Abstract

Magnetite (Fe3O4) is a ferromagnetic iron oxide of both Fe(II) and Fe(III), prepared by FeCl2 and FeCl3. XRD was used for the confirmation of Fe3O4. Via the modification of Tetraethyl orthosilicate (TEOS), (3-Aminopropyl)trimethoxysilane (APTMS), and Alginate (AA), Fe3O4@SiO2, Fe3O4@SiO2-NH2, and Fe3O4@SiO2-NH2-AA nanoparticles could be obtained, and IR and SEM were used for the characterizations. Alkaloid adsorption experiments exhibited that, as for Palmatine and Berberine, the most adsorption could be obtained at pH 8 when the adsorption time was 6 min. The adsorption percentage of Palmatine was 22.2%, and the adsorption percentage of Berberine was 23.6% at pH 8. Considering the effect of adsorption time on liquid phase system, the adsorption conditions of 8 min has been chosen when pH 7 was used. The adsorption percentage of Palmatine was 8.67%, and the adsorption percentage of Berberine was 7.25%. Considering the above conditions, pH 8 and the adsorption time of 8min could be chosen for further uses.

Highlights

  • There are many pure phases of iron oxide in nature, the most popular magnetic nanoparticles (MNPs) are the nanoscale zero-valent iron, Fe3 O4 and γ-Fe2 O3

  • Fe3 O4 @SiO2 composite nanoparticles have the desirable properties of magnetic nanoparticles while benefiting from the SiO2 shell, such as good hydrophilicity, stability, and biocompatibility [6,7,8]

  • In 2016, Tang reported that (3-aminopropyl)-triethoxysilane (APTES) was used as surface modification reagents to get Fe3 O4 @SiO2 -NH2, which could be used for selective removal of Zn(II) ions from wastewater [9]

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Summary

Introduction

There are many pure phases of iron oxide in nature, the most popular magnetic nanoparticles (MNPs) are the nanoscale zero-valent iron (nZVI), Fe3 O4 and γ-Fe2 O3. In 2001, Asher reported co-precipitation method using oleic acid as the surface modification agent to obtain Fe3 O4 nanoparticles (2–15 nm) [2]. In 2016, Tang reported that (3-aminopropyl)-triethoxysilane (APTES) was used as surface modification reagents to get Fe3 O4 @SiO2 -NH2 , which could be used for selective removal of Zn(II) ions from wastewater [9]. While Fe3 O4 @SiO2 -NH2 nanoparticles could be modified to obtain mercaptoamine-functionalised silica-coated magnetic nanoparticles for the removal of mercury and lead ions from wastewater [10]. As for the removal of ions, arsenate removal could be achieved by calcium alginate-encapsulated magnetic sorbent, which was prepared by physical method [11]. In order to investigate the effects of the covalent alginate-modified method, alkaloid adsorption experiments were designed to study the properties of alginate-modified Fe3 O4 @SiO2 -NH2 nanoparticles

Experimental Section
Preparation of Fe3 O4 Nanoparticles
Preparation
Preparation of Fe33O
Preparation of Calibration Standards
Influence
Influence from Adsorption Time
XRD Analysis of Fe3 O4 Nanoparticles
SEM Figure
Analysis of Alkaloid Adsorption Test
Conclusions

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