10.1007/s40097-019-0303-z

Synthesis of SDS micelles-coated Fe3O4/SiO2 magnetic nanoparticles as an excellent adsorbent for facile removal and concentration of crystal violet from natural water samples

  1. Department of Chemistry, Shahr-e-Qods Branch, Islamic Azad University, Tehran, IR
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Published in Issue 22-05-2019

How to Cite

Maleki, S., Falaki, F., & Karimi, M. (2019). Synthesis of SDS micelles-coated Fe3O4/SiO2 magnetic nanoparticles as an excellent adsorbent for facile removal and concentration of crystal violet from natural water samples. Journal of Nanostructure in Chemistry, 9(2 (June 2019). https://doi.org/10.1007/s40097-019-0303-z

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Abstract

Abstract In this research, a simple and rapid method for the separation and preconcentration of trace amounts of crystal violet (CV) from aqueous sample solutions by modified magnetic nano-particles (MNPs) has been developed. The modification of magnetite nanoparticles was conducted by tetra ethoxysilane (TEOS) followed by micelles of anionic surfactant (SDS) to enhance the preconcentration of CV. To characterize the shape and structure of the nanoadsorbent, FT-IR and XRD procedures were used. Also, the average size of the synthesized nanoparticles was achieved between 30 and 40 nm by TEM technique. The effects of some important parameters such as: aqueous solution pH, adsorbent dosage, contact time, temperature and desorption conditions on the separation and concentration of CV were investigated. So, under optimal experimental conditions: aqueous solution pH 6, solution temperature = 20 °C, 7 mg of adsorbent, 1 mL of eluent (0.8 mL of acetonitrile + 0.2 mL of acetic acid), the recovery of CV from river water samples was achieved 98.32 ± 0.056% ( n  = 5) in two short periods of time for extraction (5 min) and elution (2 min). The maximum sorption capacity of the nano-composite was determined to be 16.37 mg/g. Also linear dynamic range and limit of detection were calculated to be 10–2500 ppb and 1.82 ppb, respectively. Finally, the proposed method was successfully applied for the separation and concentration of CV from the real water samples and the results were satisfied. Graphical abstract Under optimal conditions, a significant amount of nanocomposite was added to the dye solution. After dye removal in a short time, the nanoadsorbent-containing dye was magnetically separated from the solution and then the adsorbed dye was eluted into low volume of a suitable eluting solution.

Keywords

  • Crystal violet,
  • Fast removal, SDS micelle-coated MNP,
  • Concentration,
  • Magnetic nanoparticles

References

  1. Crini (2006) Non-conventional low-cost adsorbents for dye removal: a review (pp. 1061-1085) https://doi.org/10.1016/j.biortech.2005.05.001
  2. Šafařı́k and Šafařı́ková (2002) Detection of low concentrations of malachite green and crystal violet in water (pp. 196-200) https://doi.org/10.1016/S0043-1354(01)00243-3
  3. Sharma et al. (2019) Efficient capture of eosin yellow and crystal violet with high performance xanthan-acacia hybrid super-adsorbent optimized using response surface methodology (pp. 314-323) https://doi.org/10.1016/j.colsurfb.2018.12.017
  4. Otero et al. (2003) Elimination of organic water pollutants using adsorbents obtained from sewage sludge (pp. 55-65) https://doi.org/10.1016/S0143-7208(03)00005-6
  5. Sadeghi and Nasehi (2018) Simultaneous determination of brilliant green and crystal violet dyes in fish and water samples with dispersive liquid–liquid micro-extraction using ionic liquid followed by zero crossing first derivative spectrophotometric analysis method (pp. 134-142) https://doi.org/10.1016/j.saa.2018.04.061
  6. An et al. (2010) Simultaneous spectrophotometric determination of trace amount of malachite green and crystal violet in water after cloud point extraction using partial least squares regression (pp. 883-888) https://doi.org/10.1016/j.jhazmat.2009.10.092
  7. Al-Degs and Sweileh (2012) Simultaneous determination of five commercial cationic dyes in stream waters using diatomite solid-phase extractant and multivariate calibration (pp. 219-224) https://doi.org/10.1016/j.arabjc.2010.08.016
  8. Manzo et al. (2013) Determination of crystal violet in water by direct solid phase spectrophotometry after rotating disk sorptive extraction (pp. 305-308) https://doi.org/10.1016/j.talanta.2012.11.004
  9. Korn et al. (2006) Separation and preconcentration procedures for the determination of lead using spectrometric techniques: a review (pp. 16-24) https://doi.org/10.1016/j.talanta.2005.10.043
  10. Tian et al. (2009) Solid-phase extraction of tanshinones from Salvia Miltiorrhiza Bunge using ionic liquid modified silica sorbents (pp. 738-742) https://doi.org/10.1016/j.jchromb.2009.02.012
  11. Falaki and Fakhri (2013) Study of the adsorption of methyl orange from aqueous solution using nickel oxide nanoparticles: equilibrium and kinetics studies 10(2) (pp. 117-124)
  12. Falaki and Fakhri (2014) Adsorption properties of nickel oxide nanoparticles for removal of congo red from aqueous solution 10(4) (pp. 255-262)
  13. Helmi et al. (2017) Highly facile removal of acid red 88 from aqueous samples by using synthesized iron oxide magnetic nanoparticles and 1-butyl-3-methylimidazolium tetrachloroferrate magnetic ionic liquid (pp. 331-340) https://doi.org/10.5004/dwt.2017.21321
  14. Zhao et al. (2008) Cetyltrimethylammonium bromide-coated magnetic nanoparticles for the preconcentration of phenolic compounds from environmental water samples (pp. 1201-1206) https://doi.org/10.1021/es071817w
  15. Faraji et al. (2010) Magnetic nanoparticles: synthesis, stabilization, functionalization, characterization, and applications https://doi.org/10.1007/BF03245856
  16. Falaki and Berijani (2016) Aspartic acid-modified magnetic nanoparticles as an ideal sorbent for solid phase extraction of Pb in water samples prior to ICP-OES determination (pp. 25765-25772) https://doi.org/10.1080/19443994.2016.1157706
  17. Zhang et al. (2006) Synthesis of novel porous magnetic silica microspheres as adsorbents for isolation of genomic DNA (pp. 514-518) https://doi.org/10.1021/bp050400w
  18. Zhu et al. (2010) Mixed hemimicelles SPE based on CTAB-coated Fe3O4/SiO2 NPs for the determination of herbal bioactive constituents from biological samples (pp. 1873-1880) https://doi.org/10.1016/j.talanta.2009.10.037
  19. Ezoddin et al. (2010) Application of modified nano-alumina as a solid phase extraction sorbent for the preconcentration of Cd and Pb in water and herbal samples prior to flame atomic absorption spectrometry determination (pp. 900-905) https://doi.org/10.1016/j.jhazmat.2010.02.023
  20. Keyhanian et al. (2016) Magnetite nanoparticles with surface modification for removal of methyl violet from aqueous solutions (pp. S348-S354) https://doi.org/10.1016/j.arabjc.2011.04.012
  21. Davudabadi Farahani and Shemirani (2014) Mixed hemi-micelle solid-phase extraction based on modified magnetic nanoparticles for extraction of cadmium and lead from food and water samples 97(6) (pp. 1682-1688) https://doi.org/10.5740/jaoacint.12-407
  22. Suyanta, Kunarti, E.S., Muzakir, M., Pertiwi, C., Pertiwi, D.: Comparative study of methods in the synthesis of magnetite (Fe
  23. 3
  24. O
  25. 4
  26. ). In: Proceedings of the International Conference on Research. Implementation and Education of Mathematics And Sciences 2014, Yogyakarta State University, pp. 18–20 (2014)
  27. Ramimoghadam et al. (2012) The effect of sodium dodecyl sulfate (SDS) and cetyltrimethylammonium bromide (CTAB) on the properties of ZnO synthesized by hydrothermal method (pp. 13275-13293) https://doi.org/10.3390/ijms131013275
  28. Sharma et al. (2019) Response surface methodology directed synthesis of luminescent nanocomposite hydrogel for trapping anionic dyes (pp. 380-390) https://doi.org/10.1016/j.jenvman.2018.10.038
  29. Bhalla et al. (2019) One-pot green synthesis of polymeric nanocomposite: biodegradation studies and application in sorption-degradation of organic pollutants (pp. 345-356) https://doi.org/10.1016/j.jenvman.2018.12.117
  30. Sun et al. (2017) Application and mechanism of anionic collector sodium dodecyl sulfate (SDS) in phosphate beneficiation 7(29) (pp. 1-13)
  31. Bavili Tabrizi and Dehghani Teymurlouie (2016) Application of sodium dodecyl sulfate coated iron oxide magnetic nanoparticles for the extraction and spectrofluorimetric determination of propranolol in different biological samples (pp. 108-116)
  32. Rahman (1983) Effect of pH on the critical micelle concentration of sodium dodecyl sulphate (pp. 1331-1334) https://doi.org/10.1002/app.1983.070280407
  33. Esmaeili-Shahri and Es’haghi (2015) Superparamagnetic Fe3O4@SiO2 core–shell composite nanoparticles for the mixed hemimicelle solid-phase extraction of benzodiazepines from hair and wastewater samples before high-performance liquid chromatography analysis (pp. 4095-4104) https://doi.org/10.1002/jssc.201500743
  34. Shariati et al. (2011) Fe3O4 magnetic nanoparticles modified with sodium dodecyl sulfate for removal of safranin O dye from aqueous solutions (pp. 160-165) https://doi.org/10.1016/j.desal.2010.11.040
  35. Ghanbari Adivi et al. (2019) Agarose-coated Fe3O4@SiO2 magnetic nanoparticles modified with sodium dodecyl sulfate, a new promising sorbent for fast adsorption/desorption of cationic drugs 75(3) (pp. 1239-1256) https://doi.org/10.1007/s00289-018-2418-7
  36. Bagheri et al. (2012) Extraction of fluoxetine from aquatic and urine samples using sodium dodecyl sulfate-coated iron oxide magnetic nanoparticles followed by spectrofluorimetric determination (pp. 61-65) https://doi.org/10.1016/j.aca.2011.10.033
  37. Tavakoli et al. (2014) Magnetic mixed hemimicelles solid-phase extraction of three food colorants from real samples (pp. 100-108) https://doi.org/10.1007/s12161-013-9603-y
  38. Dehghan Noudeh et al. (2007) The effect of temperature on thermodynamic parameters of micellization of some surfactants (pp. 47-52) https://doi.org/10.3923/jas.2007.47.52
  39. Zhao et al. (2008) Preparation of silica-magnetite nanoparticle mixed hemimicelle sorbents for extraction of several typical phenolic compounds from environmental water samples (pp. 140-147) https://doi.org/10.1016/j.chroma.2008.02.069
  40. Sharma et al. (2019) Selective removal of cationic dyes using response surface methodology optimized gum acacia sodium alginate blended superadsorbent (pp. 331-345) https://doi.org/10.1016/j.ijbiomac.2018.11.213
  41. Azarkohan, A., Shemirani, F., Alvand, M.: Fast analysis of water samples for trace amount of crystal violet dye based on solid phase extraction using nanoporous SBA-3 prior to determination by fiber optic-linear array detection spectrophotometry. J. Chem. (accepted 28 Oct 2013)
  42. Razi-Asrami et al. (2017) Simultaneous spectrophotometric determination of crystal violet and malachite green in water samples using partial least squares regression and central composite design after preconcentration by dispersive solid-phase extraction https://doi.org/10.1007/s10661-017-5898-2