Abstract
In this study, citric acid (CA)-coated magnetite Fe3O4 magnetic nanoparticles (Fe3O4@CA MNPs) for use as draw solution (DS) agents in forward osmosis (FO) were synthesized by co-precipitation and characterized by Fourier transform infrared spectroscopy (FTIR), thermogravimetric analysis (TGA), dynamic light scattering (DLS), transmission electron microscopy (TEM) and magnetic measurements. Prepared 3.7% w/w colloidal solutions of Fe3O4@CA MNPs exhibited an osmotic pressure of 18.7 bar after purification without aggregation and a sufficient magnetization of 44 emu/g to allow DS regeneration by an external magnetic field. Fe3O4@CA suspensions were used as DS in FO cross-flow filtration with deionized (DI) water as FS and with the active layer of the FO membrane facing the FS and NaCl as a reference DS. The same transmembrane bulk osmotic pressure resulted in different water fluxes for NaCl and MNPs, respectively. Thus the initial water flux with Fe3O4@CA was 9.2 LMH whereas for 0.45 M NaCl as DS it was 14.1 LMH. The reverse solute flux was 0.08 GMH for Fe3O4@CA and 2.5 GMH for NaCl. These differences are ascribed to a more pronounced internal dilutive concentration polarization with Fe3O4@CA as DS compared to NaCl as DS. This research demonstrated that the proposed Fe3O4@CA can be used as a potential low reverse solute flux DS for FO processes.
Keywords: citrate-coated magnetic nanoparticle, forward osmosis, draw solution, osmotic pressure, non-ideality analysis
1. Introduction
Magnetic nanoparticles (MNPs) have attracted attention in research and industry in the chemical, environmental and medical fields. MNPs have shown promising performance in removing contaminants or reducing toxicity [1,2,3,4,5] and have generated interest in research into technical applications for treatment of polluted water and water purification processes [6,7,8,9,10]. In recent years, MNP’s have also attracted attention as materials for generating the driving force to transport water in a forward osmosis (FO) membrane separation process, one of the emerging membrane technologies that can meet the increasing global demand for water recycling and reuse [11]. FO is a technical term describing a natural phenomenon of osmosis: the transport of water molecules across a semi-permeable membrane [12]. In contrast to pressure-driven membrane processes, FO is driven by the osmotic pressure difference across the FO membrane. In ideal FO, a concentrated draw solution (DS) with high osmotic pressure extracts water from a dilute feed solution (FS) while ideally rejecting all FS solutes [13,14]. In order to function effectively as a draw agent in FO, the osmotic pressure of the DS must significantly exceed that of the FS. Simple inorganic salts, such as NaCl, remain the most widely used DS agents due to their ability to have high osmotic pressures while maintaining low solution viscosities. The strong affinity of small inorganic ions for water is reflected in their highly exothermic enthalpies of hydration [15]. Strong solvent-solute interactions provide high solution osmotic pressures while making the regeneration of DS more difficult. In resolving this problem, the development of easily removable DS agents, which allow for regeneration through exploitation of solute size, thermal sensitivity or magnetic properties, is desirable [16].
Although the FO technology is gaining popularity in niche applications including cold-concentration in the food and beverage industry, drawbacks, such as high reverse solute flux and high regeneration costs, still restrict wider application [17,18,19]. A reverse solute flux can potentially contaminate the FS apart from decreasing the osmotic pressure difference across the membrane. The suitability of a draw solute is defined by the ability to develop sufficient osmotic pressure in order to ensure a high water flux while maintaining low (ideally no) diffusion from the DS to the FS. The molecular size and ionic structure of the DS agent define its applicability in FO. A smaller molecular size of the DS agents reduces the internal concentration polarization and thus associated with a higher water flux however, this is generally also associated with higher reverse solute flux. In comparison, larger DS agent molecules are associated with less internal concentration polarization (and thus lower water flux) but also a lower reverse solute diffusion [20], the latter a prerequisite for use in cold-concentration.
Over the past years, a variety of compounds have been investigated as draw solutes, including sulfur dioxide [21], various inorganic salts and a variety of sugars [22,23], thermally unstable ammonium salts [24,25] polyelectrolytes [26] and MNP’s [27,28,29]. Iron oxide MNPs such as maghemite (γ-Fe2O3) and magnetite (Fe3O4) MNPs have been widely studied due to well-defined properties such as small uniform particle size in the range of 10 to 100 nm, biocompatibility, heat generation in response to an alternating magnetic field (AMF), easy surface manipulation for targeted release, low toxicity profile, and good colloidal stability [30]. Although pristine iron oxide MNPs have desirable properties (size and stability) as DS they cannot generate significant osmotic pressure without appropriate surface modification [31,32]. To improve water solubility and surface hydrophilicity, MNP’s functionalized with strong hydrophilic groups are considered as one of the feasible solutions to generate sufficient osmotic pressures, as well as allow for facile regeneration [33] as exemplified by Fe3O4 MNPs, which can be easily separated from water by an external magnetic field [34]. To maximize the osmotic pressure that is generated from the functional groups coated on the iron oxide MNPs, a high number of polymer hydrophilic groups must be available to interact with the solvent water molecules. Citric acid (CA) is a small molecule which is suitable for facile functionalization and confers hydrophilic properties to MNPs by virtue of three –COOH groups with one or two –COOH groups absorbed on the surface of the MNPs and at least one remaining free [32,35,36,37]. Recently Khazaie et al. and his co-workers synthesized Fe3O4 nanoparticles and covalently functionalized them with tri-sodium citrate. The DS with an optimal ratio of CA: MNPs (2:1) with concentrations of 20, 40, 60, and 80 g L−1 showed water fluxes of 7.1, 10.7, 14.2, and 17.1 LMH, with osmotic pressures of 114, 117, 120 and 124 bar respectively [38]. Applications with MNP coated with sodium citrate has also reported by [39,40,41].
Here we investigate the synthesis of Fe3O4 MNP’s coated with CA and evaluate their feasibility as DS agents in FO. MNP’s were synthesized by co-precipitation of Fe2+ and Fe3+ aqueous solutions with hydrophilic CA by adding a base in a one-pot synthesis. The research is comprised of two sections: (1): the synthesis of Fe3O4@CA MNP’s with characterization using FTIR, TGA, DLS, TEM and magnetic measurements and (2): DS testing using an AIM™ hollow fibre FO (HFFO) module where water flux and reverse solute flux is benchmarked against NaCl as DS using deionized (DI) water as the FS.
2. Materials and Methods
2.1. Materials
The chemicals used for the synthesis of Fe3O4 MNP’s coated with CA were iron (III) chloride hexahydrate (FeCl3 × 6H2O, Sigma Aldrich, Darmstadt, Germany), iron (II) chloride tetrahydrate (FeCl2 × 4H2O, Sigma Aldrich), sodium hydroxide (NaOH, Sigma Aldrich) and CA (C6H8O7, Laiwu Taihe Biochemistry Co., Laiwu, Shadong Province, China). All the chemicals used in the experiments were of analytical grade. Inert nitrogen (N2, Messer, Ruše, Slovenia) atmosphere was used during synthesis. Ethanol (C2H5OH, Sigma Aldrich) was used as washing materials. DI water is used throughout all experiments. The chemical used for FO filtrations was sodium chloride (NaCl, LabExpert, Berdyansk, UK). DI water was used for NaCl solution preparation, for cleaning the membrane module, and as FS during performing baseline measurement.
2.2. Synthesis of Fe3O4@CA MNPs
For the synthesis of Fe3O4@CA MNPs a typical co-precipitation process was applied [35]. A 25 mL solution containing 1.28 M Fe3+, 0.64 M Fe2+ (molar ratio 2:1), and 1.28 M CA was placed in a three-necked flask at 80 °C (oil bath) with vigorous stirring (340 rpm) for 20 min under N2 atmosphere. Then 250 mL 1 M NaOH solution was added drop by drop using a dropping funnel and the solution was continuously stirred for an additional 60 min at 80 °C under an N2 atmosphere. The reaction scheme is as follows (Equation (1)):
(1) |
In the final product, in addition to the desired Fe3O4 MNP’s, a large amount of dissolved sodium and chloride ions is also present. To reduce their concentration, the suspension was washed several times as described here (discussed in more details in Section 3.1). Fe3O4@CA MNPs were uniformly dispersed in 100 mL of DI as a stock solution by 30-min sonication in an ultrasonic bath. The synthesis process is shown schematically in Figure 1.
2.3. Characterization of Fe3O4@CA MNP’s
The functional groups of Fe3O4@CA MNP’s were analysed by Fourier transform infrared spectroscopy (FTIR, mod. 5000, Perkin-Elmer Inc., Beaconsfield, UK). The FTIR spectrum was measured in the range 4000–400 cm−1. The weight loss of Fe3O4@CA MNP’s was characterized by thermogravimetric analysis (TGA, TGA/SDTA, 851e Mettler Toledo, Greifensee, Switzerland). The measurement was performed under air from 30 to 800 °C at a heating rate of 10 K/min. The average hydrodynamic particle size, zeta potential, and isoelectric point (IEP) were determined by dynamic light scattering (DLS, Zetasizer Nano ZS, Malvern, Worcestershire, UK) using purified Fe3O4@CA MNP’s water dispersions at 0.1 g/L with DI and pH adjusted from the current pH value to 2.0 during the measurements with an auto titrator [42]. The size and morphology of the nanoparticles were investigated by transmission electron microscopy (TEM, JEM-2010F, JEOL, Tokyo, Japan). The Fe3O4@CA MNP suspension was deposited on a copper-grid-supported carbon film specimen holder and left to dry at ambient conditions. The empirical size distribution of the MNPs was estimated by measuring an area of the MNP’s on the TEM image. The average particle size dTEM is given as a number-weighted average equivalent diameter (from Gaussian fit of the empirical distribution), the diameter of a circle having the same area as the imaged particle. The surface ligand concentration ns (the number of ligands per particle) were estimated using Equation (2) [43]:
(2) |
where, ω is weight loss (%), d is particle diameter (nm), estimated from the TEM images to be 3–7 nm assuming spherical-shaped nanoparticles, ρFe3O4 is 5.18 g/cm3 and MCA is 192.14 g/mol.
The room temperature magnetization curve of the Fe3O4@CA MNP’s as a dry powder was measured using a vibrating sample magnetometer (VSM; model 7307, Lake Shore Cryotronics, Westerville, OH, USA). The saturation magnetization Ms of the sample is given as the average of the magnetiza-tions measured at magnetic field strength H of −10 kOe and 10 kOe.
The osmolality of the DS prepared from MNP’s was measured with an osmometer (Gonotec-Osmomat 030, Berlin, Germany) and the osmotic pressure, π of Fe3O4@CA MNP’s solutions were calculated using Equation (3):
(3) |
where R is gas constant (8.31447 J/mol K), T is the absolute temperature (K), n is the amount of substance (mol), c is the molarity of a solution (mol/L), and ϕ is an osmotic coefficient (-). The characterisation methods in detailed is presented in a previous paper [29].
2.4. FO Filtrations
The FO filtration experiments were performed using the AIM™ HFFO module. The specification of the AIM™ HFFO module and experimental set-up used in the study was presented in a previous paper [44]. The cross-flow velocity used for experiments was 120 mL/min in co-current mode. Characteristics of used DS and FS are presented in Table 1.
Table 1.
DS | FS | VDS (mL) | VFS (mL) | |
---|---|---|---|---|
1 | MNP (3.7% w/w) | DI water | 100 | 250 |
2 | 0.45 M NaCl | DI water | 100 | 250 |
Water flux, Jw (LMH) across the membrane was calculated using Equation (4) [45]:
(4) |
where: ΔV total volume change of permeate water (L), A effective membrane area (m2) and Δt is the time (h).
The reverse salt flux, Js (GMH) was determined using Equation (5) [45]:
(5) |
where: γ0 = initial concentration of the FS (g/L), V0 = initial volume of the FS (L), γt = solute concentration at time t (g/L), Vt = volume of the FS measured at time t (L), A = effective membrane area (m2) and Δt = time (h).
The recovery fraction (R) indicates the amount of feed recovered as permeate using Equation (6) [46]:
(6) |
where: VP = the permeate volume of water (L), and VF = the volume of water in the FS (L).
3. Results and Discussion
The results are presented as follows: First, MNP’s were synthesized by co-precipitation of Fe2+ and Fe3+ aqueous solutions with hydrophilic CA by adding a base in a one-pot synthesis, see Figure 1. Second, the as-prepared Fe3O4@CA MNP’s were fully characterized using TEM, FTIR, TGA, DLS, zeta potential and magnetic measurements (Section 3.1). Third, the non-ideality of the solutions of un-grafted and grafted CA molecules onto MNP’s was investigated (Section 3.2) and the osmotic properties and FO performance described (Section 3.3). Finally, FTIR and TGA analyses were done of Fe3O4@CA MNP’s after the FO process (Section 3.4).
3.1. Magnetic Particle Preparation
After synthesis, the Fe3O4@CA MNPs solution was cooled to room temperature (21 °C), and the black product was separated by a permanent magnet (0.8 T). Fe3O4@CA MNPs were rinsed out four times with DI water, once with ethanol and finally with DI again. In Table 2 conductivity, pH and osmotic pressures of Fe3O4@CA MNPs after synthesis and washing cycles are presented.
Table 2.
Conductivity (mS/cm) |
pH | Osmotic Pressure (bar) |
|
---|---|---|---|
After synthesis | 69.4 | 12.5 | 33.2 |
Drained water | 70.8 | 12.9 | 32.2 |
1. Cleaning with DI water | 28.8 | 12.4 | 10.3 |
Drained water | 27.7 | 12.5 | 10.2 |
2. Cleaning with DI water | 16.1 | 12.1 | 5.4 |
Drained water | 15.5 | 12.2 | 5.4 |
3. Cleaning with DI water | 7.6 | 11.9 | 2.5 |
Drained water | 7.3 | 11.9 | 2.6 |
4. Cleaning with DI water | 3.3 | 11.6 | 0.9 |
Drained water | 2.7 | 11.4 | 0.9 |
5. Cleaning with ethanol | 0.38 | 11.9 | 89.6 |
Drained ethanol | / | / | / |
6. Cleaning with DI water | 0.62 | 11.3 | / |
Drained water | 0.5 | 11.3 | / |
Prepared DS | 0.77 | 10.3 | 13.2 |
From Table 2, the changes in conductivity, pH and osmotic pressure after synthesis and multiple washing with ethanol and water can be followed (explained in more details in the Results (Section 3.4.2.)).
3.2. Characterization of Fe3O4@CA MNPs
The coordination of the CA (carboxylic groups) to the nanoparticle surface is confirmed by FTIR spectroscopy (Figure 2). In the FTIR spectrum of bare MNPs (black), the band at 580 cm−1 corresponds to the vibration of the Fe-O bonds in the crystal lattice of Fe3O4 (magnetite) [47,48]. A broad band at 3400 cm−1 can be assigned to the structural OH groups of water molecules [36]. The FTIR spectrum of pure CA (red) dispersive and broadened O-H stretching vibration at 3400 cm−1 and C=O stretching vibration of (R-COOH) group at 1739 cm−1 are present. Asymmetrical and symmetrical stretching vibrations of the carboxylate group were observed at 1547 cm−1 and 1386 cm−1, respectively.
Compared to bare MNPs, two additional peaks were observed for Fe3O4@CA MNP’s at the wavelengths 1600 cm−1 and 1400 cm−1 (blue), representing the symmetrical and asymmetrical stretching of C=O and CO vibration of the three carboxyl groups (-COOH) as well as the large and intense band from 3200 to 3400 cm−1 corresponding to the OH group confirms the presence of non-dissociated OH groups of the CA and water traces [36,49,50]. Thus, our FTIR measurements confirmed that the CA binds chemically to the magnetite surface by carboxylate chemisorption and citrate ions are formed.
A thermogravimetric analysis (TGA) was performed to measure the organic content of Fe3O4@CA MNP’s. The results of the TGA are shown in Figure 3 which shows the weight loss of Fe3O4@CA. Here, the correction (3%) due to the oxidation of magnetite in hematite was taking into the account and the mass loss of the acetic acid was therefore accordingly corrected.
The weight loss curve observed in a range of 100 to 800 °C is attributed to the evaporation of water, the decomposition of the bound citrate molecules on the Fe3O4 MNPs’ surfaces 3% [41,51] and to oxygen during magnetite oxidation 3.3%. The initial weight loss below 160 °C due to the evaporation of physically adsorbed water was 5% and the organic content of coated Fe3O4@CA was determined to be 6.3%. This is the mass percentage of all surface coated organic groups on the MNPs corresponding to desorption of CA molecules on the magnetite particles. The number of COOH groups bound to the surface of the nanoparticles can be calculated according to Equation (2). Assuming a spherical shape of the MNPs with an average diameter of five nm, then the estimated total number of COOH groups is 71 per particle.
The surface charges of the bare Fe3O4 MNPs and Fe3O4@CA MNPs were characterized by zeta potential measurements as a function of pH from 7 to 2 and z-average hydrodynamic diameter changes as a function of pH. Figure 4 presents the results for Fe3O4@CA MNPs.
As reported in the literature, the isoelectric point (IEP) for neat Fe3O4 is ~6.8 [41,52]. Fe3O4@CA MNP’s have a negative zeta potential of −30 mV at pH = 7 as shown in Figure 4. This observed phenomenon is likely caused by the adsorption of CA molecules on the bare MNPs’ surface, where the surface charges were influenced by the introduction of carboxylate groups [41,53]. The zeta potential value becomes more negative with increasing pH due to the increase of OH– ions in the dissociated solution and deprotonation of the carboxyl groups of CA. This confirmed the presence of negatively charged carboxylate groups’ on the MNPs surface. The ensuing electrostatic repulsion ensures their colloidal stability in aqueous suspension where some of the carboxylate groups from CA are adsorbed/coordinated on the surface of MNPs while uncoordinated species protrude into the water medium [54]. Thus, the effective charge at pH 7 provides stabilization of Fe3O4@CA MNPs. The effective hydrodynamic diameter of Fe3O4@ CA MNPs, measured by DLS at 25 °C, changes from 500 to 3500 nm with varying pH. Since the pH was adjusted with HCl, the effective particle size increased when the IEP 4.93 was reached and then decreased back to the original size when the pH dropped below the IEP 4.93.
The osmotic pressure of the Fe3O4@CA solution was determined by the freezing point depression method. Table 3 shows concentration, osmotic pressure, size, number of molecules (ns), IEP, and magnetic saturation of Fe3O4@CA MNPs.
Table 3.
Sample Name | Concentration [%] |
pH | Osmotic Pressure [bar] |
dx [nm] |
nS [molecules/nm2] |
IEP |
Ms [emu/g] |
---|---|---|---|---|---|---|---|
Fe3O4@CA | 3.7 | 7 | 18.7 | 3–7 | 0.904 | 4.93 | 44 |
Morphology and size of the nanoparticles Fe3O4@CA were observed using TEM. Upon drying on the TEM specimen support the nanoparticles formed agglomerates (Figure 5a,b). However, at the edges of the agglomerates, the deposit of nanoparticles is relatively thin and individual nanoparticles can be resolved (Figure 5b). The nanoparticles are approximately spherical and their estimated average diameter dTEM is 5.2 nm ± 0.9 nm (Figure 5c).
The room-temperature magnetization curve of the nanoparticles Fe3O4@CA suggests a superparamagnetic state of the nanoparticles, due to the lack of measured coercivity and remanence (Figure 6). The saturation magnetization of the Fe3O4@CA Ms of 45 emu/g is significantly smaller than reported values for bulk Fe3O4, which are in the range between 92 emu/g and 100 emu/g [54]. In the Fe3O4@CA magnetic nanoparticles are “diluted” with diamagnetic physically adsorbed water and CA (Figure 4) which reduces the measured Ms. The TGA analysis suggests that the diamagnetic mater contributes approx. 8 wt.% of the simple Fe3O4@CA, therefore estimated value of Ms of the Fe3O4 is 49 emu/g. The value is still smaller than value characteristic for bulk material and is consistent with small size of the Fe3O4 MNPs [55]. Because of the surface effects, namely the magnetically distorted surface layer small nanoparticles in general exhibit lower values of saturation magnetization than bulk material of the same composition [56].
3.3. Properties of Fe3O4@CA
The advantage of coated nanoparticles is that they may have higher osmotic pressures than solutions consisting of the grafting agents alone at the same concentration [16]. The increase in osmotic pressure values can be attributed to the increased solvent-accessible surface area and thus improved hydration. The non-ideality parameters I and S were determined for Fe3O4@CA, see Figure 7 and M*CA calculated using the semi-empirical model Equations (7) and (8):
(7) |
(8) |
where mw and ms is the mass of water and solute respectively; S and I are the non-ideality parameters, π the osmotic pressure, ρ is the density of water at temperature T, M is the molecular weight of the solute and R, T gas constant and temperature.
The results show that the osmotically derived molecular weights are M*CA = 176.12 g/mol for pure CA and M*CA = 57.9 g/mol for MNP@CA. The value M*CA = 57.9 g/mol is significantly lower than the nominal standard value of 192.12 g/mol, indicating that the MNP-grafted CA molecule are almost four-fold stronger as osmotic agent as CA alone.
3.4. Forward Osmosis Process Evaluation
3.4.1. Determination of Jw and Js
Fe3O4 MNPs at concentrations of CA of 3.7% were used to prepare Fe3O4@CA as DS in a lab-scale cross-flow FO filtration setup. In Figure 8 water flux is presented where DI was used as FS and Fe3O4@CA as well as the 0.45 M NaCl was used as DS, respectively, in order to make a comparison between Fe3O4@CA solution and standard DS (NaCl solution). For this purpose, we wanted to imitate the FO process when using Fe3O4@CA solution as DS, including measuring conditions (e.g., starting volumes of FS and DS, initial osmotic power of DS). Imitation was performed using NaCl solution as DS, therefore, 0.45 M concentration of NaCl was used to give initial osmotic pressure comparable to the solution of Fe3O4@CA. The filtrations with Fe3O4@CA were stopped after 2 h to ensure sufficient data to have an insight into the filtration dynamics. The filtration with 0.45 M NaCl as DS was finished spontaneously in 1 h (75.2 g of FS left) because the water flux was higher in comparison when Fe3O4@CA was used as DS agent despite the similar initial osmotic transmembrane gradient.
The initial water flux of 0.45 M NaCl solution as reference is higher (14.1 LMH) when comparing to the Fe3O4@CA (9.3 LMH). A uniform water flux decline was observed for all solutions as a function of time. The overall water flux decreased 30% and 70% for 0.45 M NaCl and Fe3O4@CA, respectively, due to dilution of DS and reduction in the osmotic pressure difference between FS and DS.
When Fe3O4@CA was used as DS, the diffusion of water molecules decreased due to the higher concentration polarization of the Fe3O4@CA from the draw side (96.1 mL), presented in Table 5. Therefore, the dilutive ICP in FO mode is stronger for Fe3O4@CA and the effective osmotic gradient across the active layer is lower, see Figure 9.
Table 5.
DS | FS |
VDS (mL) Initial |
VFS (mL) Initial |
VDS (mL) | VFS (mL) | |||
---|---|---|---|---|---|---|---|---|
at 1 h | at 2 h | at 1 h | at 2 h | |||||
1 | MNP | DI water | 100 | 250 | 185.1 | 206.2 | 163.6 | 142.5 |
2 | 0.45 M NaCl | DI water | 100 | 250 | 273.7 | / | 75.2 | / |
The decrease in water flux with an increase in the conductivity indicates that the main driving force across the FO membrane is the osmotic pressure difference between the DS and FS. The conductivity was monitored (Figure 10a) and reverse solute flux, Js (Figure 10b) was calculated using Equation (5) where concentrations in FS were obtained out of measured conductivity data in the FS. Although the 0.45 M NaCl solution gives rise to higher water flux (29.1% higher) compared to Fe3O4@CA, the reverse solute flux is also larger (2.5 versus 0.08 GMH). The conductivity increased (as well as Js) for the 0.45 M NaCl solution during one hour.
The suitability of a draw solute is defined by its ability to develop osmotic pressure, which leads to higher water flux, and lower diffusion to the feed side. From the molecular view, the size and ionic structure of the draw solute defines its applicability in the FO process. The lower molecular size increases the diffusivity of the DS and reduces the internal concentration polarization that leads to the higher water flux, while the reverse salt flux is also enhanced. The larger molecules are designed as DS to prevent reverse salt diffusion.
In this study, small molecules such as NaCl that were used for comparison generated high osmotic pressure at low solution viscosities and mitigate ICP due to their high reverse solute flux [20].
The synthesized Fe3O4@CA particles are relatively large, and the reverse diffusion was low, however, the potency of DS to build up a reasonable osmotic pressure and water flux was enhanced by increasing particle hydrophilicity.
The used AIM™ HFFO module was cleaned using only DI water for 30 min and then a new baseline experiment was performed under the same conditions. The water flux of the cleaned AIM™ HFFO module (restored to about 97%) was almost the same as that of the pristine module. This indicates that simple physical flushing can effectively rejuvenate the used module membrane and the average water flux can be restored to about 93.2% even after 2 cycles.
3.4.2. Development of the FS and DS Osmotic Pressures
The osmotic pressure of the Fe3O4 functionalized with CA is relatively high due to the higher hydrophilicity because the CA molecule possesses two terminal COOHs, one central COOH, and one C−OH group, which are all active in bonding with iron oxide via the Fe−OH groups [35,36]. For a given concentration and temperature, the osmotic pressure depends on the solubility and molecular weight of the DS moieties. From the CA (H3C6H5O7) speciation, CA will be mostly deprotonated as HC6H5O72− and C6H5O73− over a broad pH range (5.0–9.0). Thus, at pH = 7 there will be mostly HC6H5O72− and C6H5O73− functional groups of CA [57]. The deprotonated CA made MNP@CA surfaces highly negatively charged [32]. However, both MNP@CA (and CA alone) will have counter ions closely attached and will thus not contribute to bulk solution conductivity as such.
When comparing the development in FS conductivity (Figure 10a) with the FS osmotic pressure development (Figure 11a) it is observed that the osmotic pressure of the FS with 0.45 M NaCl as DS reached 0.5 bar in one hour while at the same time, the osmotic pressure for the FS with Fe3O4@CA as DS reached 4 bar, respectively. This suggests that DS solutes diffuse across the membranes into the FS. The DS contains four components: Fe3O4@CA MNP, unconjugated CA, ethanol and NaOH. As the conductance increase in the FS is negligible (compared to NaCl) the reverse solute flux could in principle be due to any of the three first components or a combination thereof (since NaOH would be dissociated and thus give rise to an increase in solution conductivity). However, a 4 bar FS osmotic pressure at the end of the experiment (see Figure 12a) generated solely by Fe3O4@CA MNPs would correspond to a 0.8% w/w solution which is opaque. Since the FS is transparent it is unlikely that Fe3O4@CA MNP’s are crossing the membrane. This leaves only ethanol and/or unconjugated CA as potential reverse flux solute candidates. The FS ethanol concentration was measured to be 0.07% which corresponds to an osmotic pressure of 2.8 bar. Thus, ethanol diffusion can explain some of the FS osmotic pressure increase during the experiment. With regards to unconjugated CA is crossing the membrane, it is noted that CA has a molecular weight of 192 Da which is relatively large as compared to ionic salts. However, it has previously been shown that peptides with molecular weights of 375 and 692 Da can cross a thin film composite Aquaporin Inside™ Membrane (AIM) FO membrane and the transport mechanism was determined to be diffusion-based [58]. Thus, it is likely that unconjugated CA (with Na+ as associated counter ion) also contributes to the increase in FS osmotic pressure.
When comparing with other studies where magnetic nanoparticles were used a DS in FO, several studies have focused on poly-sodium acrylate (PSA) coated MNPs as DS. Thus, a water flux of 5.3 LMH and a DS osmotic pressure of 11.4 bar has been reported using PSA-MNPs at 0.078%, wt% (~1.3 g/L) DS concentration ([57]. Ge and co-workers [59] reported an osmotic pressure of 11–12 bar at a concentration of ~15%, wt% PSA (Mn 1800) as DS. Similar osmotic pressures were obtained with 24–48%, wt% PSA DS (in the form of free polyelectrolyte osmotic agent) [31]. The significant difference in osmotic pressure between PSA-MNP solutions and free PSA solutions reflect the non-ideality of PSA-MNP solutions similar to what we observe in this study. However, the robustness of PSA-MNP based DSs (i.e., their ability to maintain their osmotic pressure after repeated concentrations) is still an issue [29].
In our previous study [29] a 7% solution of robust PSA-coated MNPs yielded an initial Jw of 4.2 LMH and an osmotic pressure of 9 bar and a reverse solute flux Js of 0.05 GMH. Thus, the results presented here where Fe3O4@CA MNPs a 3.7% solution yielded approximately a two-fold higher initial Jw (Figure 8) and osmotic pressure (Figure 9) implies that the Fe3O4@CA MNPs DS is about four-fold more potent as DS compared to a DS based on PSA-coated MNPs. However, the nominal reverse solute flux for Fe3O4@CA of 0.08 GMH (Figure 10b) is slightly higher than for PSA-coated MNP based DS.
3.5. Characterization after FO Process
The functional groups of chemical bonds between Fe3O4 and CA after the FO process were characterized by FTIR (Figure 13a). It is confirmed that the Fe3O4@CA spectral features are preserved, so the CA coating on Fe3O4 MNPs was maintained. The TGA results in Figure 13b show the weight loss of Fe3O4@CA before (black curve) and after the FO process (red curve). The overall weight loss of Fe3O4@CA before the FO process was determined 8.3% and after the FO process 6.6%. The total estimated number of COOH groups is still 85 molecules per particle after FO process.
4. Conclusions
The CA-coated Fe3O4 nanoparticles (Fe3O4@CA MNPs) have been synthesized for use as draw solution (DS) agents in forward osmosis (FO) and systematically analyzed. Non-ideality of the solutions of ungrafted and grafted CA molecules onto MNPs indicates that the MNP-grafted CA molecule are almost four-fold stronger as osmotic agent as CA alone. Carboxyl groups of CA have an affinity for MNPs, thus preventing aggregation. The osmotic pressure of as-prepared MNP@CA was high enough to be used as a DS in FO. Although the 0.45 M NaCl solution gives rise to higher water flux (for 29.1%) compared to Fe3O4@CA, the reverse solute flux is also larger (2.5 to 1.8 GMH). These differences are ascribed to a more pronounced internal concentration polarization associated with Fe3O4@CA as DS as compared to NaCl as DS. The results showed that the conductivity of the feed solution stays the same low level before and after FO filtration, and that the reverse solute flux of Fe3O4@CA MNPs is negligible. Still the FS osmotic pressure is increasing during the filtration, which is ascribed to diffusion of DS ethanol and unconjugated CA. Thus, an effective purification of Fe3O4@CA MNPs is a prerequisite in order to be able to benefit fully from the low inherent reverse solute flux. Therefore, FO can be considered as a potential candidate for a broad range of concentration applications where current technologies still suffer from critical limitations
Table 4.
S | I | |
---|---|---|
MNP@CA | 434 | 3.92 |
CA | 142 | −0.17 |
Acknowledgments
This research was funded by Slovenian National Agency, grant numbers P3-0036, P2-0006, P2-0089, J1-9169, and J3-1762, L4-1843, and NEPWAT funded by the Novo Nordisk Foundation.
Author Contributions
Conceptualization I.B., I.P. and C.H.-N.; experimental investigation J.S., H.B., M.D. and S.G.; writing—original draft preparation, review and editing, I.B., I.P., H.B., J.S., M.D., S.G. and C.H.-N. All authors have read and agreed to the published version of the manuscript.
Funding
The authors are grateful for support from the Novo Nordisk Foundation (NNF18OC0034918).
Institutional Review Board Statement
Not applicable.
Informed Consent Statement
Not applicable.
Data Availability Statement
Data available on request.
Conflicts of Interest
The authors declare no conflict of interest.
Footnotes
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.
References
- 1.Farmany A., Mortazavi S.S., Mahdavi H. Ultrasond-assisted synthesis of Fe3O4/SiO2 core/shell with enhanced adsorption capacity for diazinon removal. J. Magn. Magn. Mater. 2016;416:75–80. doi: 10.1016/j.jmmm.2016.04.007. [DOI] [Google Scholar]
- 2.Lu X., Deng S., Wang B., Huang J., Wang Y., Yu G. Adsorption behavior and mechanism of perfluorooctane sulfonate on nanosized inorganic oxides. J. Colloid Interface Sci. 2016;474:199–205. doi: 10.1016/j.jcis.2016.04.032. [DOI] [PubMed] [Google Scholar]
- 3.Roto R., Yusran Y., Kuncaka A. Magnetic adsorbent of Fe3O4@SiO2 core-shell nanoparticles modified with thiol group for chloroauric ion adsorption. Appl. Surf. Sci. 2016;377:30–36. doi: 10.1016/j.apsusc.2016.03.099. [DOI] [Google Scholar]
- 4.Turcu R., Socoliuc V., Craciunescu I., Petran A., Paulus A., Franzreb M., Vasile E., Vekas L. Magnetic microgels, a promising candidate for enhanced magnetic adsorbent particles in bioseparation: Synthesis, physicochemical characterization, and separation performance. Soft Matter. 2015;11:1008–1018. doi: 10.1039/C4SM02430C. [DOI] [PubMed] [Google Scholar]
- 5.Tratnyek P.G., Johnson R.L. Nanotechnologies for environmental cleanup. Nano Today. 2006;1:44–48. doi: 10.1016/S1748-0132(06)70048-2. [DOI] [Google Scholar]
- 6.Al-Hobaib A., Al-Sheetan K., El Mir L. Effect of iron oxide nanoparticles on the performance of polyamide membrane for ground water purification. Mater. Sci. Semicond. Process. 2016;42:107–110. doi: 10.1016/j.mssp.2015.08.004. [DOI] [Google Scholar]
- 7.Ghaemi N., Madaeni S.S., Daraei P., Rajabi H., Zinadini S., Alizadeh A., Heydari R., Beygzadeh M., Ghouzivand S. Polyethersulfone membrane enhanced with iron oxide nanoparticles for copper removal from water: Application of new functionalized Fe3O4 nanoparticles. Chem. Eng. J. 2015;263:101–112. doi: 10.1016/j.cej.2014.10.103. [DOI] [Google Scholar]
- 8.Sabbatini P., Yrazu F., Rossi F., Thern G., Marajofsky A., de Cortalezzi M.F. Fabrication and characterization of iron oxide ceramic membranes for arsenic removal. Water Res. 2010;44:5702–5712. doi: 10.1016/j.watres.2010.05.059. [DOI] [PubMed] [Google Scholar]
- 9.Shen J.F., Tang J., Nie Z.H., Wang Y.D., Ren Y., Zuo L. Tailoring size and structural distortion of Fe3O4 nanoparticles for the purification of contaminated water. Bioresour. Technol. 2009;100:4139–4146. doi: 10.1016/j.biortech.2009.04.004. [DOI] [PubMed] [Google Scholar]
- 10.Yantasee W., Warner C.L., Sangvanich T., Addleman R.S., Carter T.G., Wiacek R.J., Fryxell G.E., Timchalk C., Warner M.G. Removal of Heavy Metals from Aqueous Systems with Thiol Functionalized Superparamagnetic Nanoparticles. Environ. Sci. Technol. 2007;41:5114–5119. doi: 10.1021/es0705238. [DOI] [PubMed] [Google Scholar]
- 11.Zhao S., Zou L., Tang C.Y., Mulcahy D. Recent developments in forward osmosis: Opportunities and challenges. J. Membr. Sci. 2012;396:1–21. doi: 10.1016/j.memsci.2011.12.023. [DOI] [Google Scholar]
- 12.Wei R., Zhang S., Cui Y., Ong R.C., Chung N.T.-S., Helmer B.J., de Wit J.S. Highly permeable forward osmosis (FO) membranes for high osmotic pressure but viscous draw solutes. J. Membr. Sci. 2015;496:132–141. doi: 10.1016/j.memsci.2015.08.054. [DOI] [Google Scholar]
- 13.Salehi H., Rastgar M., Shakeri A. Anti-fouling and high water permeable forward osmosis membrane fabricated via layer by layer assembly of chitosan/graphene oxide. Appl. Surf. Sci. 2017;413:99–108. doi: 10.1016/j.apsusc.2017.03.271. [DOI] [Google Scholar]
- 14.Shakeri A., Salehi H., Rastgar M. Chitosan-based thin active layer membrane for forward osmosis desalination. Carbohydr. Polym. 2017;174:658–668. doi: 10.1016/j.carbpol.2017.06.104. [DOI] [PubMed] [Google Scholar]
- 15.Yamada S., Tanaka M. Softness of some metal ions. J. Inorg. Nucl. Chem. 1975;37:587–589. doi: 10.1016/0022-1902(75)80387-3. [DOI] [Google Scholar]
- 16.Roach J.D., Bondaruk M.M., Burney Z. Osmotically Driven Membrane Processes—Approach, Development and Current Status. IntechOpen; London, UK: 2018. Nonideal Solution Behavior in Forward Osmosis Processes Using Magnetic Nanoparticles. [Google Scholar]
- 17.Cui Y., Liu X.-Y., Chung T.-S., Weber M., Staudt C., Maletzko C. Removal of organic micro-pollutants (phenol, aniline and nitrobenzene) via forward osmosis (FO) process: Evaluation of FO as an alternative method to reverse osmosis (RO) Water Res. 2016;91:104–114. doi: 10.1016/j.watres.2016.01.001. [DOI] [PubMed] [Google Scholar]
- 18.Xue W., Yamamoto K., Tobino T. Membrane fouling and long-term performance of seawater-driven forward osmosis for enrichment of nutrients in treated municipal wastewater. J. Membr. Sci. 2016;499:555–562. doi: 10.1016/j.memsci.2015.11.009. [DOI] [Google Scholar]
- 19.Han G., Liang C.-Z., Chung T.-S., Weber M., Staudt C., Maletzko C. Combination of forward osmosis (FO) process with coagulation/flocculation (CF) for potential treatment of textile wastewater. Water Res. 2016;91:361–370. doi: 10.1016/j.watres.2016.01.031. [DOI] [PubMed] [Google Scholar]
- 20.Qasim M., Darwish N.A., Sarp S., Hilal N. Water desalination by forward (direct) osmosis phenomenon: A comprehensive review. Desalination. 2015;374:47–69. doi: 10.1016/j.desal.2015.07.016. [DOI] [Google Scholar]
- 21.Ling M.M., Chung T.-S. Desalination process using super hydrophilic nanoparticles via forward osmosis integrated with ultrafiltration regeneration. Desalination. 2011;278:194–202. doi: 10.1016/j.desal.2011.05.019. [DOI] [Google Scholar]
- 22.Zhao D., Chen S., Guo C., Zhao Q., Lu X. Multi-functional forward osmosis draw solutes for seawater desalination. Chin. J. Chem. Eng. 2016;24:23–30. doi: 10.1016/j.cjche.2015.06.018. [DOI] [Google Scholar]
- 23.Kessler J., Moody C. Drinking water from sea water by forward osmosis. Desalination. 1976;18:297–306. doi: 10.1016/S0011-9164(00)84119-3. [DOI] [Google Scholar]
- 24.McCutcheon J.R., McGinnis R.L., Elimelech M. A novel ammonia—carbon dioxide forward (direct) osmosis desalination process. Desalination. 2005;174:1–11. doi: 10.1016/j.desal.2004.11.002. [DOI] [Google Scholar]
- 25.McGinnis R.L., Elimelech M. Energy requirements of ammonia–carbon dioxide forward osmosis desalination. Desalination. 2007;207:370–382. doi: 10.1016/j.desal.2006.08.012. [DOI] [Google Scholar]
- 26.Ge Q., Su J., Amy G.L., Chung N.T.-S. Exploration of polyelectrolytes as draw solutes in forward osmosis processes. Water Res. 2012;46:1318–1326. doi: 10.1016/j.watres.2011.12.043. [DOI] [PubMed] [Google Scholar]
- 27.Ling M.M., Wang K.Y., Chung N.T.-S. Highly Water-Soluble Magnetic Nanoparticles as Novel Draw Solutes in Forward Osmosis for Water Reuse. Ind. Eng. Chem. Res. 2010;49:5869–5876. doi: 10.1021/ie100438x. [DOI] [Google Scholar]
- 28.Guo C.X., Huang S., Lu X. A solventless thermolysis route to large-scale production of ultra-small hydrophilic and biocompatible magnetic ferrite nanocrystals and their application for efficient protein enrichment. Green Chem. 2014;16:2571–2579. doi: 10.1039/c3gc42645a. [DOI] [Google Scholar]
- 29.Ban I., Markuš S., Gyergyek S., Drofenik M., Korenak J., Helix-Nielsen C., Petrinić I. Synthesis of Poly-Sodium-Acrylate (PSA)-Coated Magnetic Nanoparticles for Use in Forward Osmosis Draw Solutions. Nanomaterials. 2019;9:1238. doi: 10.3390/nano9091238. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 30.Wu W., Wu Z., Yu T., Jiang C., Kim W.-S. Recent progress on magnetic iron oxide nanoparticles: Synthesis, surface functional strategies and biomedical applications. Sci. Technol. Adv. Mater. 2015;16:023501. doi: 10.1088/1468-6996/16/2/023501. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 31.Zufia-Rivas J., Morales P., Veintemillas-Verdaguer S. Effect of the Sodium Polyacrylate on the Magnetite Nanoparticles Produced by Green Chemistry Routes: Applicability in Forward Osmosis. Nanomaterials. 2018;8:470. doi: 10.3390/nano8070470. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 32.Liu J., Dai C., Hu Y. Aqueous aggregation behavior of citric acid coated magnetite nanoparticles: Effects of pH, cations, anions, and humic acid. Environ. Res. 2018;161:49–60. doi: 10.1016/j.envres.2017.10.045. [DOI] [PubMed] [Google Scholar]
- 33.Chung N.T.-S., Zhang S., Wang K.Y., Su J., Ling M.M. Forward osmosis processes: Yesterday, today and tomorrow. Desalination. 2012;287:78–81. doi: 10.1016/j.desal.2010.12.019. [DOI] [Google Scholar]
- 34.Hong R., Feng B., Chen L., Liu G., Li H., Zheng Y., Wei D. Synthesis, characterization and MRI application of dextran-coated Fe3O4 magnetic nanoparticles. Biochem. Eng. J. 2008;42:290–300. doi: 10.1016/j.bej.2008.07.009. [DOI] [Google Scholar]
- 35.Manal-Mounir R., Eglal H., Gadallah A., Ali Azab H.M. Comparative study for the preparation of superparamagnetic-citric coated magnetic nanoparticle and fodesalination application. ARPN J. Appl. Sci. Eng. 2018;13:1150–1162. [Google Scholar]
- 36.Ge Q., Yang L., Cai J., Xu W., Chen Q., Liu M. Hydroacid magnetic nanoparticles in forward osmosis for seawater desalination and efficient regeneration via integrated magnetic and membrane separations. J. Membr. Sci. 2016;520:550–559. doi: 10.1016/j.memsci.2016.07.033. [DOI] [Google Scholar]
- 37.Srivastava S., Awasthi R., Gajbhiye N.S., Agarwal V., Singh A., Yadav A., Gupta R.K. Innovative synthesis of citrate-coated superparamagnetic Fe3O4 nanoparticles and its preliminary applications. J. Colloid Interface Sci. 2011;359:104–111. doi: 10.1016/j.jcis.2011.03.059. [DOI] [PubMed] [Google Scholar]
- 38.Khazaie F., Sheshmani S., Shokrollahzadeh S., Shahvelayati A.S. Desalination of Saline Water via Forward Osmosis Using Magnetic Nanoparticles Covalently Functionalized with Citrate Ions as Osmotic Agent. Environ. Technol. 2020:1–26. doi: 10.1080/09593330.2020.1866087. [DOI] [PubMed] [Google Scholar]
- 39.Guizani M., Saito M., Ito R., Funamizu N. Engineering of size-controlled magnetic nanoparticles for use as a draw solution in a forward osmosis process. Desalin. Water Treat. 2019;154:21–29. doi: 10.5004/dwt.2019.24088. [DOI] [Google Scholar]
- 40.Kadhim R.M., Al-Abodi E.E., Al-Alawy A.F. Citrate-coated magnetite nanoparticles as osmotic agent in a forward osmosis process. Desalin. Water Treat. 2018;115:45–52. doi: 10.5004/dwt.2018.22456. [DOI] [Google Scholar]
- 41.Na Y., Yang S., Lee S. Evaluation of citrate-coated magnetic nanoparticles as draw solute for forward osmosis. Desalination. 2014;347:34–42. doi: 10.1016/j.desal.2014.04.032. [DOI] [Google Scholar]
- 42.Kaszuba M., Corbett J., Watson F.M., Jones A. High-concentration zeta potential measurements using light-scattering techniques. Philos. Trans. R. Soc. A Math. Phys. Eng. Sci. 2010;368:4439–4451. doi: 10.1098/rsta.2010.0175. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 43.Park S.Y., Ahn H.-W., Chung J.W., Kwak S.-Y. Magnetic core-hydrophilic shell nanosphere as stability-enhanced draw solute for forward osmosis (FO) application. Desalination. 2016;397:22–29. doi: 10.1016/j.desal.2016.06.017. [DOI] [Google Scholar]
- 44.Petrinic I., Bukšek H., Galambos I., Gerencsér-Berta R., Sheldon M.S., Helix-Nielsen C. Removal of naproxen and diclofenac using an aquaporin hollow fibre forward osmosis module. Desalin. Water Treat. 2020;192:415–423. doi: 10.5004/dwt.2020.26082. [DOI] [Google Scholar]
- 45.Oh S.-H., Im S.-J., Jeong S., Jang A. Nanoparticle charge affects water and reverse salt fluxes in forward osmosis process. Desalination. 2018;438:10–18. doi: 10.1016/j.desal.2018.03.015. [DOI] [Google Scholar]
- 46.McCutcheon J.R., McGinnis R.L., Elimelech M. Desalination by ammonia–carbon dioxide forward osmosis: Influence of draw and feed solution concentrations on process performance. J. Membr. Sci. 2006;278:114–123. doi: 10.1016/j.memsci.2005.10.048. [DOI] [Google Scholar]
- 47.Zhang B., Tu Z., Zhao F., Wang J. Superparamagnetic iron oxide nanoparticles prepared by using an improved polyol method. Appl. Surf. Sci. 2013;266:375–379. doi: 10.1016/j.apsusc.2012.12.032. [DOI] [Google Scholar]
- 48.Gaihre B., Khil M.S., Lee D.R., Kim H.Y. Gelatin-coated magnetic iron oxide nanoparticles as carrier system: Drug loading and in vitro drug release study. Int. J. Pharm. 2009;365:180–189. doi: 10.1016/j.ijpharm.2008.08.020. [DOI] [PubMed] [Google Scholar]
- 49.Singh D., Gautam R.K., Kumar R., Shukla B.K., Shankar V., Krishna V. Citric acid coated magnetic nanoparticles: Synthesis, characterization and application in removal of Cd (II) ions from aqueous solution. J. Water Process. Eng. 2014;4:233–241. doi: 10.1016/j.jwpe.2014.10.005. [DOI] [Google Scholar]
- 50.Răcuciu M. Synthesis protocol influence on aqueous magnetic fluid properties. Curr. Appl. Phys. 2009;9:1062–1066. doi: 10.1016/j.cap.2008.12.003. [DOI] [Google Scholar]
- 51.Cheng C., Wen Y., Xu X., Gu H. Tunable synthesis of carboxyl-functionalized magnetite nanocrystal clusters with uniform size. J. Mater. Chem. 2009;19:8782–8788. doi: 10.1039/b910832g. [DOI] [Google Scholar]
- 52.Campelj S., Makovec D., Drofenik M. Preparation and properties of water-based magnetic fluids. J. Phys. Condens. Matter. 2008;20:204101. doi: 10.1088/0953-8984/20/20/204101. [DOI] [PubMed] [Google Scholar]
- 53.Imran M., Riaz S., Sanaullah I., Khan U., Sabri A.N., Naseem S. Microwave assisted synthesis and antimicrobial activity of Fe3O4-doped ZrO2 nanoparticles. Ceram. Int. 2019;45:10106–10113. doi: 10.1016/j.ceramint.2019.02.057. [DOI] [Google Scholar]
- 54.Cornell R.M., Schwertmann U.U. The Iron Oxides: Structure Properties, Reactions, Occurrences and Uses. 2nd ed. Completely Revised and Extended Edition; Wiley-VCH; Weinheim, Germany: 2003. [Google Scholar]
- 55.Kodama R. Magnetic nanoparticles. J. Magn. Magn. Mater. 1999;200:359–372. doi: 10.1016/S0304-8853(99)00347-9. [DOI] [Google Scholar]
- 56.Elbagerma M.A., Edwards H.G.M., Azimi G., Scowen I.J. Raman spectroscopic determination of the acidity constants of salicylaldoxime in aqueous solution. J. Raman Spectrosc. 2011;42:505–511. doi: 10.1002/jrs.2716. [DOI] [Google Scholar]
- 57.Dey P., Izake E.L. Magnetic nanoparticles boosting the osmotic efficiency of a polymeric FO draw agent: Effect of polymer conformation. Desalination. 2015;373:79–85. doi: 10.1016/j.desal.2015.07.010. [DOI] [Google Scholar]
- 58.Bajraktari N., Madsen H.T., Gruber M.F., Truelsen S.F., Jensen E.L., Jensen H., Hélix-Nielsen C. Separation of Peptides with Forward Osmosis Biomimetic Membranes. Membranes. 2016;6:46. doi: 10.3390/membranes6040046. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 59.Ge Q., Su J., Chung T.-S., Amy G. Hydrophilic Superparamagnetic Nanoparticles: Synthesis, Characterization, and Performance in Forward Osmosis Processes. Ind. Eng. Chem. Res. 2010;50:382–388. doi: 10.1021/ie101013w. [DOI] [Google Scholar]
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Data Availability Statement
Data available on request.