POROUS SUPERABSORBENT POLYMER MATERIAL FOR MICROALGAE HARVESTING
20230149899 · 2023-05-18
Inventors
Cpc classification
B01J20/28085
PERFORMING OPERATIONS; TRANSPORTING
B01J20/28021
PERFORMING OPERATIONS; TRANSPORTING
C12N1/02
CHEMISTRY; METALLURGY
International classification
B01J20/28
PERFORMING OPERATIONS; TRANSPORTING
B01J20/26
PERFORMING OPERATIONS; TRANSPORTING
Abstract
The present disclosure relates to methods for harvesting microalgae and to porous superabsorbent polymeric materials useful in such processes.
Claims
1. A method for harvesting microalgae from a medium, the method comprising (a) adding a porous superabsorbent polymer bead to the medium; (b) allowing water in the medium to absorb into pores in the porous superabsorbent polymer beads to form hydrated beads; and (c) separating the microalgae from the hydrated beads, thereby harvesting the microalgae.
2. A method for increasing the concentration of microalgae in a medium, the method comprising (a) adding a porous superabsorbent polymer bead to the medium; (b) allowing water in the medium to absorb into pores in the porous superabsorbent polymer beads to form hydrated beads, thereby increasing the concentration of microalgae in the medium; and (c) optionally, separating the microalgae from the hydrated beads.
3. The method according to claim 1, wherein the microalgae is Chlorella vulgaris, Isochrysis sp., Pseudioisochrysis sp., Dicrateria sp., Monochrysis sp., Tetraselmis sp., Pyramimonas sp., Micromonas sp., Chroomonas sp., Cryptomonas sp., Rhodomonas sp., Chlamydomonas sp., Chlorococcum sp., Olisthodiscus sp. Carteria sp., Dunaliella sp., Spirulina sp., Haematococcus sp., Rhodella sp., Arthrospira maxima, Nannochloropsis sp., or any combination thereof.
4. The method according to claim 1, where the microalgae are dried after separation from the hydrated beads.
5. The method according to claim 1, wherein in step (b) microalgae are excluded from the pores of the bead.
6. The method according to claim 1, wherein in step (b) microalgae are concentrated in the medium.
7. The method according to claim 1, wherein the medium is a microalgal suspension.
8. The method according to claim 1, wherein the porous superabsorbent polymer comprises a copolymer.
9. The method according to claim 8, wherein the copolymer comprises monomers selected from one or more ionic monomers, one or more non-ionic monomers, or any combination thereof.
10. The method according to claim 9, wherein the ionic monomers are selected from sodium acrylate, acrylic acid, potassium acrylate, itaconic acid, sodium itaconate, potassium itaconate, and any combination thereof.
11. The method according to claim 10, wherein the non-ionic monomers comprise acrylamide.
12. The method according to claim 1, wherein the pores in the superabsorbent polymer beads are between about 0.001 and about 10 micrometers.
13. The method according to claim 1, wherein the water absorbency of the superabsorbent polymer beads is between about 10 and about 150 g g.sup.−1.
14. The method according to claim 1, wherein the superabsorbent polymer beads are made by a process comprising reacting one or more ionic monomers and/or one or more non-ionic monomers, or any combination thereof, with a porogen, optionally in the presence of a cross-linker.
15. The method according to claim 14, wherein the porogen is selected from poly(ethylene glycol), polyvinyl alcohol, or a combination thereof.
16. The method of claim 14, wherein the amount of porogen present in the monomer solution during preparation of the porous superabsorbent polymer beads is an amount between about 1 wt. % and about 10 wt. %.
17. The method according to claim 1, wherein the swelling ratio of the superabsorbent polymer beads is between about 1 g g.sup.−1 and about 500 g g.sup.−1.
18. The method according to claim 1, wherein the initial biomass density of the medium is between about 0.2 and about 70 g L.sup.−1.
19. The method according to claim 1, wherein the final biomass density of the medium is between about 0.4 and about 150 g L.sup.−1.
20. The method according to claim 1, wherein the efficiency of the process (harvesting efficiency) is greater than about 70%.
21. The method according to claim 1, wherein the method further comprises repeating steps (a) and (b) one or more times,
22. The method according to claim 21, wherein steps (a) and (b) are repeated, one, two, three, four or five times.
Description
BRIEF DESCRIPTION OF THE DRAWINGS
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DETAILED DESCRIPTION OF THE INVENTION
[0078] As used herein the following definitions shall apply unless otherwise indicated.
[0079] As used herein, the term “microalgae” refers to microscopic, unicellular algae that can exist individually or in groups.
[0080] As used herein, the term “porous superabsorbent polymer” refers to a polymer which has tunable pore structure and water-absorbing ability.
[0081] As used herein, the terms “water absorbency” and “swelling ratio” refer to the mass of the water a polymer absorbed relative to its own mass.
[0082] As used herein, the term “harvesting efficiency” refers to the efficiency of the mass of microalgae collected after harvesting process compared with its original amount.
Preparation and Characterization of PSAP Beads
[0083] Porous polymers may be prepared using conventional methods (e.g., suspension, dispersion, precipitation, and multistage polymerization) and emerging methods (e.g., membrane emulsification and microfluidic technique). See, e.g., Gokmen et al., Prog. Polymer Sci., 37, 365-405, 2012; Wu et al., Chem. Rev., 112, 3659-4015, 2012.
[0084] In the present invention, PSAP beads were fabricated with desired micrometer-sized pores via polymerization-induced phase separation. See, e.g., Chen et al., ACS Mat. Lett., 2, 1545-1554, 2020. As shown in
[0085] To obtain PSAP beads with optimal pore structure and swelling properties, precursors with different amounts of porogen (e.g., PEG) were used, including, e.g., 2.5, 5.0, and 7.5 wt. % PEG, and the PSAP beads obtained are labeled as PEG-2.5, PEG-5.0, and PEG-7.5, respectively. The dried PSAP products are white-colored beads with an average diameter of around 1.5 mm (See
Swelling Behavior of PSAP Beads
[0086] The swelling behavior of the PSAP beads was studied using microalgae cultivation medium, BG-11 medium. See, e.g., Liu et al., Environ. Sci.: Nano, 7, 2021-2031, 2020. Since the precursor contains a large amount of ionic monomer, lots of ionic side groups are bonded to the polymer backbone after polymerization. The resulting PSAP beads have high water affinity and high permeability. When the dried beads are in contact with an aqueous solution, the water molecules attack the bead surface and quickly penetrate into the inner pores due to the capillary effect. As the polymer network swells, the pores inside the beads are enlarged and gradually filled with water. Thus, the swelling process of the beads is spontaneous and does not need additional driving forces. The highly porous structure of the PSAP beads greatly increases the specific surface area of the polymer, enhances its contact with water molecules, and also provides extra volume for water retention (See
[0087] To investigate the effects of pore structure on bead swelling, the swelling kinetics of the SAP beads and PSAP beads in BG-11 medium was monitored. The SAP and PSAP beads have the same chemical composition for the polymer network, except for the difference in the pore structures (See
Microalgae Harvesting Performance
[0088] According to the rational design, the optimal PSAP beads should achieve both a high swelling capacity, such that only a small number of beads is required for high capacity concentration and a high harvesting efficiency that the loss of microalgae is minimized during the concentration process. To evaluate the microalgae harvesting performance, the PSAP beads were used to concentrate the model microalga, Chlorella vulgaris, which is a unicellular and spherically shaped green alga with a size of 3-5 μm.
[0089] Based on the swelling properties results, the PSAP beads were applied to harvest microalgae, and spectrophotometry was used to measure microalgae concertation, thereby analyzing harvesting efficiency. The treatment time was 30 minutes for all harvesting experiments. The concentration factor was set at around 2, which means the liquid volume should be reduced to half after treatment and the final microalgae concentration would be doubled. The PSAP beads are negatively charged because of the carboxylate groups introduced by co-polymerization of the ionic monomer. The negative surface charge of the beads results in an electrostatic repulsion toward negatively charged microalgal cells during the harvesting at circum-neutral pH conditions. The results shown in
[0090] Without wishing to be bound by theory, the decrease in harvesting efficiency may be caused by more microalgal cells attaching to the PSAP beads with higher porosity and left on the beads after treatment. Both differential interference contrast (DIC) and fluorescence microscopy were used to observe and visualize the distribution of microalgal cells on bead surface or inside beads after treatment. As shown in
[0091] In order to achieve effective and efficient microalgae harvesting at the lowest possible cost, PSAP beads were prepared with 5.0 wt. % PEG and selected due to their excellent swelling properties and optimal pore structure. The selected PSAP beads have a highly porous structure and thus large specific surface area, resulting in a much higher rate of water absorption than non-porous polymer. It takes only 30 minutes for such beads to reach their water absorption capacity, while it may require several hours for normal SAPs to achieve a similar swelling level. In addition, both the porosity and pore size of the PSAP beads with 5.0 wt. % are moderate so that the water absorption capacity is sufficient while the adsorption of microalgal cells onto the beads is minimized to avoid possible biomass loss after harvesting.
Process Optimization of Microalgae Harvesting
[0092] The harvesting process using PSAP beads with 5.0 wt. % PEG was further studied and optimized. The concentration factor, namely the ratio of the sample volume before and after treatment, is an important parameter in the microalgae harvesting process. For a certain amount of microalgal suspension, an increased PSAP dosage should result in a higher concentration degree due to the continuous decrease in residual liquid volume. As shown in
[0093] The decline of recovery efficiency at higher concentration factors is mainly caused by losses of liquid during the separation of beads from the concentrated microalgae. For example, when the PSAP dosage increases, the entrainment of liquid between the hydrated beads increases, which is difficult to separate or collect and results in loss of microalgae. At a higher concentration factor, the higher viscosity of the concentrated microalgal suspension may increase the surface attachment of microalgal cells to the beads and result in lower harvesting efficiency. Considering all these effects, when the initial microalgal concentration is 0.2 g L.sup.−1, an optimized concentration factor for microalgae harvesting should be about 4-6 to avoid disadvantageous loss of biomass for a single-stage operation. Under such conditions, the PSAP beads can achieve an effective and low-cost concentration with the harvesting efficiency higher than 95%, which is comparable to or even better than the performance of energy-intensive harvesting methods such as centrifugation. See, e.g., Singh et al., J. Environ. Manage., 217, 499-508. The optimal concentration factor may vary depending on the initial microalgal concentration. For example, a relatively lower concentration factor may be preferred to maintain a high harvesting efficiency at higher initial microalgal concentrations due to the increased cell attachment.
[0094] The fast and efficient microalgae harvesting methods using PSAP beads, as described herein, also have several additional advantages, such as simple operation, mild conditions, nontoxicity, and free of residues. Thus, the viability of the microalgal cultures should not be affected after treatment. To demonstrate the viability, flow cytometry combined with cell staining was used to detect and identify live and dead cells in microalgal samples. Because of the difference in permeability, live microalgae with intact cell membranes exhibited significantly enhanced green fluorescence, while dead microalgae with damaged cell membranes exhibited weak green fluorescence under the same excitation conditions.
[0095] In some cases, the microalgal concentration may still not be high enough after a single concentration treatment. For example, it requires an extremely high biomass density for effective processing in direct oil extraction and biogas fermentation (30-100 g L.sup.−1 in dry weight). See, e.g., del Campo et al., Biotechnol. Bioeng., 110, 3227-3234, 2013; Wei et al., Bioresour. Technol., 249, 713-719, 2018. Under this circumstance, multistage harvesting may be required in order to obtain desired concentrated products.
[0096] Accordingly, the harvesting performance of the PSAP beads in microalgal suspensions with a relatively high initial concentration was investigated. As shown in
Regeneration and Reuse of PSAP Beads
[0097] To achieve sustainable microalgae harvesting processes, the possibility of reusing the PSAP beads was investigated. To regenerate the PSAP beads, the hydrated beads after microalgae harvesting were heated in an oven to evaporate absorbed water. The reclaimed beads were then reused to concentrate and harvest microalgae. The absorption-desorption process of the PSAP beads was controlled under the same conditions, in which the absorption time is 30 minutes at 22° C. and the desorption time was 2 hours at 60° C. for each cycle.
EXAMPLES
Materials and Methods
Microalgae Cultivation and Biomass Measurement
[0098] The microalgae used in this work, Chlorella vulgaris, was obtained from Carolina Biological Supply Company (Burlington, N.C.). The microalgae were cultivated using BG-11 culture medium. The composition of BG-11 medium for microalgae cultivation is shown in the table below.
TABLE-US-00001 Concentration Concentration Compound (mM) Compound (mM) H.sub.3BO.sub.3 46 NaNO.sub.3 0.23 MnCl.sub.2 4H.sub.2O 9 K.sub.2HPO.sub.4 0.3 ZnSO.sub.4 7H.sub.2O 0.77 MgSO.sub.4 7H.sub.2O 0.24 Na.sub.2MoO.sub.4 2H.sub.2O 1.6 CaCl.sub.2 2H.sub.2O 0.031 CuSO.sub.4 5H.sub.2O 0.3 Citric Acid H.sub.2O 0.021 Co(NO.sub.3).sub.2 6H.sub.2O 0.17 Ferric Ammonium 0.0027 Citrate NaNO.sub.3 17.6 Na.sub.2EDTA 2H.sub.2O 0.19
[0099] The as-prepared BG-11 medium had a pH of 7.76 and conductivity of 2360 μS cm.sup.−1.
[0100] The sterilized flasks containing the microalgae were placed in a culture incubator (VWR International, Radnor, Pa.) with the temperature set at 22° C. and the light-to-dark time ratio of 1:1. The microalgal biomass density was determined by measuring the optical density at wavelength 685 nm (OD.sub.685) using a UV-Vis spectrophotometer (Hach DR6000, Loveland, Colo.). All samples were properly diluted by BG-11 medium before the test to ensure the absorbance is within the range of 0.05-1. The obtained OD.sub.685 values were then converted to biomass density (dry cell weight) based on the linear correlation: c (g L.sup.−1)=0.2853OD.sub.685+0.0004 (See
Preparation of PSAP Beads
[0101] To prepare PSAP beads, a reaction mixture containing ionic monomer (6 wt. % of sodium acrylate), non-ionic monomer (4 wt. % of acrylamide), and crosslinker (0.1% of N,N′-methylenebisacrylamide) was prepared. Poly(ethylene glycol) (PEG) with an average molecular weight of 6000 g mol.sup.−1 was selected as the porogen and added to the reaction mixture (2.5-7.5 wt. %). Next, the initiator, 0.3 wt. % of ammonium persulfate, was added to the system and mixed well until fully dissolved. The 96-well plate with each well containing 15 μL of precursor solution was sealed and placed into a bath heater (Thermo Scientific, Waltham, Mass.) for 20 minutes at 70° C. The resultant polymer beads were washed with 95% ethanol to remove the porogen and then thoroughly dried in a 60° C. oven to obtain PSAP beads.
[0102] SAP beads, as the control group, were prepared using the same process but without the addition of PEG. The subsequent procedures including aliquoting and polymerization were similar. The reaction time for SAP fabrication was extended to 60 minutes for complete polymerization. The as-obtained SAP beads were then rinsed with DI water three times and dried at 60° C.
Characterization of PSAP Beads
[0103] Imaging and analysis of the SAP and PSAP beads were performed by scanning electron microscopy (SEM, Hitachi SU8230, Tokyo, Japan). All specimens were coated with gold for 15 seconds at 20 mA by sputter coating (Quorum Q150T ES, Lewes, United Kingdom) prior to imaging. The swelling process of the SAP beads and PSAP beads prepared with different amounts of PEG (2.5-7.5 wt. %) in BG-11 medium was monitored for 1 hour using digital microscopy (Dino-Lite AM73915, Torrance, Calif.). During the swelling, the weight of the hydrated beads was measured and compared with the weight of the dried beads to calculate the swelling ratio (S=(m.sub.hydrated−m.sub.dried)/m.sub.dried). Three replicates were conducted for each kind of beads in the swelling kinetics test.
Microalgae Harvesting Using the PSAP Beads
[0104] The performance of the PSAP beads for microalgae harvesting was tested. A certain amount of PSAP beads (m.sub.beads) was added to a sterile tube with 5 mL of microalgal suspension (liquid volume: V.sub.0, biomass density: c.sub.0). The PSAP dosage was calculated based on the initial suspension volume and the dry bead weight, PSAP dosage (g L.sup.−1)=m.sub.beads/V.sub.0. After 30 minutes absorption, the tube containing the microalgae and hydrated beads was gently shaken by hand to avoid aggregation and reduce biomass loss in subsequent separation. Next, the concentrated microalgae were separated from the hydrated beads using a pipet. The volume (V) and biomass density (c) of the concentrated liquid were measured to determine the harvesting efficiency, ρ(%)=cV/c.sub.0V.sub.0×100. Triplicate testing was performed for all harvesting conditions. The mean values and standard deviations of the obtained experimental results were calculated and reported. To investigate the microalgae adsorption on the PSAP beads, the surface and cross section of the beads after harvesting were visualized and analyzed by digital microscopy and fluorescence microscopy (Zeiss Axio Observer 7, Oberkochen, Germany). The viability of microalgal cells before and after PSAP treatment was determined by a flow cytometer (BD Accuri C6, San Jose, Calif.). The microalgae were stained by green fluorescent SYTO 9 nucleic acid dye (5 The excitation wavelength was 488 nm and fluorescence signals at 530 nm were measured to differentiate live and dead cells.
Regeneration and Reusability of the PSAP Beads
[0105] The PSAP beads were applied to harvest 5 mL of microalgal suspension at an initial concentration of 0.2 g L.sup.−1. After the treatment, the hydrated beads were separated and dewatered in a 60° C. oven for 2 hours. The regenerated PSAP beads were then used to treat another 5 mL of microalgal suspension. The absorption-desorption process of the PSAP beads was repeated five times (30 minutes absorption and 2 hours desorption). During the five cycles, the bead swelling ratio, microalgae harvesting efficiency, and concentration factor were monitored. After that, the PSAP beads were immersed in DI water for 1 hour to wash off the absorbed salt and reused for microalgae harvesting.
[0106] The description of the present embodiments of the invention has been presented for purposes of illustration but is not intended to be exhaustive or to limit the invention to the form disclosed. Many modifications and variations will be apparent to those of ordinary skill in the art. As such, while the present invention has been disclosed in connection with an embodiment thereof, it should be understood that other embodiments may fall within the spirit and scope of the invention.
[0107] All patents and publications cited herein are incorporated by reference in their entirety.