Abstract
Magnetic graphene-based aerogels have attracted intensive interest due to their unique properties. In this study, a two-step strategy was proposed to fabricate a family of magnetic reduced graphene oxide aerogels (abbreviated as rGO/Fx, x = 1, 2 and 3) as adsorbents for removing heavy metals from water. The hydrogen bonds between poly(vinyl) alcohol (PVA) and rGO maintained the integrity of the rGO/Fx structures evidenced by FT-IR and Raman spectra. The rGO/Fx showed a unique structure with nanoparticles/nanoplates embedded on rGO sheets by SEM observation. The rGO/Fx consisted of PVA, rGO and Fe-based species (Fe3O4, Fe0 and FeOOH) identified by PXRD, TGA and XPS analysis. The impressive magnetic property of rGO/Fx can be easily tuned by the mass ratio of Fe/GO. The saturation magnetizations were 0.50, 0.72, and 9.59 emu/g for rGO/F1, rGO/F2 and rGO/F3, respectively. The capacity of rGO/F1 was calculated to be 21.84 and 16.10 mg/g for Cd2+ and Pb2+, respectively. This study may contribute a novel synthesis method of magnetic graphene aerogels by using polymers and metals, and offer an alternative adsorbent for removing heavy metals.
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1 Introduction
Graphene, exfoliated from natural graphite, is a two-dimensional (2D) carbon layer material, which has attracted extensive interest in the fields of chemistry and material science, due to its unique structure, large specific surface area and excellent mechanical property (Cong et al., 2014; Mao et al., 2015). Though graphene is theoretically a superior adsorbent, it cannot practically achieve this purpose. The main reason is that graphene nanosheets are usually prone to restacking up driven by weak van der Waals attractions among individual layers, severely reducing its specific surface area and restricting its application (Jiang & Fan, 2014; Perreault et al., 2015).
In this regard, three-dimensional graphene aerogels (3D GA) assembled from 2D sheets have drawn considerable attention (Upadhyay et al., 2014). In comparison with the 2D structure, 3D GA contain diverse hierarchical pores including micro-, meso- and macropores, in which the texture of the micro- and mesoporosity can generate a large specific surface area and the texture of the macroporosity can guarantee easy mass transfer to internal surfaces (Mao et al., 2018; Shen et al., 2015). This feature is greatly beneficial to the improvement of adsorption performance. Notedly, the macroscopic monolith morphology makes 3D GA convenient for manipulation and collection in application (Kemp et al., 2013). Based on these distinct properties, 3D GA has exhibited remarkable advantages (Qiu et al., 2018). A number of synthesis strategies for 3D GA have been reported, such as self-assembly, template-assisted preparation and direct deposition. Among these, the self-assembly method can afford a convenient and scalable process to fabricate graphene aerogels with excellent thermal stability (Chen & Yan, 2011; Cong et al., 2014; Xu et al., 2010a, 2010b). Many materials, such as DNA, organic molecules, metal ions and polymers, have already been used as cross-linkers for the self-assembly of GO sheets via covalent bonding, electrostatic interaction, and hydrogen bonding (Cao et al., 2014; Xu et al., 2010a, 2010b).
To expand the potential application of 3D GA, numerous efforts have been made for the fabrication of the 3D GA composites with designable and controllable structures. For instance, graphene was deposited on diverse template surfaces including spongy Ni foam, polystyrene spheres, silica spheres, and cellulose, and then the corresponding composites were easily garnered (Luo & Zhi, 2015). Moreover, the incorporation of 3D GA with other nanostructures (e.g. NPs, nanorods, nanotubes, and nanosheets) is deemed as an efficient method for the fabrication of new composites (Cong et al., 2014). Among them, magnetic composites have been highlighted due to their unique magnetic property. These composites integrate the porous structure of 3D GA and the property of magnetic nanoparticles (Sahraei et al., 2017; Wu et al., 2019).
Magnetic aerogels can be prepared by several methods. For instance, ferrous ions can be used as reductants for GO self-assembly, and their products would be decorated on the resultant 3D GA (Cong et al., 2012). A polymer-template method was also proposed for the synthesis of magnetic aerogels, and this method can enhance nanostructures of the aerogel (Zhuang et al., 2019). Recently, another strategy combining filler-loaded networks with vacuum freeze-drying was used to fabricate magnetic aerogels. This method can endow the resultant aerogels with strong superparamagnetic behavior (Arabkhani & Asfaram, 2020).
However, the aerogels usually suffer from unsatisfactory structural stability, which has limited their application. Polymers or metal ions can induce crosslinking of GO, and reinforce the structure of aerogels by different mechanisms. Presumably, structural stability of aerogels may tend to be enhanced by combining polymers and metal ions. However, the study about fabrication of magnetic graphene-based aerogels by a simple method is still scarce.
In this study, we proposed a combination strategy for preparation of magnetic aerogels, which combined the template effect of poly(vinyl) alcohol (PVA) and the modification functionality of iron species. The role of PVA was investigated in the formation of rGO/Fx. The iron species in the resultant aerogels were identified based on characterization technologies. The tuning mechanism of magnetic property of rGO/Fx was also studied. Taking Cd2+/Pb2+ as model pollutants, the adsorption performance of rGO/Fx was primarily estimated. This study aims to provide a novel synthesis concept of magnetic aerogels by using polymers and metal ions.
2 Experimental Section
2.1 Materials and Reagents
Graphene oxide (GO) suspension (10 mg/mL), poly(vinyl) alcohol (PVA, Mw ~ 145,000), FeCl3·6H2O, Pb(NO3)2, NaBH4, and Cd(NO3)2·4H2O were provided by Sinopharm Chemical Reagent Co., Ltd. (Shanghai, China). All chemicals in this study were of analytical grade and used directly without any further purification. The cadmium and lead standard solutions (1000 mg/L) were purchased from General Research Institute for Nonferrous Metals (Beijing, China). Pb(II) and Cd(II) stock solutions were prepared by dissolving corresponding nitrate salts in ultrapure water, respectively.
2.2 Synthesis of rGO/Fx
A two-step strategy was applied to fabricate a family of magnetic poly(vinyl) alcohol/graphene oxide (labeled as: rGO/Fx, x = 1, 2, 3).
Typically, a certain amount of Fe3+ and PVA (16 g/L) were dissolved in hot ultrapure water with vigorously stirring for 2 h, preparing three concentrations of Fe3+ by varying the mass of FeCl3·6H2O (solution 1: 0.013 mol/L, solution 2: 0.026 mol/L, solution 3: 0.052 mol/L). 8 mg/mL GO suspension was prepared by diluting GO stock solution. Then, the as-prepared GO suspension was evenly divided into dozens of aliquots in some small beakers (2.5 mL of suspension in each beaker). In each beaker, 0.625 mL of mixing solution containing Fe3+ and PVA was added dropwise into GO suspension and stirred rapidly to accelerate gelation. Several seconds later, the hydrogel of PVA/GO/Fe3+ was thus formed. After freeze drying, the PVA/GO/Fe3+ aerogel was naturally obtained. Adding the solutions1, 2, and 3, we could prepare a family of aerogels, namely, PVA/GO/Fe3+-y, y = 1, 2, 3. For comparison, two control experiments were also conducted as follows: one was without PVA and the other was no addition of Fe3+. The corresponding aerogels were labelled as GO/Fe3+ and PVA/GO.
In the reducing process, the experiment groups and control groups were impregnated in NaBH4 solution (0.1 mol/L) and a redox reaction was initiated at room temperature under the nitrogen atmosphere, resulting in the conversion of Fe3+ and GO. After 2 h reaction, the as-synthesized hydrogels were rinsed for several times with ultrapure water until pH of eluting solutions became neutral. These hydrogels were dried again by lyophilization to yield rGO/Fx, PVA/rGO and rGO/Fe.
2.3 Characterization of rGO/Fx
The morphology and surface element species of the as-prepared rGO/Fx series were characterized via a field emission scanning electron microscopy (FESEM) combined with an energy dispersive X-ray (EDX) system (Hitachi SU-8010, Japan). The crystalline phases of rGO/Fx series were examined by an X′Pert PRO diffractor (PANalytical, Holland, Cu Kα, λ = 0.15406 nm) under the condition of 40 kV and 40 mA. Fourier transforming infrared spectra (FT-IR) were recorded on a total reflection infrared spectrometer (Thermo Fisher Scientific, Nicolet-6700, USA). Raman spectra were obtained via a Raman spectrometer (Horiba HR-800, France, λ = 532 nm). The specific surface areas and pore distributions of rGO/Fx series were calculated from the nitrogen adsorption–desorption isotherms, determined on an automatic chemical adsorption instrument (Quantachrome Autosorb-1, USA). X-ray photoelectron spectra (XPS) of rGO/Fx series were examined in a PHI 5000C ESCA system (PHI, USA). The stability of rGO/Fx series was measured on a thermogravimetric analyzer (TGA, PerkinElmer, USA) from 25 ℃ to 800 ℃ at a rate of 10 ℃/min. The magnetic intensity of rGO/Fx series was determined under the condition of ± 20,000 Oe at 300 K by Vibrating Sample Magnetometer (VSM, MPMS-3, USA).
2.4 Adsorption Performance
The adsorption tests were conducted in conical flasks containing 100 mL of pollutant solution (Cd2+/Pb2+) and 50 mg of rGO/Fx, which were placed in a shaker and continuously stirred. At predetermined time intervals (~ 360 min), an aliquot of supernatant was taken from the containers by using 1 mL pipette, and then filtered with syringes equipped with polytetrafluoroethylene filters (0.22 µm of pore diameter). The collected filtrate was stored for subsequent analysis.
Ionic samples were measured by polarized Zeeman Atomic Absorption Spectrophotometer ZA3000 Series (AAS, Hitachi, Japan). In this study, all adsorption experiments were carried out in duplicate and the corresponding average values were reported. The adsorption amounts (q) were calculated from the following Eq. 1, and Eqs. 2 and 3 are mathematical expressions of the pseudo first-order model (PFO) and the pseudo second-order model (PSO) (Dai et al., 2019; Guo & Wang, 2019; Yu et al., 2017):
where C0 and Ct (mg/L) are initial concentration and instant concentration (at time t) of Cd2+ and Pb2+ in the solution, respectively. V (mL) represents the solution volume, and m (mg) is the mass of rGO/Fx. qt and qe (mg/g) are the instant and equilibrium adsorption amounts, respectively. k1 (min−1) and k2 (g mg−1 min−1) are the kinetic constants of PFO and PSO, respectively.
3 Results and Discussion
3.1 The Role of PVA in the Fabrication of rGO/Fx
During the synthesis process, an interesting phenomenon can be found that when PVA participated in the reaction, the rGO/Fx morphology was generally retained after even undergoing a redox reaction, otherwise it would be highly loose (control group: rGO/Fe). Considering this fact, it can be inferred that PVA may act as an important role in maintaining the structure intactness (Zakaria & Kamarudin, 2021; Zhang et al., 2018). In the first step, PVA and Fe3+ played a synergistic role in the gelation due to the strong hydrogen bonds and electrostatic attraction (Mohammadian et al., 2019).
As displayed in the Scheme 1, there were three main changes when PVA/GO/Fe3+ reacted with NaBH4. Firstly, GO was converted into reduced GO (rGO), in other words, these epoxy groups on the GO sheets were reduced (De Silva et al., 2017). Secondly, excess NaBH4 would further reduce in situ ferric ions into Fe3O4 or Fe0, even other iron-based species (Zou et al., 2016). Lastly, accompanying by the transformation of GO into rGO, a few hydrogen bonds were broken due to the disappearance of epoxy groups, while most hydrogen bonds, built among hydroxyl groups of PVA and hydroxyl/carboxyl groups on the basal plane of GO or rGO, were maintained. These hydrogen bonds could play against the dispersion of adjacent GO sheets, thus reserving an intact aerogel. Therefore, PVA is deemed as a necessary constituent to enhance the structural stability.
3.2 Morphology and Structure of rGO/Fx
The morphology of rGO/F1, rGO/F2 and rGO/F3 is displayed in Fig. 1. rGO/F1 possessed a stacking structure made up of sheets (Fig. 1a-b), as a result of the self-assembly of rGO sheets when redox reaction occurred. Only a small portion of iron-based species were attached to the sheets surface. No other species were recognized on the smooth surface from the magnification image (Fig. 1c). The porous crosslinking structure densely decorated by small nanoparticles was discovered from the images of rGO/F2 and rGO/F3 (Fig. 1d-e). These nanoparticles can be ascribable to the Fe-based species produced in the redox reaction.
In comparison with rGO/F1, the micromorphology of rGO/F2 and rGO/F3 exhibited a relatively compact but hierarchical structure. This may be because the Fe3+ intercalator imposed a strong attraction on the sheet structure when the mass ratio of Fe/GO increased. Although an increasement of Fe amount inevitably cause a low tenacity originated from the salting-out effect, PVA can restrain the detachment of rGO sheets via strong hydrogen bonds and molecular viscosity property (Dai et al., 2018; Yi et al., 2018). Driven by the resultant action, a hierarchical porous but dense structure of rGO/Fx (x = 2, 3) was eventually formed, and such a structure may show diverse features in terms of SAA and pore size distributions. Comparing Figs. 1f and i, we found another interesting phenomenon that the Fe-based species in rGO/F2 were mostly composed of nano-scale plates, while rGO/F3 consisted of a mixture of nanoplates and nanoparticles. This suggested that the Fe-based species were different when the mass ratios of Fe/GO were different. In other words, the structure and property of the as-synthesized aerogels can be tunable by adjustment of Fe/GO ratio. Except rGO/F1, rGO/F2 and rGO/F3 possessed a unique structure of nanoparticles- and nanoplates-on-sheets (Vafakhah et al., 2019; Wu et al., 2019).
The elemental compositions of rGO/Fx were examined by SEM–EDX. As shown in Fig. 2, rGO/Fx series were basically made of carbon, oxygen and iron elements. The iron contents were approximately 2.86%, 4.35%, and 11.63% for rGO/F1, rGO/F2, and rGO/F3, respectively. Iron contents showed an increment increasing at elevated mass ratios of Fe/GO. In view of the morphological difference, it is speculated that the composition and the property of the rGO/Fx series would be different.
PXRD spectra of the rGO/Fx series are depicted in Fig. 3a. As is known, the characteristic peak of GO was generally located at 2θ = ~ 11°. After reduction of GO, a new peak appeared at 2θ = 26.5° and this could confirm the conversion of GO into rGO (Liang et al., 2018). Moreover, a broad peak centered at 2θ = 20.5°, which is assignable to the typical peak of PVA (Dai et al., 2018). Peaks located at 2θ = 13.5°/23.5° were in line with those of orthorhombic iron hydroxide oxide (FeOOH, PDF No. 01–070-0714). The other two peaks at 2θ = 35.8° and 43.9° were consistent with those of orthorhombic Fe3O4 (PDF No. 01–075-1609) and cubic Fe0 (PDF No. 01–001-1252), respectively (Chen et al., 2019; Tang & Wang, 2018a, 2018b; Yao et al., 2019a, 2019b). By analysis above, the Fe-based species of rGO/F1 were mostly FeOOH, while those of rGO/F2 and rGO/F3 contained FeOOH, Fe3O4 and Fe0. Moreover, rGO/F2 and rGO/F3 differed in the relative contents of Fe-based species.
FT-IR spectra of PVA/GO (as a reference) and rGO/Fx series are shown in Fig. 3b. A small peak at 611 cm−1 was probably assigned to the vibration of Fe–O (Feng et al., 2017; Yao et al., 2019a, 2019b), implying the existence of FeOOH and Fe3O4 in the rGO/Fx series. This is consistent with the PXRD analysis. Comparing to the reference spectrum (PVA/GO), an obvious difference can be observed in those spectra of rGO/Fx series, i.e., the peak of hydroxyl groups (or hydrogen bonds) shifted to a short-wave direction along with an intensity fading. This phenomenon was probably related to the partial removal of hydrogen bonds, originated from the reduction of epoxy groups on GO (Fu, et al., 2018). However, the residual hydrogen bonds were enough to preserve the mechanical property of the resultant rGO/Fx series. Without PVA participation, a monolith structure would not be well preserved. The facts suggested that PVA played an essential role in the synthesis of the rGO/Fx series.
In general, the value of ID/IG reflects the defect degree of carbon-based materials, and also represents the mechanical stability of the materials to some extent (Xia et al., 2017; Xiao et al., 2013). To clearly identify the roles of PVA and ferric ions, Raman spectra of the control groups (without addition of PVA or Fe3+) and experiment groups were examined before and after reduction, as shown in Fig. 4. The value of ID/IG of GO/Fe3+ was 1.00, while it increased to 1.25 after reduction (Fig. 4a), which suggested that ferric ions raised the defect degree in the structure. As for PVA/GO, the value of ID/IG remained almost unchanged (from 0.96 to 0.93, in Fig. 4b). This indicated that PVA had a slight effect on the defect structure. Screening the spectra of rGO/Fx series (Fig. 4c-4e), we found that all these values increased, but the increment showed a decline trend as the mass ratio of Fe/GO increased. This finding can be explained by these ferric ions can create structural defects or cause the distortion deformation, while this ability is probably different for different Fe-based species. Overall, the morphology of rGO/Fx series were prone to more complexity after a redox reaction, as observed from the SEM images. The structural defect is usually conducive to interfacial processes such as adsorption or catalysis.
The nitrogen adsorption–desorption isotherms and the corresponding pore size distribution curves of rGO/Fx series are presented in Fig. 5. The BET specific surface areas (SSA) are 23.9, 33.6, and 29.1 m2/g, and the average pore diameter (APD) are 13.3, 18.0, and 17.3 nm for rGO/F1, rGO/F2 and rGO/F3, respectively. Apparently, these data reflected the mesoporous nature (H3 hysteresis loop observed in the isotherms) of rGO/Fx series, and this mesoporous structure is favored for adsorption and catalysis process (Li et al., 2018a, 2018b). The SSA and APD showed a similar trend: they increased firstly followed by a decline as the mass ratio of Fe/GO increased. Taking analysis of SEM and PXRD into account, we speculated the encapsulation of FeOOH nanoplates enlarged the SSA, but when plenty of Fe3O4 nanoparticles were generated in rGO/F3 structure, the agglomeration effect inversely reduced the SSA. Additionally, the SSA contribution of different Fe-based species may be different. Overall, both larger SSA and decoration by Fe-based species would play positive roles in the adsorption and catalysis process.
TG was determined in the temperature range of 40 ℃—800 ℃ under air atmosphere, and the curves are shown in Fig. 6a. Below 200 ℃, 8.2% weight loss in rGO/Fx series generally were assigned to the evaporation of water molecules. In the range of 200 – 400 ℃, 36.3% weight loss for rGO/F1 and rGO/F2, and 26.3% weight loss for rGO/F3 were mostly caused by the decomposition of oxygen-containing groups of GO and PVA (Mohammadian et al., 2019). In the range of 400 ℃—500 ℃, 36.4%, 32.3%, and 36.5% weight loss for rGO/F1, rGO/F2, and rGO/F3, respectively, can ascribe to the decomposition of rGO (Zhuang et al., 2019). Above 600 ℃, a weight increasing trend can be found in the rGO/Fx, as presented in Fig. 6b. The weight increments for rGO/F1, rGO/F2, and rGO/F3 were 1.7%, 0.4%, and 0.2%, respectively. This abnormal phenomenon may be generated from the conversion of Fe3O4 into Fe2O3. For rGO/Fx series, the end-products consisted of Fe2O3, a stable phase. The basic components of rGO/Fx can be approximately obtained, as listed in Table 1.
The magnetic hysteresis loops of rGO/Fx series are shown in Fig. 7. The saturation magnetizations were 0.498, 0.716, and 9.592 emu/g for rGO/F1, rGO/F2 and rGO/F3, respectively. rGO/F1 and rGO/F2 exhibited weak magnetic properties while rGO/F3 had a strong property. This phenomenon can be explained by different Fe contents and different magnetic species contents. Moreover, an obvious loop can be seen from the rGO/F3 curve, suggesting its ferromagnetism nature (Tang & Wang, 2019). Seeing the inset of Fig. 7, rGO/Fx series can be adsorbed to a magnet surface (the inset of Fig. 7). The rGO/Fx series with magnetic properties make them promising in the adsorption/catalysis process.
From XPS survey spectra of rGO/Fx series (Fig. 8a), three peaks at 284.8, 532.5, and 711.3 eV can be ascribed to typical peaks of C 1 s, O 1 s, and Fe 2p, respectively (Tang & Wang, 2019). This suggested that rGO/Fx series mainly consisted of C, O and Fe elements, which was in accordance with the SEM–EDX analysis. Figure 8b and d illustrate the high-resolution spectra of Fe 2p from Gaussian curve fitting. Two intense peaks at 725.0 and 711.8 eV were ascribed to the representative peaks of Fe 2p1/2 and Fe 2p3/2, and the other two small peaks at 719.3 and 706.8 eV were typical satellite peaks of Fe3+ and Fe0, respectively (Shao et al., 2019; Tang & Wang, 2018a, 2018b). Moreover, the intensity of these satellite peaks gradually increased when the mass ratio of Fe/GO increased. These findings suggested that the relative content of Fe3O4 and Fe0 increased (Li et al., 2018a, 2018b). Thus, the magnetism intensity of rGO/Fx became strong as the mass ratio of Fe/GO increased.
Peaks of C 1 s and O 1 s can be deconvoluted into several typical peaks, as shown in Fig. 9. For O 1 s, it was divided into three subspecies including HO-H (located at ca. 536.1 eV), O = C (located at ~ 532.5 eV) and O-Fe (located at ~ 530.5 eV). These results confirmed that there were hydroxyl groups, carboxyl groups and iron oxide or iron hydroxide in the rGO/Fx series (Wu et al., 2019). The hydroxyl groups were likely related to PVA, water and rGO whereas the carboxyl groups were mostly associated with rGO. Hydroxyl groups were occupied due to hydrogen bond interaction, and carboxyl groups could be responsible for Fe-based species attachment or as free groups for cation capture. The species contents are provided in Table 2. The relative contents of carboxyl groups accounted for approximately 85% and the relative contents of hydroxyl groups and metal–oxygen bonds only accounted for ~ 5% and ~ 10%, respectively. The contents of metal–oxygen bonds in rGO/F3 (~ 14.56%) were mostly linked to the high mass ratio of Fe/GO.
Likewise, the C 1 s species were deconvoluted into three main subspecies C = O (~ 288.5 eV), C–C (~ 286.3 eV) and C = C (~ 284.8 eV) (Shao et al., 2019). The C = O (carboxyl groups) and C = C (sp2 hybridization) were in main connection with rGO while the C–C bonds (sp3 hybridization) were deemed as evidence of existence of PVA. As listed in Table 2, the contents of C = C are the highest (~ 60%), and those of C–C and C = O accounted for ~ 35% and ~ 5%, although their contents showed a slight fluctuation with the mass ratio of Fe/GO.
3.3 Adsorption of Cd(II)/Pb(II) on rGO/Fx
As shown in Fig. 10a and c, the instant concentrations (Ct) of Cd2+ and Pb2+ decreased rapidly when the contact time increased. It seems that the adsorption performance was inversely proportional to the mass ratio of Fe/GO. The rGO/F1 can adsorb Cd2+ and Pb2+ with a better activity to a low residual concentration (0.52 and 3.45 mg/L for Cd2+ and Pb2+, respectively) compared with those of rGO/F2 (6.56 and 3.86 mg/L for Cd2+ and Pb2+, respectively) and rGO/F3 (5.76 and 4.21 mg/L for Cd2+ and Pb2+, respectively). As calculated from Eq. 1, the adsorption amount of rGO/F1 (21.84 and 16.10 mg/g for Cd2+ and Pb2+, respectively) was higher than those of rGO/F2 (8.80 and 15.28 mg/g for Cd2+ and Pb2+, respectively) and rGO/F3 (10.32 and 14.58 mg/g for Cd2+ and Pb2+, respectively). The inhibiting effect may be related to the iron oxides or hydroxides, since these products may consume some active sites in the synthesis stage.
The kinetic fitting curves are presented in Fig. 10b and d, and these parameters are listed in Table 3. It is obvious that PSO (R2 = ~ 0.9848, ~ 0.9125) can fit better than PFO (R2 = ~ 0.9391, ~ 0.8380) both for Cd2+ and Pb2+ adsorption. This indicated the rate-limiting step in adsorption was chemical adsorption (Chen et al., 2015; Gao et al., 2019; Vijayakumar et al., 2021). (The discussion of the intra-particle diffusion model (Eq. S1 and Fig. S1) can be found in Supplementary Materials). The oxygen-containing groups of GO sheets may serve as predominating active sites for heavy metals elimination (Koilraj et al., 2019). (Table S1 shows the performance of the rGO/Fx and other similar magnetic materials in the literature.)
Moreover, the rGO/Fx can be magnetically retrieved from solution after use. This merit would make them stand out, and would be very helpful for practical application.
4 Conclusions
In this study, a two-step strategy was proposed to prepare a family of magnetic reduced graphene oxide aerogels (abbreviated as rGO/Fx series, x = 1, 2 and 3). Poly(vinyl) alcohol was demonstrated to be essential in maintaining the rGO/Fx morphology. The rGO/Fx showed a unique structure with nanoparticles and nanoplates embedded on rGO sheets. The rGO/Fx consisted of PVA, rGO and Fe-based species (Fe3O4, Fe0 and FeOOH). The specific surface areas were 23.9, 33.6 and 29.1 m2/g and the saturation magnetizations were 0.50, 0.72 and 9.59 emu/g for rGO/F1, rGO/F2 and rGO/F3, respectively. The impressive magnetic property of rGO/Fx can be tunable by the mass ratio of Fe/GO. The rGO/Fx were able to efficiently remove Cd2+ and Pb2+ from water. This study may offer a new synthesis method of magnetic aerogels and an effective adsorbent for capturing heavy metals from water.
Data Availability
All data generated or analyzed during this study are included in this published article (and its supplementary information files).
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Acknowledgements
This work was supported by a research program from the State Administration of Science, Technology and Industry for National Defense, China ([2017]1474).
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Jiang-Bo Huo: Conceptualization, Methodology, Validation, Writing- original draft. Guoce Yu: Conceptualization, Writing—review & editing, Project administration, Funding acquisition.
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Huo, JB., Yu, G. Poly(vinyl) Alcohol-Assisted Fabrication of Magnetic Reduced Graphene Oxide Aerogels and their Adsorption Performance for Cd(II) and Pb(II). Water Air Soil Pollut 234, 231 (2023). https://doi.org/10.1007/s11270-023-06247-2
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DOI: https://doi.org/10.1007/s11270-023-06247-2