2016
DOI: 10.1002/jssc.201600231
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Magnetic solid‐phase extraction based on a polydopamine‐coated Fe3O4 nanoparticles absorbent for the determination of bisphenol A, tetrabromobisphenol A, 2,4,6‐tribromophenol, and (S)‐1,1’‐bi‐2‐naphthol in environmental waters by HPLC

Abstract: Polydopamine-coated Fe3 O4 magnetic nanoparticles synthesized through a facile solvothermal reaction and the self-polymerization of dopamine have been employed as a magnetic solid-phase extraction sorbent to enrich four phenolic compounds, bisphenol A, tetrabromobisphenol A, (S)-1,1'-bi-2-naphthol and 2,4,6-tribromophenol, from environmental waters followed by high-performance liquid chromatographic detection. Various parameters of the extraction were optimized, including the pH of the sample matrix, the amoun… Show more

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Cited by 36 publications
(12 citation statements)
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“…To fabricate the miniaturized calix [4]arene-GO/PDA-CFs adsorbent, the CFs were cut into small lengths (0.20 cm). Subsequently, the PDA was coated on the surface of CFs via self-polymerization [28]. Briefly, dopamine hydrochloride (180 mg) was dissolved in 100 mL of 0.010 M tris buffer (pH 8.5), and the CFs were added to the solution and stirred at 500 rpm for 4 h at 27 ± 1 • C. Meanwhile, the calix [4]arene-GO was synthesized by adapting previous methods [29].…”
Section: Preparation Of Calix[4]arene-go/pda-coated Cfs Adsorbentmentioning
confidence: 99%
“…To fabricate the miniaturized calix [4]arene-GO/PDA-CFs adsorbent, the CFs were cut into small lengths (0.20 cm). Subsequently, the PDA was coated on the surface of CFs via self-polymerization [28]. Briefly, dopamine hydrochloride (180 mg) was dissolved in 100 mL of 0.010 M tris buffer (pH 8.5), and the CFs were added to the solution and stirred at 500 rpm for 4 h at 27 ± 1 • C. Meanwhile, the calix [4]arene-GO was synthesized by adapting previous methods [29].…”
Section: Preparation Of Calix[4]arene-go/pda-coated Cfs Adsorbentmentioning
confidence: 99%
“…As a consequence, studies on MSPE have devoted efforts to design and screen magnetic adsorbent materials with high extraction performance towards target pollutants. Furthermore, many functional materials, such as Fe 3 O 4 /cobalt(II)‐based metal‐organic nanotubes (Fe 3 O 4 /Co‐MONT), Cd(II)‐ion imprinted magnetic mesoporous silica material, octadecyl‐functionalized monodispersed magnetic ferrite microspheres, Fe 3 O 4 /3‐(trimethoxysilyl)propyl methacrylate/ionic liquid nanoparticles, zeolitic imida zolate framework‐8 (ZIF‐8), Fe 3 O 4 /metal‐organic framework (Fe 3 O 4 /MOF), Fe 3 O 4 /SiO 2 /UiO‐66 microspheres, and polydopamine‐coated magnetic Fe 3 O 4 composites (Fe 3 O 4 @PDA) , have been successfully used in the MSPE of various environmental pollutants.…”
Section: Introductionmentioning
confidence: 99%
“…As a consequence, studies on MSPE have devoted efforts to design and screen magnetic adsorbent materials with high extraction performance towards target pollutants. Furthermore, many functional materials, such as Fe 3 [5,[9][10][11][12][13][14][15], have been successfully used in the MSPE of various environmental pollutants.…”
Section: Introductionmentioning
confidence: 99%
“…Magnetic adsorbents play an important role in the MSPE of various analytes, causing many researchers to focus on exploring novel MSPE adsorbents . Multiple magnetic materials have been used to extract trace bisphenols from environmental water samples, such as Fe 3 O 4 /graphene quantum dots (Fe 3 O 4 /GQDs) magnetic nanocomposite , iron‐ferric oxide/graphene oxide composite (Fe@Fe 2 O 3 /GO) , polydopamine‐coated magnetic Fe 3 O 4 composites (Fe 3 O 4 @PDA) , and ionic liquid (IL) coated magnetic Fe 3 O 4 nanoparticles (NPs) . However, the most magnetic sorbents are based on iron oxides that are vulnerable under acidic conditions.…”
Section: Introductionmentioning
confidence: 99%