping and organic acid scrubbing could improve energy efficiencies and lower chemical consumption while offering a closed-loop system.
Future research should explore principles to inhibit ion leakage and water migration, analyze the combined effects of various operating variables using RSM, and validate the potential for lower energy consumption in full-scale BPMED. Developing continuous BPMED processes is crucial for full-scale application, and integrating BPMED with other processes such as air stripping and acid scrubbing may enhance ammonia recovery and production efficiency.
The insights gleaned from this study provided a solid foundation for enhancing ammonia recovery processes from ammonium citrate scrubber wastewater, thereby promoting sustainable and resource-saving industrial practices.
...
This study focused on optimizing BPMED for the recovery of ammonia and citric acid from ammonium citrate scrubber effluents. The impact of current density, membrane configuration, feed solution characteristics (pH and initial N concentration), and temperature on recovery efficiency, current efficiency, and energy consumption of a BPMED system was evaluated. The limiting current density (LCD), a key factor in the normal operating range of the system, was determined using the Cowan and Brown method, yielding a critical value of 1.01 A/m2.
Comparative experiments conducted on three BPMED configurations, including 3-chamber BPMED (BPCA), 2-chamber base BPMED (BPC), and 2-chamber acid BPMED (BPA), revealed the superior performance of the BPC in terms of current efficiency, energy consumption, and running time. The optimal operating time of BPC was determined to be 120 minutes, achieving a recovery efficiency of 55.9%, a current efficiency of 44.2%, and an energy consumption of 8.4 kWh/kg-N.
Moreover, regression models were established using Box-Behnken design (BBD) from response surface methodology (RSM) to optimize operating conditions (pH, initial N concentration, and temperature), maximize recovery efficiency, current efficiency, and minimize energy consumption. Verified by analysis of variance, normal probability plot, and residual analysis, the model showed high accuracy and significance.
Univariate analysis elucidated that pH and initial N concentration were found to be important variables, while temperature was not. Increasing pH (3–7) enhanced recovery and current efficiency while decreasing energy consumption. Higher initial N concentrations (2–10 g/L) improved current efficiency, decreased energy consumption, but reduced recovery efficiency, emphasizing the need for a careful balance. Temperature variations (20–40°C) had no significant impact on BPMED. Critical factors limiting ammonia recovery efficiency, current efficiency, and energy consumption were identified, including solution conductivity, H+ ion leakage, water migration, and NH3 diffusion.
Furthermore, the study revealed non-significant interactions between these variables through 3D response surface plots and 2D contour plots. Adjusting operational variables proved feasible for optimizing performance indicators. The optimized conditions (pH 6.05, initial N concentration 6.67 g/L, temperature 30°C) were experimentally verified, and the predicted values were in good agreement with the actual values, confirming the reliability of the optimization model. Specifically, the recovery efficiency was 52.9%, the current efficiency was 45.4%, and the energy consumption was 7.0 kWh/kg-N.
Energy evaluation of the BPMED system in BPC configuration under optimal conditions showed significant energy efficiency. Based on the comparison with the available literature, the integration of BPMED with air stripping and organic acid scrubbing could improve energy efficiencies and lower chemical consumption while offering a closed-loop system.
Future research should explore principles to inhibit ion leakage and water migration, analyze the combined effects of various operating variables using RSM, and validate the potential for lower energy consumption in full-scale BPMED. Developing continuous BPMED processes is crucial for full-scale application, and integrating BPMED with other processes such as air stripping and acid scrubbing may enhance ammonia recovery and production efficiency.
The insights gleaned from this study provided a solid foundation for enhancing ammonia recovery processes from ammonium citrate scrubber wastewater, thereby promoting sustainable and resource-saving industrial practices.
Recycling steam condensate for hydrogen production
Producing hydrogen through alkaline water electrolysis using electrolyte that contains ammonia
When steam condensate is used instead of ultra-pure water, it is important to find out what happens to the added ammonia and if it affects the production rate and the production efficiency, or if it degrades the equipment. The experiments in this report used three different ammonia concentrations and the electrolyte was made using potassium hydroxide. The electrolysis cell used nickel mesh electrodes and a Selemion™ anion exchange membrane. Each of the experiments were carried out at 2.15 Volts for a duration of 50 minutes.
It was found that adding 1 mmol/L ammonia to the electrolyte decreased the current density of the cell. Doubling the ammonia concentration led to an even larger decrease in current density of up to 19%. A significant effect on the Faraday efficiency was not measured. During the experiments, the ammonia was partially stripped from the electrolyte due to its high alkalinity. Another part was oxidised to produce nitrogen gas and nitrate. Some of the ammonia had not reacted after the 50-minute experiment and could be measured in the spent electrolyte. After all the experiments were carried out, the cell was disassembled. The cathode showed significant signs of degradation. However, the many starts and stops between experiments could be the primary reason for this degradation. The ammonia could have accelerated the degradation, but this was not proven.
Overall, the benefits of using steam condensate do not seem to outweigh the drawbacks. The ammonia caused a significant decrease in current density. On the long term, ammonia might cause electrode poisoning which would further lower the current density. The experiments also found nitrate in the spent electrolyte. Having additional pollutants in both the spent electrolyte and the produced gasses might introduce additional disadvantages to using an ammonia containing electrolyte. If steam condensate is used as a water source, a treatment step is advised. Aeration could be used to strip the ammonia from the electrolyte. To get a more accurate insight into the effects of ammonia on alkaline water electrolysis, additional research is necessary. In future research, the effects of ammonia should be measured more accurately, and the long-term effects should be researched.
...
When steam condensate is used instead of ultra-pure water, it is important to find out what happens to the added ammonia and if it affects the production rate and the production efficiency, or if it degrades the equipment. The experiments in this report used three different ammonia concentrations and the electrolyte was made using potassium hydroxide. The electrolysis cell used nickel mesh electrodes and a Selemion™ anion exchange membrane. Each of the experiments were carried out at 2.15 Volts for a duration of 50 minutes.
It was found that adding 1 mmol/L ammonia to the electrolyte decreased the current density of the cell. Doubling the ammonia concentration led to an even larger decrease in current density of up to 19%. A significant effect on the Faraday efficiency was not measured. During the experiments, the ammonia was partially stripped from the electrolyte due to its high alkalinity. Another part was oxidised to produce nitrogen gas and nitrate. Some of the ammonia had not reacted after the 50-minute experiment and could be measured in the spent electrolyte. After all the experiments were carried out, the cell was disassembled. The cathode showed significant signs of degradation. However, the many starts and stops between experiments could be the primary reason for this degradation. The ammonia could have accelerated the degradation, but this was not proven.
Overall, the benefits of using steam condensate do not seem to outweigh the drawbacks. The ammonia caused a significant decrease in current density. On the long term, ammonia might cause electrode poisoning which would further lower the current density. The experiments also found nitrate in the spent electrolyte. Having additional pollutants in both the spent electrolyte and the produced gasses might introduce additional disadvantages to using an ammonia containing electrolyte. If steam condensate is used as a water source, a treatment step is advised. Aeration could be used to strip the ammonia from the electrolyte. To get a more accurate insight into the effects of ammonia on alkaline water electrolysis, additional research is necessary. In future research, the effects of ammonia should be measured more accurately, and the long-term effects should be researched.
To address these limitations, a novel approach has gained traction within the research community: the paired electrolysis of CO2 reduction reaction (CO2RR) and glycerol oxidation reaction (GOR). How- ever, these studies mostly employ expensive platinum group metal (PGM) catalysts in flow cells, failing to address cost dependency or scalability for future industrial applications due to inefficient energy use in this electrolyzer configuration. Therefore, this study intends to understand and optimize the paired electrolysis of CO2RR with GOR in zero-gap electrolyzers while comparing the performances of Pt (a relatively rare PGM catalyst) and Ni (an abundant non-PGM catalyst). The effects of applied cell po- tential, glycerol concentration, active surface area, and ion exchange membrane type on GOR product selectivity and the system’s energy demand are evaluated through potential and current controlled ex- periments. Gas chromatography (GC) and proton nuclear magnetic resonance spectroscopy (H-NMR) are used for product analysis.
This thesis demonstrates the viability of paired electrolysis in zero-gap electrolyzers, yielding major products like formate and lactate alongside minor byproducts such as acetate, glycerate, and dihydrox- yacetone. The results reveal Ni’s superior performance over Pt at current densities below 200 mA/cm2 in zero-gap electrolyzers. The negative influence of increasing applied potentials on faradaic efficien- cies (FEs) is presented, particularly in Ni, likely due to side reactions like OER or formate oxidation. The study also illustrates that increased glycerol concentrations decrease FEs and system activities due to heightened viscosity-related diffusivity issues. Moreover, the tests conducted using the Ni anode in zero-gap electrolyzers utilizing bipolar membranes (BPM) show a minor reduction in product selectivity likely caused by the increased amounts of OH– ions near the anode coming from the water dissociation reaction (WDR).
The study also uncovers that the anticipated significant reduction in the cell’s energy demand with the replacement of OER with GOR is not observed in zero-gap electrolyzers. No conclusive improve- ments are observed for either catalyst when anion exchange membranes (AEM) are employed, and only marginal improvements in the cell’s energy demand are achieved when bipolar membranes are used with Ni. Although this behavior is speculated to be a consequence of the absence of a flowing electrolyte near the anode, further investigations are needed to identify the cause of this unexpected lack of improvement in the energy demand. ...
To address these limitations, a novel approach has gained traction within the research community: the paired electrolysis of CO2 reduction reaction (CO2RR) and glycerol oxidation reaction (GOR). How- ever, these studies mostly employ expensive platinum group metal (PGM) catalysts in flow cells, failing to address cost dependency or scalability for future industrial applications due to inefficient energy use in this electrolyzer configuration. Therefore, this study intends to understand and optimize the paired electrolysis of CO2RR with GOR in zero-gap electrolyzers while comparing the performances of Pt (a relatively rare PGM catalyst) and Ni (an abundant non-PGM catalyst). The effects of applied cell po- tential, glycerol concentration, active surface area, and ion exchange membrane type on GOR product selectivity and the system’s energy demand are evaluated through potential and current controlled ex- periments. Gas chromatography (GC) and proton nuclear magnetic resonance spectroscopy (H-NMR) are used for product analysis.
This thesis demonstrates the viability of paired electrolysis in zero-gap electrolyzers, yielding major products like formate and lactate alongside minor byproducts such as acetate, glycerate, and dihydrox- yacetone. The results reveal Ni’s superior performance over Pt at current densities below 200 mA/cm2 in zero-gap electrolyzers. The negative influence of increasing applied potentials on faradaic efficien- cies (FEs) is presented, particularly in Ni, likely due to side reactions like OER or formate oxidation. The study also illustrates that increased glycerol concentrations decrease FEs and system activities due to heightened viscosity-related diffusivity issues. Moreover, the tests conducted using the Ni anode in zero-gap electrolyzers utilizing bipolar membranes (BPM) show a minor reduction in product selectivity likely caused by the increased amounts of OH– ions near the anode coming from the water dissociation reaction (WDR).
The study also uncovers that the anticipated significant reduction in the cell’s energy demand with the replacement of OER with GOR is not observed in zero-gap electrolyzers. No conclusive improve- ments are observed for either catalyst when anion exchange membranes (AEM) are employed, and only marginal improvements in the cell’s energy demand are achieved when bipolar membranes are used with Ni. Although this behavior is speculated to be a consequence of the absence of a flowing electrolyte near the anode, further investigations are needed to identify the cause of this unexpected lack of improvement in the energy demand.
The process waters are C5C6 and C5 sugar streams and the main ions present are sodium and sulphate. A desalting target of 60% is set for these two ions and the experiments are done using a lab-scale electrodialysis set-up. Tests are run to check the desalting rate, effect of filtration, powdered activated carbon (PAC) and acidification, persistence of fouling and the effect of cleaning-in-place. The increase in average resistance and run time is used as an indicator of membrane fouling.
The raw C5C6 sugar solution could not reach the desalting target but once the solution is filtered, a desalting of 75.5% (Na+) and 66.5% (SO42-) is achieved. The average resistance also drops significantly. The fouling is removed by a CIP and is deemed to be ‘reversible’ in nature. On the other hand, the C5 sugar solution did not improve in performance after filtration. Although the desalting target could be achieved after filtration, the average resistance rose to 130 ohms. A CIP did not have any effect and increased run-time and drop in desalting efficiency was observed. The main reason for fouling in both cases is attributed to the presence of lignin degradation compounds. Lignin is more concentrated in the C5 sugar as compared to the C5C6 sugar solution due to its production process. In C5 sugar, the irreversible fouling pattern is hypothesized to be due to adsorption whereas in case of C5C6 sugar the reversible fouling pattern is cake fouling. PAC was dosed to remove the organic foulants in C5 sugar and improved the average resistance to 48 ohms and significantly reduced the run time. Desalting of 61.4% (Na+) and 87.2% (SO42-) was reached. Acidification protonated the feed and reduced the charged interactions, thereby both reducing run time and the average resistance. Desalting of 65.79% (Na+) and 68.02% (SO42-) was reached after acidification.
To conclude, the studied ED system could desalt the organic C5C6 and C5 sugar streams after a treatment step. Lignin degradation products were found to heavily foul the AEM membranes as its increased presence in C5 sugar stream led to a more severe fouling which could not be restored even with a chemical CIP. However, mitigation of the degradation products in the pre-treatment step could ensure that the solution was desalted by the ED unit. Thus, quantifying the composition of organic streams is imperative to predict the propensity of fouling in an ED unit.
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The process waters are C5C6 and C5 sugar streams and the main ions present are sodium and sulphate. A desalting target of 60% is set for these two ions and the experiments are done using a lab-scale electrodialysis set-up. Tests are run to check the desalting rate, effect of filtration, powdered activated carbon (PAC) and acidification, persistence of fouling and the effect of cleaning-in-place. The increase in average resistance and run time is used as an indicator of membrane fouling.
The raw C5C6 sugar solution could not reach the desalting target but once the solution is filtered, a desalting of 75.5% (Na+) and 66.5% (SO42-) is achieved. The average resistance also drops significantly. The fouling is removed by a CIP and is deemed to be ‘reversible’ in nature. On the other hand, the C5 sugar solution did not improve in performance after filtration. Although the desalting target could be achieved after filtration, the average resistance rose to 130 ohms. A CIP did not have any effect and increased run-time and drop in desalting efficiency was observed. The main reason for fouling in both cases is attributed to the presence of lignin degradation compounds. Lignin is more concentrated in the C5 sugar as compared to the C5C6 sugar solution due to its production process. In C5 sugar, the irreversible fouling pattern is hypothesized to be due to adsorption whereas in case of C5C6 sugar the reversible fouling pattern is cake fouling. PAC was dosed to remove the organic foulants in C5 sugar and improved the average resistance to 48 ohms and significantly reduced the run time. Desalting of 61.4% (Na+) and 87.2% (SO42-) was reached. Acidification protonated the feed and reduced the charged interactions, thereby both reducing run time and the average resistance. Desalting of 65.79% (Na+) and 68.02% (SO42-) was reached after acidification.
To conclude, the studied ED system could desalt the organic C5C6 and C5 sugar streams after a treatment step. Lignin degradation products were found to heavily foul the AEM membranes as its increased presence in C5 sugar stream led to a more severe fouling which could not be restored even with a chemical CIP. However, mitigation of the degradation products in the pre-treatment step could ensure that the solution was desalted by the ED unit. Thus, quantifying the composition of organic streams is imperative to predict the propensity of fouling in an ED unit.
The effect of different current densities on the ohmic and non-ohmic resistance of bipolar membranes (BPM), under forward and reverse bias were studied using electrochemical impedance spectroscopy (EIS). Hereafter, an anion exchange membrane (AEM), cation exchange membrane (CEM) and BPM were examined individually and in series using EIS, to compose a simplified equivalent circuit for a whole ABFB triplet.
For the effect of different current densities on the BPM, an exponential decline of the non-ohmic resistance of the diffusion boundary layer (DBL) was found as a function of the current density. Under forward bias, the DBL resistance becomes significant. The resistance of the water dissociation reaction (WDR) was minimal under all current densities. Flow experiments validate a depletion and enrichment of the DBL during water association and dissociation, respectively.
To compose a simplified equivalent circuit for an AEM, BPM and CEM in series, it was found that the specific resistances of all membranes can be summed at their respective frequencies. This made it possible to construct a simplified equivalent circuit for a whole triplet containing an AEM, BPM and CEM. ...
The effect of different current densities on the ohmic and non-ohmic resistance of bipolar membranes (BPM), under forward and reverse bias were studied using electrochemical impedance spectroscopy (EIS). Hereafter, an anion exchange membrane (AEM), cation exchange membrane (CEM) and BPM were examined individually and in series using EIS, to compose a simplified equivalent circuit for a whole ABFB triplet.
For the effect of different current densities on the BPM, an exponential decline of the non-ohmic resistance of the diffusion boundary layer (DBL) was found as a function of the current density. Under forward bias, the DBL resistance becomes significant. The resistance of the water dissociation reaction (WDR) was minimal under all current densities. Flow experiments validate a depletion and enrichment of the DBL during water association and dissociation, respectively.
To compose a simplified equivalent circuit for an AEM, BPM and CEM in series, it was found that the specific resistances of all membranes can be summed at their respective frequencies. This made it possible to construct a simplified equivalent circuit for a whole triplet containing an AEM, BPM and CEM.
To investigate this, first a 2D model for a coastal area of an ocean is formed. As a basis for this model the 0D model of Steele and Henderson is used to describe the predator-prey model for zooplankton and phytoplankton. Due to this model a repeating pattern in time arises, which is called a limit cycle. This predator-prey
model is expanded to a 2D model by applying convection (v) and diffusion (D) to it, representing the current and dispersion in the water. The chosen parameters and boundary conditions are inspired by the coastal area of the west coast of Portugal.
To evaluate the effect of the water temperature rising, first, the effect of diffusion and convection are studied by answering the following questions: is the convection important for the development in space and time of the plankton population in a 2D model of a coastal area of an ocean? And: is the diffusion important for the development in space and time of the plankton population in a 2D model of a coastal area of an ocean?
The diffusion is dominant in the direction perpendicular to the coast. Due to the diffusion the limit cycle of the predator-prey model is suppressed. Its range gets smaller until the plankton population is completely constant for D > 2.5 m^2/s. This critical value is included in the realistic value of D, which varies from 1 to 2000 m^2/s.
Due to convection, the limit cycle corresponding to the boundary condition occurs in the direction parallel to the coast, making every point in the domain steady state. The higher the velocity v corresponding to the convection is, the less oscillations in phytoplankton density there are in the domain, thus the larger the wavelength of the oscillation is. For v > 0.06 m/s the current is so fast that the predator-prey model has little time to develop before it reaches the right boundary, making the left boundary value more important. This critical value is included in the realistic value of v, which varies from 0.03 to 0.28 m/s.
The model experiences both diffusion and convection more or less equally when the Péclet number vH^2/DL≈1, resulting in D/v≈50 m. If this number is significantly larger than 50 m, diffusion dominates the solution. If the number is significantly smaller than 50 m, convection dominates the solution.
Now the main research question can be answered. By increasing the temperature of the water the growth rate of phytoplankton increases. Due to this increase, the timescale of the predator-prey (τpp ) decreases. The value of D and v for which the predator-prey model and diffusion and convection all influence the solution
equally depends on the timescale with the factor 1/τpp . A smaller time scale means that the predator-prey model contributes more to the model. However, this change is very small in comparison to the scale of the realistic values. In conclusion, in the formed 2D model the temperature increase of the water is not important for the development of the plankton population in space and time.
The results of this report are influenced by the assumptions and approximations made. In this study, several processes, both physical and biological, are described with constants and simplifications. Improving the models of these processes is left for further research. ...
To investigate this, first a 2D model for a coastal area of an ocean is formed. As a basis for this model the 0D model of Steele and Henderson is used to describe the predator-prey model for zooplankton and phytoplankton. Due to this model a repeating pattern in time arises, which is called a limit cycle. This predator-prey
model is expanded to a 2D model by applying convection (v) and diffusion (D) to it, representing the current and dispersion in the water. The chosen parameters and boundary conditions are inspired by the coastal area of the west coast of Portugal.
To evaluate the effect of the water temperature rising, first, the effect of diffusion and convection are studied by answering the following questions: is the convection important for the development in space and time of the plankton population in a 2D model of a coastal area of an ocean? And: is the diffusion important for the development in space and time of the plankton population in a 2D model of a coastal area of an ocean?
The diffusion is dominant in the direction perpendicular to the coast. Due to the diffusion the limit cycle of the predator-prey model is suppressed. Its range gets smaller until the plankton population is completely constant for D > 2.5 m^2/s. This critical value is included in the realistic value of D, which varies from 1 to 2000 m^2/s.
Due to convection, the limit cycle corresponding to the boundary condition occurs in the direction parallel to the coast, making every point in the domain steady state. The higher the velocity v corresponding to the convection is, the less oscillations in phytoplankton density there are in the domain, thus the larger the wavelength of the oscillation is. For v > 0.06 m/s the current is so fast that the predator-prey model has little time to develop before it reaches the right boundary, making the left boundary value more important. This critical value is included in the realistic value of v, which varies from 0.03 to 0.28 m/s.
The model experiences both diffusion and convection more or less equally when the Péclet number vH^2/DL≈1, resulting in D/v≈50 m. If this number is significantly larger than 50 m, diffusion dominates the solution. If the number is significantly smaller than 50 m, convection dominates the solution.
Now the main research question can be answered. By increasing the temperature of the water the growth rate of phytoplankton increases. Due to this increase, the timescale of the predator-prey (τpp ) decreases. The value of D and v for which the predator-prey model and diffusion and convection all influence the solution
equally depends on the timescale with the factor 1/τpp . A smaller time scale means that the predator-prey model contributes more to the model. However, this change is very small in comparison to the scale of the realistic values. In conclusion, in the formed 2D model the temperature increase of the water is not important for the development of the plankton population in space and time.
The results of this report are influenced by the assumptions and approximations made. In this study, several processes, both physical and biological, are described with constants and simplifications. Improving the models of these processes is left for further research.
This study looks into energy efficiency and treatment performance from ammonium sulphate and ammonium citrate scrubber effluents by BPM-ED technology. A three-compartment BPM-ED was used to investigate the use of salt mixture in the feed solution and factors affecting ammonium yield.
Salt mixture of ammonium sulphate and tri-ammonium citrate were used. It was found that use of a salt mixture of ammonium sulphate and tri-ammonium citrate decreased the energy consumption and increased the current efficiency for both of the salts. Use of a mixture of ammonium sulphate and tri-ammonium citrate resulted in better energy performance than either of the salts when they were used alone. Ammonium recovery performance was higher when tri-ammonium citrate concentration was higher in the initial feed solution. This was due to increase in buffer capacity and basic pH in feed solution due to OH- leakages from base compartment. Sulphate ions were favored over citrate ions in their transfer through anion exchange membranes due to higher mobility of sulphate ions. As a further investigation a BPM-ED stack with different combinations, perhaps a two-compartment stack, can be tested to get a deeper understanding to optimize the operation.
Factors affecting ammonium yield that were investigated were H+ leakages and ammonia diffusion. It was found that H+ leakages were same for ammonium sulphate and potassium sulphate feed solutions and H+ leakages were not affected by ammonia diffusion. Ammonia diffusion resulted in higher energy consumption and loss of ammonium recovery potential. Ammonia diffusion increased even with experimental time of 60 minutes. Ammonia diffusion rates also increased through experimental time of 60 minutes. Ammonium and potassium transfer rates from diluate compartment did not follow a specific trend within the first 30 minutes. Clear reasoning behind this was unknown and the results were not completely satisfactory. In current study, it was assumed that ion cross-over and back diffusion were identical for ammonium and potassium. Investigating ion cross-over and back diffusion of the ions in BPM-ED could bring a deeper understanding to the energy efficiency and treatment performance.
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This study looks into energy efficiency and treatment performance from ammonium sulphate and ammonium citrate scrubber effluents by BPM-ED technology. A three-compartment BPM-ED was used to investigate the use of salt mixture in the feed solution and factors affecting ammonium yield.
Salt mixture of ammonium sulphate and tri-ammonium citrate were used. It was found that use of a salt mixture of ammonium sulphate and tri-ammonium citrate decreased the energy consumption and increased the current efficiency for both of the salts. Use of a mixture of ammonium sulphate and tri-ammonium citrate resulted in better energy performance than either of the salts when they were used alone. Ammonium recovery performance was higher when tri-ammonium citrate concentration was higher in the initial feed solution. This was due to increase in buffer capacity and basic pH in feed solution due to OH- leakages from base compartment. Sulphate ions were favored over citrate ions in their transfer through anion exchange membranes due to higher mobility of sulphate ions. As a further investigation a BPM-ED stack with different combinations, perhaps a two-compartment stack, can be tested to get a deeper understanding to optimize the operation.
Factors affecting ammonium yield that were investigated were H+ leakages and ammonia diffusion. It was found that H+ leakages were same for ammonium sulphate and potassium sulphate feed solutions and H+ leakages were not affected by ammonia diffusion. Ammonia diffusion resulted in higher energy consumption and loss of ammonium recovery potential. Ammonia diffusion increased even with experimental time of 60 minutes. Ammonia diffusion rates also increased through experimental time of 60 minutes. Ammonium and potassium transfer rates from diluate compartment did not follow a specific trend within the first 30 minutes. Clear reasoning behind this was unknown and the results were not completely satisfactory. In current study, it was assumed that ion cross-over and back diffusion were identical for ammonium and potassium. Investigating ion cross-over and back diffusion of the ions in BPM-ED could bring a deeper understanding to the energy efficiency and treatment performance.
The performance data revealed that the energy efficiency of hydrogen production was lower for both synthetic and municipal effluent compared to alkaline water electrolysis; this was evident for both carbon fibre and Ni-foam anode. Further, the energy efficiency was also higher when the Ni-foam anode was used compared to the carbon fibre anode. For the electrolysis of municipal effluent, a maximum energy efficiency of 75 ± 2.7% was obtained for the carbon fibre electrode, whereas for the Ni-foam anode, the maximum energy efficiency obtained was 83 ± 3.0% at an applied current density of 12.55 A/m2 with 1M KOH as the electrolyte. Despite this observation, the volumetric hydrogen production rates were not significantly affected because the rates converged closely to their theoretical values; this was also evidenced by the coulombic efficiency of hydrogen evolution reaction (HER), which exceeded 90% in all the experiments.
Concerning the extent of humic acid degradation, the Ni-foam anode was able to oxidize some of the humic acid molecules during electrolysis, and a maximum COD removal of 24.6 ± 8 % was observed after electrolysis of synthetic effluent at an applied current density of 100 A/m2 with 1M KOH as the supporting electrolyte. In contrast, the carbon fibre anode was not able to do so. Instead, the humic acid molecules tended to adsorb on the surface of the carbon fibre anode, evidenced by the increase in COD and TOC after electrolysis. Similar behaviour was also observed for the carbon fibre anode when the effect of humic acid was investigated under potentiostatic conditions, whereas under galvanostatic conditions for the Ni-foam anode, oxidation of humic acid was evident. The extent of oxidation was dependent on the duration of electrolysis, i.e., humic acid concentrations of 49.8 ± 0.98 mg O2/L and 90.0 ± 0.7 mg O2/L required a duration of 6 hrs and 8 hrs to achieve a COD removal efficiency of 43.5 ± 5.0 % and 60.4 ± 4.2 %, respectively. Additionally, the possibility to integrate an electrolyzer with an aerobic treatment plant to supply high purity oxygen was investigated. The comparison was done using BioWin simulations with a standard aerobic bioreactor for a flow of 10,000 m3/day under two conditions: 1) with atmospheric O2(baseline) 2) with high purity O2(95% purity). The investigation revealed that combining a 1 MW electrolyzer with the aerobic wastewater treatment plant would provide sufficient amount of oxygen for the proper functioning of the high purity O2 plant. In addition, the flow requirement to produce the required amount of oxygen was only 0.03% of the discharged effluent (i.e., only 3.1 m3/day of the discharged 9708 m3/day).
Further, the use of high purity oxygen in the aerobic wastewater treatment plant was accompanied by energy savings of 1.2 kWh (4320 kJ) due to reduced load on the air pumps
...
The performance data revealed that the energy efficiency of hydrogen production was lower for both synthetic and municipal effluent compared to alkaline water electrolysis; this was evident for both carbon fibre and Ni-foam anode. Further, the energy efficiency was also higher when the Ni-foam anode was used compared to the carbon fibre anode. For the electrolysis of municipal effluent, a maximum energy efficiency of 75 ± 2.7% was obtained for the carbon fibre electrode, whereas for the Ni-foam anode, the maximum energy efficiency obtained was 83 ± 3.0% at an applied current density of 12.55 A/m2 with 1M KOH as the electrolyte. Despite this observation, the volumetric hydrogen production rates were not significantly affected because the rates converged closely to their theoretical values; this was also evidenced by the coulombic efficiency of hydrogen evolution reaction (HER), which exceeded 90% in all the experiments.
Concerning the extent of humic acid degradation, the Ni-foam anode was able to oxidize some of the humic acid molecules during electrolysis, and a maximum COD removal of 24.6 ± 8 % was observed after electrolysis of synthetic effluent at an applied current density of 100 A/m2 with 1M KOH as the supporting electrolyte. In contrast, the carbon fibre anode was not able to do so. Instead, the humic acid molecules tended to adsorb on the surface of the carbon fibre anode, evidenced by the increase in COD and TOC after electrolysis. Similar behaviour was also observed for the carbon fibre anode when the effect of humic acid was investigated under potentiostatic conditions, whereas under galvanostatic conditions for the Ni-foam anode, oxidation of humic acid was evident. The extent of oxidation was dependent on the duration of electrolysis, i.e., humic acid concentrations of 49.8 ± 0.98 mg O2/L and 90.0 ± 0.7 mg O2/L required a duration of 6 hrs and 8 hrs to achieve a COD removal efficiency of 43.5 ± 5.0 % and 60.4 ± 4.2 %, respectively. Additionally, the possibility to integrate an electrolyzer with an aerobic treatment plant to supply high purity oxygen was investigated. The comparison was done using BioWin simulations with a standard aerobic bioreactor for a flow of 10,000 m3/day under two conditions: 1) with atmospheric O2(baseline) 2) with high purity O2(95% purity). The investigation revealed that combining a 1 MW electrolyzer with the aerobic wastewater treatment plant would provide sufficient amount of oxygen for the proper functioning of the high purity O2 plant. In addition, the flow requirement to produce the required amount of oxygen was only 0.03% of the discharged effluent (i.e., only 3.1 m3/day of the discharged 9708 m3/day).
Further, the use of high purity oxygen in the aerobic wastewater treatment plant was accompanied by energy savings of 1.2 kWh (4320 kJ) due to reduced load on the air pumps
On top of that, a simple 2D model was developed in COMSOL Multiphysics to understand the mass transport and concentration distribution in the gas flow channel. The model was not able to simulate the complexities of the electrochemical process and represented an ideal plug flow reactor. It is understood that the incorporation of reaction kinetics and current distribution is necessary to replicate the real scenario.
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On top of that, a simple 2D model was developed in COMSOL Multiphysics to understand the mass transport and concentration distribution in the gas flow channel. The model was not able to simulate the complexities of the electrochemical process and represented an ideal plug flow reactor. It is understood that the incorporation of reaction kinetics and current distribution is necessary to replicate the real scenario.
Selective transport between monovalent and divalent ions in electrodialysis
The effect of current density and ionic species concentration
To prevent excessive discharge into the environment, these wastewaters need to be treated. Electrodialysis has been shown to be a suitable technique for the removal and recovery of NH4+ from both synthetic and real wastewaters such as digestate rejection water and industrial condensate. These wastewaters can contain varying concentrations of Mg2+, Ca2+ and CO32-. Treating these waters with ED for NH4+ recovery also causes recovery of these divalent ions. The recovery of these ions can potentially cause scaling. Scaling is undesired and needs to be prevented. The main objective of this research was to analyse what the applied current density, Mg2+/NH4+ ratio and total ion concentration had on the the selective transport between NH4+ and Mg2+. ...
To prevent excessive discharge into the environment, these wastewaters need to be treated. Electrodialysis has been shown to be a suitable technique for the removal and recovery of NH4+ from both synthetic and real wastewaters such as digestate rejection water and industrial condensate. These wastewaters can contain varying concentrations of Mg2+, Ca2+ and CO32-. Treating these waters with ED for NH4+ recovery also causes recovery of these divalent ions. The recovery of these ions can potentially cause scaling. Scaling is undesired and needs to be prevented. The main objective of this research was to analyse what the applied current density, Mg2+/NH4+ ratio and total ion concentration had on the the selective transport between NH4+ and Mg2+.