Comparison of Membrane-Based Treatment Methods for the Removal of Micro-Pollutants from Reclaimed Water
Abstract
:1. Introduction
2. Materials and Methods
2.1. Materials
2.1.1. Feed Water
2.1.2. Membranes
- a.
- Flat sheet membrane module: A flat sheet MF membrane module made up of polyvinylidene fluoride (PVDF) with a nominal pore size of 0.14 μm and surface area 0.2 m2 was used for the MF-GAC hybrid system. It had 8 vertical membrane sheets with 11 mm gap between any two adjacent membrane sheets. The dimensions of this membrane are: 11.5 cm (width), 10.5 cm (length), and 22.5 cm (height). It was manufactured by the A3 Membrane Company, Gelsenkirchen, Germany.
- b.
- Nanofiltration (NF): Two hydrophilic NF membranes, NP030 and NTR729HF, were used to assess the performance of NF in removing micro-pollutants. The NP030 (manufactured by Macrodyn®Nadir) was made of polyethersulfone with a molecular weight cutoff (MWCO) 400 Da and Zeta potential of −15 mV at pH 7 [28]. The NTR 729HF, manufactured by Nittto Denko, was made of Polyvinylalcoho/polyamides (Heterocyclic aromatic) with a MWCO 700 Da, and the Zeta potential was −100 mV [29].
- c.
- Reverse Osmosis (RO) membranes: RO membrane (manufactured by Woongjin Chemical) made of polyamides, with MWCO of 100 Da and zeta potential −21 mV [30] was used to investigate the RO removal performance of micro-pollutants from the feed water.
2.1.3. Granular-Activated Carbon (GAC)
2.2. Methodology
2.2.1. MF-GAC Hybrid System
2.2.2. Nanofiltration
2.2.3. Reverse Osmosis
2.2.4. Analysis of Micro-Pollutants
2.2.5. Estimation of Micro-Pollutants in the Reclaimed Water
2.2.6. Removal Efficiency (%) of Micro-Pollutants
3. Results
3.1. Micro-Pollutants in the Microfiltered BTSE
3.2. Removal of Micro-Pollutants by MF
3.3. Removal of Micro-Pollutants by MF-GAC Hybrid System
3.4. Removal of Micro-Pollutants by NF
3.5. Removal of Micro-Pollutants by RO
4. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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Micro-Pollutants | Class of Micro-Pollutants | Log Kow (pH 7) | Molecular Weight (MW) (g/mol) | Precursor Ion (m/z) | Charge of Molecule | Electrospray Ionization (ESI) Mode | LOQ (ng/L) | Actual Conc (ng/L) in MF/BTSE | Estimated Conc. (ng/L) in Reclaimed Water (Max Limit) |
---|---|---|---|---|---|---|---|---|---|
Positive (+); Neutral (0); Negative (−) | Blending Proportion | ||||||||
CMF:RO (Mixing Ratio 80:20–50:50) | |||||||||
Ketoprofen | Analgesics | 3.12 | 254 | 252.80 | − | − | 5 | 95.2 | 47.5–76 |
Naproxen | Analgesics | 3.18 | 230 | 228.90 | − | − | 5 | 69–313 | 156–250 |
Ibuprofen | Analgesics | 3.97 | 206 | 204.90 | − | − | 5 | 38–70 | 35–56 |
Gemfibrozil | Lipid regulator | 4.77 | 250 | 248.90 | − | − | 5 | 24–430 | 215–344 |
Diclofenac | Analgesic | 4.51 | 296 | 293.90 | − | − | 5 | 8–200 | 100–160 |
Triclosan | Anti-microbial agent | 5.34 | 290 | 286.60 | 0 | − | 5 | 6–90 | 45–72 |
Triclocarban | Anti-microbial agent | 4.90 | 316 | 312.90 | 0 | − | 10 | 12–38 | 19–30 |
Atenolol | Beta blocker | 0.16 | 266 | 267.20 | + | + | 5 | 78–186 | 93–148 |
Sulfamethoxazole | Therapeutic | 0.89 | 253 | 254.00 | − | + | 5 | 84–114 | 57–91 |
Caffeine | Stimulant | −0.07 | 194 | 195.00 | 0 | + | 10 | 86–675 | 337–540 |
Trimethoprim | Anti-infective | 0.91 | 290 | 291.10 | +/0 | + | 5 | 26–229 | 114–183 |
TCEP Tris(2-chloroethyl) phosphate) | Flame retardant | 1.44 | 250 | 284.90 | + | 10 | 29–99 | 49–79 | |
Carbamazepine | Anti-analgesics | 2.45 | 236 | 237.00 | 0 | + | 5 | 231–541 | 270–432 |
Fluoxetine | Anti-depressant | 4.10 | 309 | 310.00 | + | + | 5 | 8–24.7 | 12–20 |
Amitriptyline | Anti-depressant | 4.92 | 277 | 278.20 | + | + | 5 | 5–37 | 18–27 |
Primidone | Therapeutic | 0.91 | 218 | 219.20 | − | + | 5 | 8–117 | 58–94 |
Verapamil | Therapeutic | 3.79 | 454 | 455.40 | + | + | 5 | 8–28 | 14–22 |
Simazine | Herbicide | 2.18 | 201 | 202.00 | 0 | + | 5 | 7–11 | 5–9 |
Diazinon | Insecticide | 3.81 | 304 | 305.10 | + | 5 | 10–104 | 52–83 | |
Diuron | Herbicide | 2.68 | 233 | 233.02 | 0 | 5 | 35.7–42.8 | 21–34 |
Micro-Pollutants | Influent (MF Feed) (ng/L) | MF Effluent (ng/L) | Removal (%) |
---|---|---|---|
Amtriptyline | 19 | 13 | 30 |
Atenolol | 104 | 84 | 19 |
Caffeine | 73 | 68 | 6 |
Carbamazepine | 393 | 369 | 6 |
Diclofenac | 164 | 152 | 7 |
Fluoxetine | 19 | 9 | 53 |
Gemfibrozil | 334 | 298 | 11 |
Ketoprofen | 114 | 95 | 17 |
Naproxen | 820 | 522 | 36 |
Primidone | 29 | 26 | 12 |
Sulfamethoxazole | 61 | 61 | 0 |
Triclocarban | 81 | 41 | 50 |
Triclosan | 91 | 5 | 95 |
Trimethoprim | 236 | 208 | 12 |
Verapamil | 35 | 27 | 23 |
Micro-Pollutants | Influent Feed Water (ng/L) | Effluent MF-GAC Hybrid System (ng/L) | Removal (%) by MF-GAC |
---|---|---|---|
Naproxen | 211 | 19 | 90.9 |
Ibuprofen | 70 | 5 | 92.8 |
Gemfibrozil | 430 | 16 | 96.3 |
Triclosan | 90 | 5 | 94.4 |
Diclofenac | 131 | 18 | 86.6 |
Triclocarban | 38 | 10 | 73.7 |
Atenolol | 220 | 7 | 96.6 |
Sulfamethoxazole | 114 | 30 | 73.7 |
Caffeine | 675 | 151 | 77.6 |
Trimethoprim | 229 | 7 | 97.0 |
TCEP | 56 | 10 | 82.1 |
Carbamazepine | 434 | 36 | 91.8 |
Fluoxetine | 20 | 5 | 74.6 |
Amtriptyline | 37 | 5 | 86.5 |
Primidone | 11 | 5 | 54.4 |
Verapamil | 28 | 5 | 82.2 |
NP030 | NTR729 HF | |||||
---|---|---|---|---|---|---|
Micro-Pollutants | Influent (ng/L) | Effluent (ng/L) | Removal (%) | Influent (ng/L) | Effluent (ng/L) | Removal (%) |
Atenolol | 220 | 76 | 65.4 | 83 | 20 | 75.5 |
Sulfamethoxazole | 114 | 80 | 29.5 | 174 | <5 | 97.1 |
Caffeine | 675 | 631 | 6.5 | 88 | 57 | 34.9 |
Trimethoprim | 229 | 146 | 36.2 | 146 | 31 | 78.7 |
Carbamazepine | 434 | 344 | 20.7 | 376 | 50 | 86.7 |
Amtriptyline | 37 | 9 | 76.8 | 11 | <5 | 55.4 |
Primidone | 11 | <10 | >10 | 26 | <5 | 80.9 |
Verapamil | 28 | 8 | 71.3 | 12 | <5 | 57.3 |
Diazinon | 104 | 6 | 94.2 | 98 | <5 | 94.9 |
Naproxen | 211 | 47 | 77.7 | 84 | <5 | 94.0 |
Gemfibrozil | 430 | 122 | 71.6 | 31 | 9 | 72.2 |
Diclofenac | 131 | 71 | 46.0 | 57 | <5 | 91.2 |
Triclocarban | 38 | <10 | 73.7 | 10 | <9 | >10 |
Diuron | 43 | 25 | 41.8 | 94 | 49 | 47.9 |
Fluoxetine | 20 | 11 | 44.7 | ND | - | - |
Ibuprofen | 70 | 17 | 76.3 | ND | - | - |
Triclosan | 90 | 25 | 72.5 | ND | - | - |
Micro-Pollutants | Influent (RO Feed) (ng/L) | Effluent (RO Permeate) (ng/L) | Removal (%) |
---|---|---|---|
Caffeine | 675 | 21.1 | 97 |
Carbamazepine | 434 | 11 | 97 |
Gemfibrozil | 430 | <5 | >99 |
Trimethoprim | 229 | <5 | >98 |
Atenolol | 220 | 5.11 | 98 |
Naproxen | 211 | <5 | >98 |
Diclofenac | 131 | <5 | >96 |
Sulfamethoxazole | 114 | <5 | >96 |
Triclosan | 90 | 7.04 | 92 |
Ibuprofen | 70 | <5 | >93 |
Triclocarban | 38 | <10 | 74 |
Amtriptyline | 37 | <5 | >86 |
Verapamil | 28 | <5 | >82 |
Fluoxetine | 20 | <5 | >75 |
Primidone | 11 | <5 | >53 |
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Devaisy, S.; Kandasamy, J.; Nguyen, T.V.; Johir, M.A.H.; Ratnaweera, H.; Vigneswaran, S. Comparison of Membrane-Based Treatment Methods for the Removal of Micro-Pollutants from Reclaimed Water. Water 2022, 14, 3708. https://doi.org/10.3390/w14223708
Devaisy S, Kandasamy J, Nguyen TV, Johir MAH, Ratnaweera H, Vigneswaran S. Comparison of Membrane-Based Treatment Methods for the Removal of Micro-Pollutants from Reclaimed Water. Water. 2022; 14(22):3708. https://doi.org/10.3390/w14223708
Chicago/Turabian StyleDevaisy, Sukanyah, Jaya Kandasamy, Tien Vinh Nguyen, Md Abu Hasan Johir, Harsha Ratnaweera, and Saravanamuthu Vigneswaran. 2022. "Comparison of Membrane-Based Treatment Methods for the Removal of Micro-Pollutants from Reclaimed Water" Water 14, no. 22: 3708. https://doi.org/10.3390/w14223708
APA StyleDevaisy, S., Kandasamy, J., Nguyen, T. V., Johir, M. A. H., Ratnaweera, H., & Vigneswaran, S. (2022). Comparison of Membrane-Based Treatment Methods for the Removal of Micro-Pollutants from Reclaimed Water. Water, 14(22), 3708. https://doi.org/10.3390/w14223708