G. Qin
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6 records found
1
During the extraction of fossil fuels, a complex waste stream is produced simultaneously, also known as produced water (PW). Membrane filtration is a promising technology that can successfully enable the treatment and reuse of PW. Silicon carbide (SiC) membranes are preferred for PW treatment, due to their low (ir)reversible fouling compared to other ceramic membranes. However, full SiC membrane is expensive and thus economically less feasible. Therefore, we established a method for coating SiC on alumina (Al2O3) ultrafiltration membranes, based on low-pressure chemical vapor deposition at 860 °C. In the presented study the fouling resistance and behavior of these novel membranes, with various pore sizes and under different operating conditions, including flux and crossflow velocity, were evaluated. We also used Al2O3 membranes and SiC-coated Al2O3 membranes in constant flux mode to treat real oilfield PW with high salinity (142 mS/cm) and COD (22670 mg/L). Additionally, the fouling mechanisms in the SiC-coated and Al2O3 membranes were analyzed with the help of Focused Ion Beam-Scanning Electron Microscopy imaging. The major findings were that pore blockage served as the initial (irreversible) fouling mechanism and that the (reversible) cake layer, a mixture of organic and inorganic components, dominated the rest of the filtration cycle, where the SiC coated membrane performed better than the original alumina membrane. In addition, it was found that the application of the SiC coating, and the selection of the appropriate pore size (62 nm) and crossflow velocity (0.8 m/s) increased the fouling mitigation, potentially advancing the utilization of ultrafiltration in treating saline PW for reuse purposes.
Impact of ionic strength and surface charge on ceramic membrane fouling by oil-in-water emulsions
A quantitative analysis using DLVO and XDLVO models
Large amounts of oily wastewater, which can be defined as produced water, are generated in oilfields. Ultrafiltration (UF) serves as an effective and economical method to purify produced water. Unfortunately, membrane fouling during produced water treatment is severe. In this paper, the effects of the ionic strength (1, 20, and 100 mM) as well as different surfactants on the membrane fouling are investigated. Four surfactants, including SDS (anionic), APG (non-ionic), CTAB (cationic) and DDAPS (zwitterionic), were selected for this study. The Derjaguin-Landau-Verwey-Overbeek (DLVO) and extended DLVO (XDLVO) models were used to quantify interactions between the membrane-oil droplet and deposited oil layer-oil droplet surfaces and to compare these interactions with the fouling experiments. The (X)DLVO interaction energies of the membrane-oil droplet exhibited a strong agreement with the fouling tendencies at 1 mM salinity. The SiC-deposited (B20) membrane showed less reversible and irreversible membrane fouling than the Al2O3 (B0) membrane when filtering negatively charged O/W emulsions stabilized with SDS, APG, or DDAPS. The DLVO model predicted a higher fouling tendency at higher salinity levels during the filtration of SDS, APG, or DDAPS-stabilized O/W emulsions and a decreased fouling tendency for CTAB-stabilized emulsion with the B20 membrane. However, at higher salinity levels, the XDLVO energy barrier was affected by both the repulsive electrostatic double layer (EL) interaction and attractive Lewis acid-base (AB) interaction. By comparing both experiments and (X)DLVO modeling, this study improves the fundamental understanding of the effect of ionic strength and surfactant types on reversible and irreversible fouling of the Al2O3 and SiC-coated membranes fouling by O/W emulsions.
First of all, a novel approach is presented for effectively separating microemulsions via SiC (3C-SiC)-coated alumina (Al2O3) membranes, fabricated based on LPCVD. With the increase in deposition time, up to 25 min, the pore size of the membranes decreased from 41 nm (without deposition) to 33 nm (deposition time of 25 min). The polycrystalline 3C-SiC-coated membranes also showed an improved hydrophilicity (water contact angle of 15º) and highly negatively charged surfaces (-65 mV). Oil-in-water (O/W) microemulsions filtration experiments were carried out at a constant permeate flux (80 Lm-2h-1) for six cycles with varying deposition time, pH, surfactant types, and pore sizes. The fouling of the SiC-coated membrane was, compared to the Al2O3 membrane, effectively mitigated due to the enhanced electrostatic repulsion and hydrophilicity. Surfactant adsorption mainly occurred when the surface charge of the microemulsion and the membranes were opposite. Therefore, the surface charge of the Al2O3 membrane changed from positive to negative when soaked in negatively charged microemulsions, whereas SiC-coated membranes remained negatively charged regardless of surfactant type. The membrane fouling was alleviated when the membrane and oil droplets had the same charge.
Subsequently, the effects of the ionic strength (1, 20, and 100 mM) as well as different surfactants in O/W emulsions on the membrane fouling were studied. Four surfactants, including sodium dodecyl sulfate (SDS, anionic), alkyl polyglycoside (APG, non-ionic), cetyltrimethylammonium bromide (CTAB, cationic) and N-dodecyl-N,N-dimethyl-3-ammonio-1-propanesulfonate (DDAPS, zwitterionic), were selected for this study. The Derjaguin-Landau-Verwey-Overbeek (DLVO) and extended DLVO (XDLVO) models were used to quantify interactions between the membrane-oil droplet and deposited oil layer-oil droplet surfaces and to compare these interactions with the fouling experiments. The (X)DLVO interaction energies of the membrane-oil droplet exhibited a strong agreement with the fouling tendencies at 1 mM salinity. The SiC-deposited membrane showed less (ir)reversible membrane fouling than the Al2O3 membrane when filtering O/W emulsions stabilized with SDS, APG, or DDAPS. The DLVO model predicted a higher tendency at higher salinity levels during the filtration of SDS, APG, or DDAPS-stabilized O/W emulsions and a decreased fouling tendency for CTAB-stabilized emulsion with the SiC-deposited membrane. However, at higher salinity levels, the XDLVO energy barrier was affected by both the repulsive electrostatic double layer (EL) interaction and attractive Lewis acid-base (AB) interaction. For the Al2O3 membrane, the XDLVO model obscured EL and Lifshitz-van der Waals (LW) interactions since the AB component was dominant, confirmed by the diminished XDLVO energy barrier, whereas for the SiC-deposited membrane, the EL interaction prevailed since the energy barrier value was positive.
Then real oilfield produced water with high salinity (142 mS/cm) and COD (22670 mg/L) was successfully treated by SiC-coated Al2O3 membranes in constant flux mode. The major findings were that pore blockage served as the initial (irreversible) fouling mechanism and that the (reversible) cake layer, a mixture of organic and inorganic components, dominated the rest of the filtration cycle, where the SiC-coated membrane performed better than the original Al2O3 membrane. In addition, it was found that the application of the SiC coating, and the selection of the appropriate pore size (62 nm) and crossflow velocity (0.8 m/s) increased the fouling mitigation, potentially advancing the utilization of ultrafiltration in treating saline produced water for reuse purposes.
Finally, synthetic wastewater containing cotton, linen, polyester, and nylon fibres and real laundry wastewater were characterized and prepared for filtration experiments, which were conducted at a flux of 70 Lm-2h-1 using an Al2O3 membrane and a SiC-coated membrane. Results revealed that natural textiles, particularly cotton and linen, released higher COD loads than synthetic fibers when tested at equal mass, in the trend of, cotton>linen>polyester>nylon, which was further supported by microscopic and SEM images. Both the Al2O3 membrane and the SiC-coated membrane showed a high fiber rejection (100 %), whereas the SiC-coated membrane showed lower reversible and irreversible fouling than the Al2O3 membrane, due to highly negatively charged surface. The fouling order of the fibers were in line with the COD concentration of the synthetic laundry wastewater containing these fibers. Finally, treatment of hot real laundry wastewater by the ceramic membranes not only mitigated membrane reversible and irreversible fouling, but also enabled the simultaneous recovery and reuse of water, surfactants, and thermal energy, offering a sustainable strategy to reduce both water consumption and energy costs.
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First of all, a novel approach is presented for effectively separating microemulsions via SiC (3C-SiC)-coated alumina (Al2O3) membranes, fabricated based on LPCVD. With the increase in deposition time, up to 25 min, the pore size of the membranes decreased from 41 nm (without deposition) to 33 nm (deposition time of 25 min). The polycrystalline 3C-SiC-coated membranes also showed an improved hydrophilicity (water contact angle of 15º) and highly negatively charged surfaces (-65 mV). Oil-in-water (O/W) microemulsions filtration experiments were carried out at a constant permeate flux (80 Lm-2h-1) for six cycles with varying deposition time, pH, surfactant types, and pore sizes. The fouling of the SiC-coated membrane was, compared to the Al2O3 membrane, effectively mitigated due to the enhanced electrostatic repulsion and hydrophilicity. Surfactant adsorption mainly occurred when the surface charge of the microemulsion and the membranes were opposite. Therefore, the surface charge of the Al2O3 membrane changed from positive to negative when soaked in negatively charged microemulsions, whereas SiC-coated membranes remained negatively charged regardless of surfactant type. The membrane fouling was alleviated when the membrane and oil droplets had the same charge.
Subsequently, the effects of the ionic strength (1, 20, and 100 mM) as well as different surfactants in O/W emulsions on the membrane fouling were studied. Four surfactants, including sodium dodecyl sulfate (SDS, anionic), alkyl polyglycoside (APG, non-ionic), cetyltrimethylammonium bromide (CTAB, cationic) and N-dodecyl-N,N-dimethyl-3-ammonio-1-propanesulfonate (DDAPS, zwitterionic), were selected for this study. The Derjaguin-Landau-Verwey-Overbeek (DLVO) and extended DLVO (XDLVO) models were used to quantify interactions between the membrane-oil droplet and deposited oil layer-oil droplet surfaces and to compare these interactions with the fouling experiments. The (X)DLVO interaction energies of the membrane-oil droplet exhibited a strong agreement with the fouling tendencies at 1 mM salinity. The SiC-deposited membrane showed less (ir)reversible membrane fouling than the Al2O3 membrane when filtering O/W emulsions stabilized with SDS, APG, or DDAPS. The DLVO model predicted a higher tendency at higher salinity levels during the filtration of SDS, APG, or DDAPS-stabilized O/W emulsions and a decreased fouling tendency for CTAB-stabilized emulsion with the SiC-deposited membrane. However, at higher salinity levels, the XDLVO energy barrier was affected by both the repulsive electrostatic double layer (EL) interaction and attractive Lewis acid-base (AB) interaction. For the Al2O3 membrane, the XDLVO model obscured EL and Lifshitz-van der Waals (LW) interactions since the AB component was dominant, confirmed by the diminished XDLVO energy barrier, whereas for the SiC-deposited membrane, the EL interaction prevailed since the energy barrier value was positive.
Then real oilfield produced water with high salinity (142 mS/cm) and COD (22670 mg/L) was successfully treated by SiC-coated Al2O3 membranes in constant flux mode. The major findings were that pore blockage served as the initial (irreversible) fouling mechanism and that the (reversible) cake layer, a mixture of organic and inorganic components, dominated the rest of the filtration cycle, where the SiC-coated membrane performed better than the original Al2O3 membrane. In addition, it was found that the application of the SiC coating, and the selection of the appropriate pore size (62 nm) and crossflow velocity (0.8 m/s) increased the fouling mitigation, potentially advancing the utilization of ultrafiltration in treating saline produced water for reuse purposes.
Finally, synthetic wastewater containing cotton, linen, polyester, and nylon fibres and real laundry wastewater were characterized and prepared for filtration experiments, which were conducted at a flux of 70 Lm-2h-1 using an Al2O3 membrane and a SiC-coated membrane. Results revealed that natural textiles, particularly cotton and linen, released higher COD loads than synthetic fibers when tested at equal mass, in the trend of, cotton>linen>polyester>nylon, which was further supported by microscopic and SEM images. Both the Al2O3 membrane and the SiC-coated membrane showed a high fiber rejection (100 %), whereas the SiC-coated membrane showed lower reversible and irreversible fouling than the Al2O3 membrane, due to highly negatively charged surface. The fouling order of the fibers were in line with the COD concentration of the synthetic laundry wastewater containing these fibers. Finally, treatment of hot real laundry wastewater by the ceramic membranes not only mitigated membrane reversible and irreversible fouling, but also enabled the simultaneous recovery and reuse of water, surfactants, and thermal energy, offering a sustainable strategy to reduce both water consumption and energy costs.
Worldwide, a considerable amount of oily wastewater is generated, with oil droplets from 2 to 200 nm that are difficult to separate because of their size and colloidal stability. This study presents a novel approach for effectively separating microemulsions via cubic silicon carbide (3C-SiC)-coated alumina (Al 2O 3) membranes fabricated based on low pressure chemical vapor deposition (LPCVD). SiC was deposited at a relatively low temperature at 860 °C on 100 nm Al 2O 3 membranes using two precursors: SiH 2Cl 2 and C 2H 2. With the increase in deposition time, up to 25 min, the pore size decreased from 41 nm to 33 nm, which is a smaller pore size of a SiC membrane than previously used for oil/water separation. The polycrystalline 3C-SiC-coated membranes showed improved hydrophilicity (water contact angle of 15°) and highly negatively charged surfaces (−65 mV). Microemulsion filtration experiments were carried out at a constant permeate flux (80 Lm −2 h −1) for six cycles with varying deposition time, pH, surfactant types, and pore sizes. The fouling of the SiC-coated membrane was, compared to the Al 2O 3 membrane, effectively mitigated due to the enhanced electrostatic repulsion and hydrophilicity. Surfactant adsorption mainly occurred when the surface charge of the microemulsion and the membranes were opposite. Therefore, the surface charge of the alumina membrane changed from positive to negative when soaked in negatively charged microemulsions, whereas SiC-coated membranes remained negatively charged regardless of surfactant type. The membrane fouling was alleviated when the membrane and oil droplets had the same charge. Lastly, the 62 nm SiC-coated membrane with 20 min coating time was the best choice for the filtration of the microemulsion, because of the high rejection of the oil droplets and low fouling tendency.