Graphene oxides cross-linked with hyperbranched polyethylenimines: Preparation, characterization and their potential as recyclable and highly efficient adsorption materials for lead(II) ions
Graphical abstract
Introduction
Lead(II) ions in water are of great concern due to their toxicity, non-biodegradability and accumulation in organisms or the food chain [1], [2]. With the rapid development of industries, the water pollution caused by Pb2+ contamination has become a serious issue. Long-term drinking of lead polluted water will cause serious disorders, such as kidney disease, anaemia and mental retardation. Due to their high toxicity, the elimination of Pb2+ from aqueous solution is crucial for the environmental pollution cleanup. Therefore, the efficient removal of Pb2+ from wastewater is very important and urgent. To date, several technologies and methods for Pb2+ removal from wastewater have been developed including solvent extraction, ion-exchange, membrane separation, reverse osmosis and adsorption [3], [4], [5]. Adsorption is one of the most promising and widely used approaches due to high efficiencies and economic feasibility [2], [6], [7]. A number of materials, such as activated carbon [8], zeolite [9], clay [10], kaolinite [11], microorganisms [12], manganese oxides [13] and carbon nanotubes [14], [15], have been successfully employed to adsorb Pb2+. However, the low removal efficiencies or low adsorption capacities of these adsorbents limit the engineering application. Therefore, it is necessary to develop new and more efficient materials for adsorption.
Carbon materials are significantly and heavily used for the removal of Pb2+ as an engineering adsorbent [16], [17]. Graphene oxide (GO), which is a new material in the carbon family, has attracted much attention for the adsorption treatment of lead-containing wastewater due to its huge surface area and a large number of functional groups [18]. Several researchers have applied GO or GO based materials for Pb2+ adsorption [19], [20], [21], [22], [23], [24], [25], [26]. However, the adsorption capacities are less than satisfactory. For example, Islam has reported Pb2+ adsorption using GO immobilized by polystyrene with an adsorption capacity of 227.92 mg g−1 [19]. A nanocomposite LS–GO–PANI was prepared via in situ polymerization, and this nanocomposite exhibited an adsorption capacity of 216.4 mg g−1 for Pb2+ [20]. Gui synthesized a magnesium silicate/reduced GO nanocomposite with a high adsorption efficiency for Pb2+ [21]. Recently, an aminosilanized GO was prepared for the selective adsorption of Pb2+, and the maximum adsorption capacity was determined to be 96 mg g−1 [22]. Polyamidoamine dendrimer (PAMAM) modified GO can be easily prepared and has a high adsorption capacity [27], [28], [29]. In comparison to linear polymers with amino groups, the metal ion binding capacity of PAMAM was much larger due to the presence of the EDA core [30]. GO-PAMAM were prepared via the “grafting-from” [31] or “grafting to” [29] method, and the GO-PAMAM 2.0 total adsorption capacity for Fe3+, Cr3+, Zn2+, Pb2+ and Cu2+ reached 1.007 mmol g−1.
Apparently, functionalization of GO is essential for improving its adsorption capacity [32], [33], [34], [35], especially by the dendritic polymers, such as PAMAMs. However, most reported GO and GO based materials cannot be directly applied as adsorbents because they are water soluble [25], [36] and small in size [23]. Assuming that adsorption occurs, the GO or GO based materials may be difficult to separate from the solution after the adsorption process using traditional separation methods due to its hydrophilic property. Therefore, the industrial application cost of GO or GO based composite materials will increase. In addition, the treated water may be re-polluted.
Therefore, the introduction of cross-linking with dendritic polymers could be more beneficial for enhancing the feasibility of GO based materials. Based on the specific spheroid-like shape, compact structure and multi-functionality, dendritic polymers (i.e., the dendrimers and hyperbranched polymers) have attracted tremendous interest, and these polymers are the most attractive compounds for the design of new structures and molecules [37], [38]. Unfortunately, the synthesis of dendrimers is a time-consuming and expensive process. Unlike dendrimers, hyperbranched polymers, which can be economically and easily prepared in one step, have gained increasing attention [38], [39], [40], [41], [42], especially in industrial applications. Commercially available hyperbranched polyethylenimine (HPEI) with a large number of primary and secondary amine groups has been widely used for encapsulation or adsorption of guest molecules [43], [44]. In addition, the number of the functional groups reacted as crosslink points will be reduced after the crosslinking reaction, which implies that the adsorption sites of these materials will be reduced. Differently and significantly, these gels have more adsorption sites over using the common cross-linking agent (especially double-functionality or tri-functionality monomer). Therefore, the objective of this work is to synthesize graphene oxide-hyperbranched polyethylenimine gels (GO-HPEI gels) that are recyclable and may possess a high adsorption capacity and be directly applied. These GO-HPEI gels could take full advantage of the characteristics of the specific physical, chemical and surface properties of GO including the specific spheroid-like shape, large number of amino groups of HPEIs, good stability and recyclability of the gels. Therefore, the GO-HPEI gel may have the potential to be a cost-effective adsorbent for the removal of Pb2+ from wastewater.
Section snippets
Materials
Hyperbranched polyethylenimines (HPEI) (Mn = 1800, 1 × 104 and 7.5 × 105 g/mol, namely HPEI1.8K, HPEI10K and HPEI750K, 99%) were obtained from Aldrich. Lead nitrate, sodium nitrate, potassium permanganate, concentrated sulfuric acid, hydrogen peroxide and other common chemicals were all obtained from Tianjin Chemical Reagent Co. graphite was obtained from Pingdu Graphite Co.
Apparatus and instruments
The FTIR spectra of the GO and GO-HPEI gels were recorded on a MAGNA550 FTIR spectrometer (Thermo Nicolet). The X-ray powder
Characterization of the GO and GO-HPEI gel
The FTIR pattern of GO is shown in Fig. 1 and reveals the presence of oxygen-containing functional groups. The peaks at 1115, 1403 and 1630 cm−1 correspond to C–O–C stretching, C–OH stretching and C–C stretching modes, respectively, of the sp2 carbon skeletal network, and the peaks located at 1734 and 3430 cm−1 correspond to CO stretching vibrations of the –COOH groups and O–H stretching vibration, respectively [46]. In comparison to GO, the GO-HPEI gel exhibits new bands at 1650–1659 cm−1 [6]
Conclusions
In the presented study, a new adsorbent (i.e., GO-HPEI gel) has been successfully prepared and characterized. Importantly, the GO-HPEI gels are different from the most reported GO-based materials and have superior adsorption performance for Pb2+. The adsorption capacities of the GO-HPEI gels for Pb2+ are highly pH dependent. The functional groups and specific spheroid-like shape of the GO-HPEI gel enhanced its adsorption ability for Pb2+. The maximum adsorption capacity for Pb2+ is as high as
Acknowledgements
This work was financially supported by the National Science Foundation of China (21304043, 51403097, 21171085), the Natural Science Foundation of Shandong Province (ZR2012BQ024, 2014ZRB019WZ) and Natural Science Foundation of Ludong University (LY2012003, LY2013010).
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