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International Journal of Inorganic Chemistry
Volume 2012 (2012), Article ID 439751, 7 pages
http://dx.doi.org/10.1155/2012/439751
Research Article

Synthesis and Characterization of Functionalized Magnetic Nanoparticles for the Detection of Pesticide

1School of Material Science, Japan Advanced Institute of Science and Technology, 1-1 Asahidai, Nomi City, Ishikawa 923-1292, Japan
2Department of Physics, Graduate School of Engineering, Yokohama National University, 79-5 Tokiwadai, Hodogaya-ku,Yokohama 240-8501, Japan
3Department of Food Science, Faculty of Bioresources and Environmental Sciences, Ishikawa Prefectural University, 1-308 Suematsu, Nonoichi, Ishikawa 921-8836, Japan

Received 13 February 2012; Accepted 9 April 2012

Academic Editor: Liane M. Rossi

Copyright © 2012 Shu Taira et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract

We synthesized magnetic nanoparticles (MNPs) by mixing aqueous solutions of 3d transition metal chlorides ( ) and a sodium metasilicate nonahydrate ( ) in order to produce monodispersed MNPs in a single step. The particle size can be controlled by adjusting the annealing temperature. We characterized the MNPs by X-ray diffraction (XRD), superconducting quantum interference device (SQUID), transmission electron microscopy (TEM), Fourier transform infrared (FT-IR), and zeta-potential measurement. Paramagnetic and superparamagnetic behaviors were found for the obtained samples depending on the particle size (  nm). The synthesized MNPs could be modified with the amino-, phenyl-, and carboxy- groups on MNPs' surface by silanization procedure, respectively. The purpose of functionalizing the surface of the nanoscale magnetic particles was to realize subsequent capture and detection with desired other molecules by nanoparticle assisted laser ionization/desorption mass spectrometry.

1. Introduction

Nanoscale magnetic particles have attracted much attention because they are able to be transported to targeted locations [14] by means of an external magnetic field as well as to be used for data storage [5] and magnetic resonance imaging [6, 7].

Synthesis methods of magnetic nanoparticles (MNPs) have been developed for composing various kinds of MNPs and controlling the sizes in the range of 1–100 nm [810]. Coprecipitation method is the most convenient way to synthesize MNPs from metal chloride solution (i.e., iron, manganese, nickel, etc.) by the addition of base solution. MNPs are precipitated under optimum temperature, pH, and ionic strength [1113] due to solubility change.

Nanometer-scale spheres show very interesting characteristic phenomena such as quantum size effect or magnetic quantum tunneling and have intrinsic instability over longer haul for the morphology. To stabilize MNP character, chemical coating on naked MNP surface was developed [1416]. For example, MNP with 10–20 nm can be stabilized in 2-aminoethanethiol (0.5 M) [14]. Polymer or surfactant coating is also used to protect the MNP configuration and avoid aggregation [1721]. These techniques can be applied to protection of MNP morphology although we should pay attention to synthesis conditions under the complicated method.

We have developed a method for synthesizing MNPs by mixing aqueous solutions of 3d transition metal chlorides (MCL2·nH2O) and a sodium metasilicate nonahydrate (Na2SiO3·9H2O) to obtain monodispersed and bite-sized MNPs in a single step. The particle size depended on the annealing temperature and time [11, 12]. MNPs prepared by this method were surrounded by amorphous SiO2, so we can prevent them from aggregation and degradation. Besides, Si ions are located on the surface, therefore, the optional functional group can be modified on MNP surface by silanization procedure [2]. Modification and coating on MNP surface does not only perform to protect MNP morphology but also serve to use functionalization with objective components, such as drug [22], enzyme [23], and amino acid [24]. It is possible that various functional groups are modified (i.e., phenyl [25], thiol [24], fluorine, chlorine, etc.) on the MNP by the silanization method.

In this research, we functionalized MNPs by the (3-aminopropyl)triethoxysilane (γ-APTES), phenyltriethoxysilane (PTES) or triethoxysilylpropyl succinic anhydride (TESPSA) to modify with amino- [2], phenyl- [26], and carboxy- [27] groups on the MNP’s surface. Moreover, MNPs can be applied to analytical field. From recent advances in mass spectrometry, it is well known that nanoparticles with metal oxide cores can ionize the molecule for the laser desorption/ionization (LDI) of analytes in mass spectrometry (MS) [28]. Functionalized MNPs also serve as an ionization-assisting material in nanoparticle-assisted laser desorption/ionization (nano-PALDI) MS, which gives no background peaks. Therefore, Nano-PALDI MS can be used in analysis of various compounds such as metabolite, drug, and oligonucleotide [2931]. Especially, phenyl group-modified (Ph-) MNPs have demonstrated the capture and ionization of target analyte by chemointeraction [26]. In this context, we investigated Ph-MNPs for the ability of recovery and detection of pesticide as a novel application for agricultural science.

2. Material and Methods

2.1. Synthesis and Characterization of Magnetic Nanoparticles with Precipitation of Wet Process Method

We developed simple preparation method of MNP. The γ-Fe2O3 MNPs surrounded by amorphous SiO2 (a-SiO2) were prepared by mixing aqueous solutions of FeCl2·4H2O (WAKO Pure Chemicals Japan) and Na2SiO3·9H2O (JUNSEI Chemical Japan). FeCl2·4H2O (10 mM) and Na2SiO3·9H2O (10 mM) were each dissolved in 500 mL of distilled water, and the two solutions were mixed. After 10 minutes of stirring, the resulting precipitates were washed several times with distilled water and dried at 353 K in a water bath. The dried samples were crushed in a porcelain mortar and then annealed in air for 6 hours at 873 K or 973 K in a furnace.

2.2. Functionalization of MNPs by Silanization Method

In this time, we prepared three types of functionalized MNPs with (i) amino, (ii) phenyl or, (iii) carboxy groups (Figure 1(a)). For each functionalization, the (3-aminopropyl)triethoxysilane (γ-APTES), phenyltriethoxysilane (PTES) or triethoxysilylpropyl succinic anhydride (TESPSA) solution was added to the solid γ-Fe2O3 MNPs, respectively. The reaction mixture was stirred at 298 K for 10 minutes and then heated to 403 or 298 K. Three or six hours after the mixture was cooled to room temperature, it was washed three times with ultrapure water (≥18.2 Ω, Milli-Q SP, Millipore Co.) and ethanol, then dried at 350 K.

fig1
Figure 1: Schematic illustration of functionalization of magnetic nanoparticle by silanization procedure (a) and the capture and ionization of target pesticide by phenyl group-modified magnetic nanoparticle (b).

Fourier transform infrared (FT-IR) spectra were observed to confirm the modification of functional groups, respectively, even after washing the samples several times to remove physisorbed organic molecules. Zeta potential was also measured using a Zetasizer Nano ZS (Malvern, UK) for recognition. Before and after the modification, each sample was examined by CuKα X-ray powder diffraction (XRD) (λ = 0.154 nm). DC magnetization was measured using a superconducting quantum interference device (SQUID) magnetometer (Quantum Design, MPMS) under a ± 40-kOe magnetic field; the magnetization measurements were performed at temperatures ranging from 5 to 300 K. The morphology of the MNPs was investigated by transmission electron microscopy (TEM; H-7100, Hitachi, Japan).

2.3. Capture and Analysis of Pesticide Samples by Phenyl Group-Modified MNPs

In the capture and analysis experiments, pyriminobac methyl (Methyl 2-(4,6-dimethoxy-2-pyrimidinyloxy)-6-(1-methoxyiminoethyl) benzoate; : 361.3) that is chemical herbicides of pesticide was used as aromatic samples (Figure 1(b)). The Phenyl group-modified (Ph-) MNPs (1 mg) were suspended in 150 μL of 70% methanol containing 10 ppm of pyriminobac methyl, and this suspension was stirred for 5 min. After recovery of the Ph-MNP’s suspension by an external magnetic force of permanent magnet, the supernatant was discarded. The precipitate particles were resuspended in 1 mL of 70% methanol as a washing procedure, and this suspension was stirred for 1 min. The Ph-MNP’s precipitation was again recovered by external magnetic force, and the supernatant was discarded. The Ph-MNPs suspension was evaluated by MS to confirm the existence of the target pesticide on the Ph-MNP through π-π interaction. The 1 μL of suspension of sample and Ph-MNPs were dropped on target plates with a pipette.

The usefulness of the MNPs for their trapping ability and as an ionization-assisting material in MS was confirmed by a matrix-assisted laser desorption/ionization (MALDI) time of flight (TOF) instrument (Voyager-DE-RP; Applied Biosystems, Germany) equipped with a nitrogen laser emitting at 337 nm. The analyte surface was irradiated with 100 laser shots in the positive ion detection mode. As a control, the same procedure was conducted using the original unfunctionalized MNPs.

3. Results

3.1. Physical Characterization of Original Nanoparticles

The XRD pattern of the iron-based MNP indicated the spinel γ-Fe2O3 structure. The broad peaks at 2θ = 35 and 60 degrees were confirmed to be the (311) reflection and the (440) reflection of γ-Fe2O3. The peak below 2θ = 30 degrees was determined to have originated from amorphous SiO2 (Figure 2(a)) [10].

fig2
Figure 2: The CuKα X-ray powder diffraction pattern (a), FT-IR spectrum, M-H curves for annealing temperature at 873 K (c) or 973 K (d), and TEM images of original magnetic nanoparticle for annealing temperature at 873 K (e) or 973 K (f), respectively.

FT-IR analysis exhibited the presence of Si–O (1100–900 cm−1) and O–H (3400–3100 cm−1) bonding as chemical bonds on the surface of the MNPs (Figure 2(b)).

The results of magnetization indicated different property by annealing temperature. In the case of the annealing temperature at 873 K, the magnetization of the iron-based MNPs increased linearly with increasing magnetic field; that is, the particle showed paramagnetism at 300 K (Figure 2(c)). In the case of the annealing temperature at 973 K, superparamagnetic behavior was shown with sigmoid curve at 300 K (Figure 2(d)). These MNPs precipitates could be easily attracted from water solution by means of an external magnetic field.

TEM images of the MNPs were shown (Figures 2(e) and 2(f)). Obtained images exhibited that the MNPs did not aggregate but disperse. The iron-based nanoparticles which were annealed at 873 K showed small groups for both the primary particle diameters (  nm) (mean ± SEM; ) (Figure 2(e)). The diameter of the iron-based nanoparticles which were annealed at 973 K was measured to be  nm (mean ± SEM; ) (Figure 2(f)). A significant difference was observed between these two iron-based MNPs ( with unpaired -test), indicating that the particle sizes were controlled through the annealing temperatures. Interestingly, the annealing temperature affected magnetization property. The property of paramagnetism changed to superparamagnetism, which indicated that magnetism value increased 6 times.

3.2. Physical Characterization of Functionalized MNP

The modification of basic functional group such as amino, phenyl and carboxy groups is important because these groups can be used to bind various reagents by covalent bond or chemical interaction. FT-IR spectra indicated the existence of these functional groups on MNP, respectively. For the amino groups on the MNP, the presence of N–H (1,640–1,540 cm−1), C–H (3,000–2,830 cm−1) and O–H (3,400–3,100 cm−1) bonding as chemical bonds on the surface of the MNPs was confirmed (Figure 3(a)). In the case of phenyl-group modified MNPs, the corresponding signal for the aromatic ring of PTES was observed for the C–C ring (1,430 and 1,390 cm−1), CH3 stretch (2,915–2,870 cm−1) and the C–H ring stretch (3,050–3,000 cm−1) on the MNP surface, even after multiple washings of the samples in order to remove excess organic molecules. The broad peak of O–H (3,400–3,100 cm−1) bonding was disappeared due to modification of PTES (Figure 3(b)). For carboxy groups, typical C=O peaks (1,600 and 1,700 cm−1), C–H peaks (3,000–2,830 and 1,400 cm−1) and O–H (3,400–3,100 cm−1) were detected for the first time in the spectrum of the functionalized particles, respectively (Figure 3(c)), whereas only the O–H (3,400–3,100 cm−1) peak was observed in the spectrum of the original MNPs (Figure 3(d)). An Si–O (1,100–900 cm−1) peak still remained from all functionalized MNPs.

439751.fig.003
Figure 3: FT-IR spectra of amino- (a), phenyl- (b), carboxy-group modified (c), and original (d) magnetic nanoparticles, respectively.

The zeta-potentials of the nanoparticles were measured by a Zetasizer using the laser Doppler velocimetry technique. For amino group-modified MNP, an isoelectric point was found for ~pH 9.8 (Inverted black triangle points in Figure 4). The nanoparticles showed positive charge in <pH 10. This indicated that NH2 groups on nanoparticle’s surface transformed into group. The zeta potential was more than +30 mV that was considered as the threshold value for electrostatic stabilization [32].

439751.fig.004
Figure 4: Zeta potential of amino- (), phenyl- (), original (▪), and carboxy-group modified (∘) magnetic nanoparticles, respectively.

In the case of phenyl group-modified MNPs (Ph-MNPs) (White triangle points in Figure 4), the MNPs showed negative charges at pH 3.0–11.0. The zeta potential of the Ph-MNPs was less negative than that of the original MNPs (White circle points in Figure 4), which indicated that the phenyl groups decreased the effect of the OH group on the MNP surface. Black square points in Figure 4 showed a plot of the zeta potential of the carboxyl groups modified MNP. From this measurement, negative charges on the surface were confirmed. It appears that carboxyl groups maintain the equilibrium position between COOH and COO + H+ in solution, and the equilibrium shifts to the right at higher pH values. These functionalized particles tend to show a negative potential as the pH value increases. Thus the modification with functional groups on magnetic nanoparticles was succesful. The amino- or carboxyl-modified functionalized nanoparticles can electrostatically or covalently conjugate to other molecules such as drugs and biomolecules and they improve hydrophilic properties of the nanoparticles. As a result, biocompatibility is expected.

For the phenyl group-modified MNP (Ph-MNP), we could capture the desired molecule chemical interaction. In the previous report, we have successfully achieved selective trapping and detection of aromatic molecules by π-π interaction [26]. In this time, we investigated whether the pyriminobac methyl as (Figure 5(a)) pesticide is captured and detected by Ph-MNP. We could successfully recover Ph-MNP by an external magnetic force. After a washing procedure, protonated (m/z 362.3), sodium adducted (m/z 384.3), and potassium adducted (m/z 400.0) form of pyriminobac methyl were detected, respectively (Figure 5(b)). On the contrast, in the case of the original MNP, no signal was observed (Figure 5(c)). The main body of pyriminobac methyl constitutes aromatic structure. Thus, this result indicated that this Ph-MNP possesses the ability of pesticide capturing after washing due to π-π interaction between phenyl groups on MNP’s surface and pesticide.

439751.fig.005
Figure 5: Chemical structure of pyriminobac methyl as pesticide (a), nano-PALDI mass spectra of pyriminobac methyl with phenyl group-modified magnetic nanoparticle (b), or original magnetic nanoparticle (c).

4. Conclusion

γ-Fe2O3 MNPs surrounded by amorphous SiO2 were prepared by the wet chemical method. The obtained MNP’s magnetization property and diameter were increased with increasing annealing temperature. Functionalization of MNP by the silanization method could provide amino, phenyl and carboxy group-modified MNPs. Functional phenyl group-modified MNP could capture aromatic molecule such as one of pesticides and could be employed in investigation of pesticide residue from agricultural products and land in the next work.

Acknowledgments

The authors thank Professor M. Takagi, Professor K. Ebitani, and Professor Y. Takamura, for providing technical assistance and advice. This research was supported by a WAKATE-B grant from the Japan Society for the Promotion of Science to S. Taira, a Grant-in-Aid to S. Taira from Kinki Innovation Center Japan and from Mitani Foundation for R&D.

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