Self-assembling covalent organic framework functionalized poly (styrene-divinyl benzene-glycidylmethacrylate) composite for the rapid extraction of non-steroidal anti-inflammatory drugs in wastewater
Graphical abstract
Introduction
Non-steroidal anti-inflammatory drugs (NSAIDs) is a group of compounds that has antipyretic, anti-inflammatory and analgesic effects for the treatment of rheumatic disorders, inflammation and soreness [[1], [2], [3]]. Because of their broad-spectrum application, NSAIDs are consumed by means of numerous human activities and discharged into the environment through urine, wastewater, and the discarding of expired drugs. NSAIDs are continually introduced into the aquatic environment; therefore, they have made elicit chronic effects in aquatic and terrestrial inhabitants [4,5]. Hence, NSAIDs are regarded as emerging contaminants by the World Health Organization (WHO) [6,7]. Accordingly, the development of reliable analytical method for determining NSAIDs in water samples is crucially important.
To date, various sample pretreatment methods, such as liquid-liquid extraction (HF-LPME), ultrasound-assisted liquid-phase microextraction (UA-LPME), solid-phase extraction (SPE), and solid-phase microextraction (SPME), have been used in determining NSAIDs [[8], [9], [10], [11], [12]]. Among these methods, SPE is the most frequently used method because of its relatively convenient operation and high extraction efficiency. Moreover, the diverse choices for sorbents materials provided ample space for SPE development. Recently, K2Ti4O9, metal organic frameworks (MOF), and ionic liquid were applied as a modifier of the sorbent for extracting of NSAIDs [[13], [14], [15]]. Ting Wang et al. prepared a MOF-functionalized magnetic material for extracting NSAIDs in wastewater and environmental water samples [14]. Amiri et al. pretreated NSAIDs in biological fluids by using supercritical fluid extraction combined with SPE procedure (Fe3O4@SiO2@IL) [15]. All of the sorbents have their own merits, but because of their slow binding kinetics, they require long extraction times, which is an important limitation for high-throughput samples analysis.
Covalent organic frameworks (COFs) are covalently bound crystalline porous material which were composed of lightweight elements such as C, H, O, N and B. COF have become noteworthy since being first reported in 2005 [16,17]. These materials possess considerable fascinating properties including high specific surface area, excellent thermal stability, high porosity, and low density. Moreover, COFs are more stable in water and acidic media than MOFs [18]. With these unique properties, COFs have been considered as a promising sorbent material with favorable capacity. However, the direct use of COF in the sample pretreatment of NSAIDs have several drawbacks, such as the relatively low affinity of bare COF for NSAIDs and the tedious centrifugal separation. Hence, the design of COF-functionalized composites with a strong NSAID affinity, and an operational convenient device are essential for the rapid and highly efficient extraction.
In this study, we prepared a novel COF-functionalized poly (styrene-divinyl benzene-glycidylmethacrylate) composite (COF@PS-GMA) by generating COF on the surface of the PS-GMA particles for NSAID extraction. The composite could be successfully synthesized via hydrothermal reaction because of the strong π-πinteraction between monomers and PS-GMA particles, as well as the self-assembly nature of COF [19]. The π-electron system of the composite provided affinity sites for the interaction with NSAIDs. In addition, the mesopores of the COF layer could eliminate the large scale interferences from the complex matrix [20]. Moreover, we proposed a miniaturized in-syringe solid-phase extraction device by using filter holder [21]. Therefore, this study provides a COF-based composite couple with a miniaturized extraction device for the rapid and efficient extraction of NSAIDs in environmental water samples.
Section snippets
Reagents and instrumentation
Flurbiprofen, ketoprofen, aspirin, naproxen, diclofenac, indomethacin, and ibuprofen were supplied by Sigma-Aldrich (MO, USA). The standard stock solution (1000 mg L−1) of the seven NSAIDs was prepared by dissolving the compounds in HPLC-grade methanol. A series of working solution was obtained daily by diluting the stock solution with deionized water.
PS-GMA particles (55% cross-linking degree) were prepared in our laboratory following a method from a previous work [22]. Methanol of HPLC-grade
Characterization
The morphology of PS-GMA and COF@PS-GMA nanoparticles were investigated with SEM. As shown in Fig. 3, the PS-GMA particles are porous spheres with a size around 6 μm. The cladding of COF layers not only significantly changed the colour of the particles, but also caused a great inversion of their porous surface nature. According to the results of element analysis (Table S1), PS-GMA has no nitrogen, but COF@PS-GMA has 0.41% nitrogen. Furthermore, compared with PS-GMA, increased absorption at 3450
Conclusion
In summary, a novel covalent organic framework (COF) functionalized poly (styrene-divinyl benzene-glycidylmethacrylate) composite was successfully constructed. The prepared composite inherits a porous structure, high surface area and favorable chemical stability. Because of the π-π stacking interactions, the COF@PS-GMA was employed as the SPE sorbent for the rapid concentration of NSAIDs in the wastewater samples. Parameters related to the in-syringe SPE were systematically studied. Under
Acknowledgements
The financial supported by Zhejiang Provincial Natural Science Foundation of China (Nos. LZ16B050001, LY15B050001), Key Laboratory of Health Risk Appraisal for Trace Toxic Chemicals of Zhejiang Province.
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2022, Journal of Chromatography ACitation Excerpt :However, in addition to silica and polymer microspheres, carbon nanomaterials [26] and magnetic materials [27] with high specific surface area and special functions are also favored as the substrates for SPE fillers. Based on these substrates, organic macromolecular [28–31], biomacromolecular [32], and other special functional materials (including ionic liquid, metal organic frameworks and covalent organic frameworks) [27,33–35] have been utilized for the surface modification. Abundant functional groups have been introduced by these materials and the proposed separation materials exhibited satisfactory performance in analytical chemistry (Table 1) [36–38].