Figures
Abstract
Carboxymethyl α-cyclodextrin immobilized Fe3O4 magnetic nanoparticles (CM-α-CD-Fe3O4) were synthesized for the selectively adsorptive extraction of five phenylarsonic acids including p-amino phenylarsonic acid, p-nitro phenylarsonic acid, p-hydroxy phenylarsonic acid, p-acylamino phenylarsonic acid and p-hydroxy-3-nitro phenylarsonic acid in chicken tissue. Using ultra performance liquid chromatography coupled with tandem mass spectrometry (UPLC-MS/MS), a highly sensitive analytical method was proposed for the determination of five phenylarsonic acids. It was shown that CM-α-CD-Fe3O4 could extract the five phenylarsonic acids in complex chicken tissue samples with high extraction efficiency. Under the optimal conditions, a high enrichment factor, ranging from 349 to 606 fold, was obtained. The limits of detection (LODs) (at a signal-to-noise ratio of 3) were in the range of 0.05–0.11 µg/kg for the five phenylarsonic acids. The proposed method was applied for the determination of five target phenylarsonic acids in chicken muscle and liver samples. Recoveries for the spiked samples with 0.2 µg/kg, 2.0 µg/kg and 20 µg/kg of each phenylarsonic acids were in the range of 77.2%–110.2%, with a relative standard deviation (RSD) of less than 12.5%.
Citation: Jia J, Zhang W, Wang J, Wang P, Zhu R (2014) Selectively Adsorptive Extraction of Phenylarsonic Acids in Chicken Tissue by Carboxymethyl α-Cyclodextrin Immobilized Fe3O4 Magnetic Nanoparticles Followed Ultra Performance Liquid Chromatography Coupled Tandem Mass Spectrometry Detection. PLoS ONE 9(9): e107147. https://doi.org/10.1371/journal.pone.0107147
Editor: Bing Xu, Brandeis University, United States of America
Received: April 14, 2014; Accepted: August 9, 2014; Published: September 12, 2014
Copyright: © 2014 Jia et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: The authors confirm that all data underlying the findings are fully available without restriction. All relevant data are within the paper and its Supporting Information files.
Funding: The authors would like to thank the NSFC (No. 31201832), Special Fund for Agro-scientific Research in the Public Interest (No. 201203094), and National International cooperation program (No. 2012DFA31140) for financially supporting this research. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
Introduction
4-Hydroxy-3-nitrobenzenearsonic acid, also known as roxarsone (ROX), has been used since 1944 as a feed additive in the poultry industry to promote growth and to control coccidiosis, a parasitic disease that infects the intestinal tract of poultry [1]. Besides ROX, some other organic arsenic compounds, including p-amino phenylarsonic acid (p-APAA), p-nitro phenylarsonic acid (p-NPAA), p-hydroxy phenylarsonic acid (p-HPAA) and p-acylamino phenylarsonic acid (AAPAA) (Fig. 1) have been successively employed for the same purposes. Their slight structural difference, i. e. different substituent groups on the aromatic ring, results in different growth-promoting and disease-controlling effects [2]. Phenylarsonic acids have been approved as feed additives by many countries at levels of 25–50 mg/kg [3]. Recent studies showed that phenylarsonic acids in the environment might be converted into elemental arsenic and other inorganic arsenic compounds, which are known to be strongly carcinogenic [4]. Some countries in EU strictly control the use of phenylarsonic acid additives, while in the U.S., Tyson Foods, the country's largest poultry producer, stopped the use of arsenic compounds in 2004. After the release of 2011 FDA report of elevated inorganic arsenic in the livers of chickens treated with ROX, Pfizer Animal Health, the US manufacturer of ROX, quickly suspended ROX sales [5]. In order to monitor the residues of phenylarsonic acid in animal products, it is of great significance to establish a convenient, sensitive and reliable method to analyze the organic arsenic in samples [6].
Several analytical methods for the determination of phenylarsonic acids in the environment have been reported, including liquid chromatography (LC) coupled to atomic absorption spectroscopy (AAS) [7], atomic emission spectroscopy (AES) [8] or atomic fluorescence spectrometry (AFS) [9] as well as gas chromatography-mass spectrometry (GC-MS) [10], capillary electrophoresis (CE) coupled to ultraviolet and visible light detector [11] or inductively coupled plasma-mass spectrometry (ICP-MS) [12]. LC has been demonstrated to be the most effective method in arsenic separation, and ICP-MS can provide low detection limit. Therefore, LC-ICP-MS is one of the most powerful research means for analysis of organic arsenic in complex samples [2], [13]. The LC-MS/MS is a powerful separation and detection platform in multi residues analysis. Pergantis et al [14] have developed a stable method for determination of 5 phenylarsonic acids including ROX, p-APAA, p-NPAA, AAPAA, p-HPAA and other organic arenics using LC-MS/MS in positive ionization mode. The LODs of the developed method achieved sub ng/g level, whereas the analytical time was too long. Furthermore, compared with other arsenic speciation methods, the LC-MS/MS could provide more structural information of the phenylarsonic acids.
After feeding, nearly all phenylarsonic acids are excreted unchanged to the environment through the disposal of poultry litter, so the residues in animal tissues are very low [15], [16]. Some studies indicated that the approved conditions of use mandate a 5-day withdrawal period from the medicated feed before animals are slaughtered, and limits are in place for total residues of combined arsenic (As) in meat from ROX treated animals [0.5 mg kg−1 As in muscle tissue and eggs, and 2 mg kg−1 As in liver and kidney] [17]. To further lower the detection limits of phenylarsonic acids in complex biological samples, nano-materials have been used to selectively extract and concentrate arsenic compounds. The most commonly used nano-materials for the adsorption of arsenic compounds include goethite [18], titania [19], iron oxide [20], [21], Fe3O4 nanoparticles [22], [23] or modified Fe3O4 nanoparticles [24]. Among these nano-materials, Fe3O4 nanoparticles are well suited for arsenic analysis due to the following advantages. First, they can be easily isolated from solutions by applying an external magnetic field [25], which ensures simplified sample adsorption and elution processes. Second, Fe3O4 nanoparticles have been demonstrated to have higher affinity toward arsenic element than other nano-materials, resulting in higher arsenic extraction efficiency. Fe3O4 magnetic nanoparticles have been used for removing inorganic arsenic ions in water sample. For example, Fe3O4 nanoparticles dispersed in chelating resins or coated with adequate chelating agents have been used for the removal of a wide range of metal ions from wastewater, overall displaying higher adsorption capacity than traditional materials [26]–[29]. More recently, β-CD coated Fe3O4 nanoparticles have been successfully applied for the removal of methylene blue and copper ions [30], [31]. It is found that the cavity of cyclodextrin and its surface hydroxyl group can impart better binding capability and chemical stability to the magnetic particle [32].
In this work, a highly sensitive determination method was established to monitor five phenylarsonic acids in chicken tissues. In our first attempt, it was found that the adsorption of phenylarsonic acids by Fe3O4 magnetic nanoparticles was not as good as inorganic arsenic compounds. It was then decided to use CM-α-CD to couple on the surface of Fe3O4 providing CD cavities to fit the benzene rings in the structures of phenylarsonic acid compounds. In addition, hydrogen bonding and electrostatic interactions between hydroxyl/carboxyl groups of modified CM-α-CD and amino/nitro of phenyl arsenic acids were also increased. The adsorption properties of modified Fe3O4 magnetic nanoparticles to phenylarsonic acids were studied, and the interactions between nanoparticles and phenylarsonic acids were examined. The synthesized materials were successfully applied in the sample clean-up and pre-concentration of phenylarsonic acids in chicken muscle and liver samples, which were subsequently separated and detected by UPLC-MS/MS.
Materials and Methods
Apparatus
ICP-MS (Agilent7500Ce, USA) was used to study the adsorption properties of synthesized material for phenylarsonic acids. The optimum operation parameters of ICP-MS were selected by tuning. The power was 1550W, the flow rates of cooling air, auxiliary air and carrier were 15.0 L/min, 1.0 L/min and 1.12 L/min, respectively. The sample rate of ascension by using peristaltic pump was set as 1.0 mL/min. The integration time for arsenic was 0.3 s/isotope. The operating parameters of UPLC-MS/MS (Waters Xevo TQ, USA) were as follows: capillary voltage = 2.8 kv, desolvation temperature = 450°C, desolvation gas flow rate = 600 L/Hr. The mobile phase was a mixture of acetonitrile (solvent A) and water containing 0.1% formic acid (solvent B) at a flow rate of 0.3 mL/min. All chromatographic separations were carried out in linear gradient mode as follows. In the first minute, solvent A was maintained at 98% (v/v). Solvent B quickly dropped to 30% from 1 to 3 min, followed by dramatic increase back to 98% from 3 to 5 min. MS parameters of UPLC-MS/MS are showed in Table 1.
The closed microwave digestion system (CEM MARS, American) was used to digest samples for the determination of the total arsenic in the crude samples. The homogenizer (IKA, Germany) was applied to sample pretreatment and rocking hammock bed was from Zhicheng, Shanghai, China.
Standard solutions and reagents
Five phenylarsonic acids (98%) were obtained from the Chinese Academy of Agricultural Sciences. The standard stock solutions were prepared by dissolving each arsenic species in pure water at an arsenic concentration equivalent to that of 1 mg/mL phenylarsonic acids and stored at 4°C in the dark.
Reagents for preparing magnetic nanoparticles: FeCl2⋅4H2O and FeCl3⋅6H2O (analytical reagent grade) were purchased from Tianjin Guangfu Fine Chemical Research Institute. Sodium chloroacetate (98%) was bought from Alfa Aesar. α-cyclodextrin (98%) was purchased from Beijing Dilang Biochemical Technology Co., Ltd., China. Other reagents including methanol, ethanol, acetone, toluene, formic acid and sodium hydroxide were of analytical reagent grade and all bought from Beijing Chemical Plant. The water used throughout the experiment was purified using a Milli-Q water purification system (Millipore, Germany).
Preparation of CM-α-CD stabilized magnetic nanoparticles
Synthesis of CM-α-CD.
CM-α-CD was prepared according to the following procedures. α-CD (3.55 mmoL) and NaOH (90.2 mmoL) were first dissolved into 20 ml water. The solution was then heated at 90°C for 5 min, followed by the addition of 74.6 mmoL sodium chloroacetate. The solution was heated for 3 h at 90°C under stirring. Once cooled to room temperature, the pH of the solution was adjusted to 6–7 by hydrochloric acid. The nearly neutral solution obtained was then poured into about 500 mL methanol. CM-α-CD was precipitated out as white solids, which was filtered and washed with methanol for a few times and then dried under vacuum for 3 d at 50°C and 0.085 MPa. The melting point of the CM-α-CD product was about 245.5°C as determined by micro melting point apparatus.
Synthesis of Fe3O4 nanoparticles.
Fe3O4 magnetic nanoparticles were prepared according to the conventional co-precipitation method [33]. A mixture of 2.0 g FeCl2⋅4H2O and 5.2 g FeCl3⋅6H2O was added into a 500 mL conical flask containing 200 ml 0.05 M HCl. After dissolution of the solids, 250 ml 0.75 M NaOH solution was poured into the flask under a blanket of N2. The mixture was stirred for another 2 h at 80°C. The Fe3O4 nanoparticles were then obtained in the form of black precipitates, which were separated with a magnet and washed subsequently by water (3 times) and ethanol (twice). It should be noted that both the HCl and NaOH solutions were degassed by a sonicator for 20 min before use.
CM-α-CD modified Fe3O4 nanoparticles (CM-α-CD-Fe3O4).
The Fe3O4 nanoparticles prepared in the previous step were added into 60 ml PBS buffer solution (pH = 6.6) containing 1.6 g of CM-α-CD. The suspension was sonicated for 3 min and then stirred for 3 h at 80°C. After cooling to room temperature, the nanoparticles were washed several times by PBS buffer solution to remove excess CM-α-CD. The CM-α-CD modified Fe3O4 nanoparticles were then dried at 80°C in a vacuum oven.
Adsorption procedure
Static adsorption.
In a 10 mL centrifuge tube, 5 mg CM-α-CD-Fe3O4 nanoparticles were mixed with 8 mL standard solution of phenylarsenic acid with a given concentration. The centrifuge tube was placed on a rocking hammock bed at a rate of 270 rpm. After equilibrating for 30 min, the magnetic nanoparticles were separated from the solution with external magnetic field. The nanoparticles were rinsed twice with ethanol and dried in N2. To desorb target compounds, 1.0 mL pure water was added to the nanoparticles followed by equilibration for 10 min. The aqueous solution containing target compounds was filtered through a 0.22 µm Poly (ether sulfones) (PES) syringe filter and analyzed by ICP-MS. Standard phenylarsenic acid solutions of other concentrations were analyzed in the same way.
Dynamic adsorption.
In a 10 mL centrifuge tube, 5 mg CM-α-CD-Fe3O4 nanoparticles were mixed with 8 mL standard solution of phenylarsenic acid with a given concentration. A number of centrifuge tubes were prepared in this manner for a given concentration of standard. The centrifuge tubes were placed on an orbital shaker at a rate of 270 r/min. At different time points, one tube was removed and the magnetic nanoparticles contained in the tube were separated from the solution with external magnetic field. The following washing, desorption and ICP-MS analysis procedures were the same as those in the static adsorption step. Standard phenylarsenic acid solutions of other concentrations were analyzed in the same way.
Sample analysis
Chicken tissues including meat and liver were bought from a supermarket in Beijing. Chicken meat and chicken liver samples were pulverized and freeze-dried for 24 h. The freeze-dried sample was homogenized by grinding and frozen until analysis. In a 50 mL centrifuge tube, 5.0 g freeze-dried chicken tissue sample and 10 mL ethanol were added. The extraction was repeated twice, each lasting 30 min. The combined extracts were equilibrated with 5 mg CM-α-CD-Fe3O4 nanoparticles for 10 min. Then the magnetic nanoparticles which adsorbed target analytes were separated under external magnetic field, the analytes adsorbed on the nanoparticles were then desorbed with 2 mL deionized water. The aqueous solution containing target compounds was filtered through a 0.22 µm PES syringe filter and analyzed by UPLC-MS-MS.
Determination of total arsenic
The total amount of arsenic in chicken tissue samples was determined by microwave digestion ICP-MS according to reference [34]. Each digestion can containing 0.5 g chicken tissues samples was added 5 mL 65% nitric acid. Stages digestion method by controlling temperature was used. The obtained digestion solution was diluted until the concentration of nitric acid fell below 5% and then subjected to ICP-MS analysis.
Results and Discussion
Optimization of adsorption efficiency
For optimal adsorption efficiency, the amounts of CM-α-CD for the modification of Fe3O4 nanoparticles were varied in six dosages of 0.8, 1.6, 2.4, 3.2, and 4.8 g to obtain 450 mL of Fe3O4 suspension as described in section 2.3.2. The adsorption was carried out by equilibrating 5 mg CM-α-CD-Fe3O4 in 8 mL ROX standard solution at a concentration of 1 µg/L. The adsorption efficiency was then determined by ICP-MS. As shown in Fig. 1, the highest adsorption efficiency corresponds to 1.6 g CM-α-CD. Fig. 2 shows the adsorption behaviors of ROX at different concentrations by CM-α-CD-Fe3O4. The amount of adsorbed ROX is linear over a large concentration range of ROX. To verify the important role of CM-α-CD in the adsorption of phenylarsonic acid, the adsorption efficiencies of modified and unmodified Fe3O4 nanoparticles for p-NPAA were compared. As shown in Fig. 3, modified material was obviously superior to unmodified material.
Characterization of magnetic CM-α-CD-Fe3O4
The transmission electron microscope (TEM), fourier transform infrared spectrometry (FTIR) and thermo gravimetric analyzer (TGA) were used to characterized the magnetic nanoparticles. The TEM images of Fe3O4 and CM-α-CD-Fe3O4 nanoparticles are shown in Fig. 4 (a) and Fig. 4 (b), respectively. Unmodified Fe3O4 nanoparticles, approximately 10 nm in diameter, trend to aggregate because of size effect of Fe3O4 nanoparticles. On the other hand, CM-α-CD-Fe3O4 nanoparticles shown in Fig. 4 (b) are much better dispersed in an aqueous solution with diameters of about 5 nm, because the Fe3O4 nanoparticles were modified with CM-α-CD and the surface of Fe3O4 nanoparticles was protected by CM-α-CD. It can be observed in Fig. 4 (b) that the composite of modified nanoparticles was more compacted and displayed roughly spherical shapes.
The FTIR spectrums of Fe3O4, CM-α-CD and CM-α-CD- Fe3O4 nanoparticles respectively were scanned (See Fig. S1). In all three samples, a strong characteristic O-H absorption band at around 3400 cm−1 is clearly visible. There is a strong Fe-O absorption peak at 580 cm−1 for both Fe3O4 and CM-α-CD-Fe3O4, suggesting the intactness of the Fe-O bond during the modification process. Compared with the innate Fe3O4 nanoparticles, new characteristic peaks at 1100 and 2900 cm−1 appeared in the spectrum of CM-α-CD- Fe3O4 nanoparticles, corresponding to C-O-C and C-H groups of CM-α-CD, which are also visible in the spectrum of pure CM-α-CD. This confirms the success of the modification of CM-α-CD to Fe3O4 nanoparticles.
The amount of CM-α-CD grafted on the surface of Fe3O4 and the number of CM-α-CD molecules immobilized on a single Fe3O4 nanoparticle can be estimated from the TGA results. It is known that CM-α-CD decomposes completely above 600°C.The TGA curves of Fe3O4 and CM- α-CD-Fe3O4 exhibit two steps of weight loss. In both cases, the first step can be attributed to the loss of residual water.The amounts of CM-α-CD coated on the surface of Fe3O4, calculated on the basis of the second-step loss, are 5.3% and 9.6% for Fe3O4 nanoparticles and CM-α-CD-Fe3O4 nanoparticles, respectively. The increase of the weight loss can be ascribed to CM-α-CD grafted on Fe3O4 nanoparticles (about 43 mg/g). According to Y. P. Wu [35], the number of CM-α-CD molecules immobilized on a single Fe3O4 can be calculated in equation (1): (1)where N is the number of CM-α-CD molecules immobilized on each Fe3O4, R is the mean radius of CM-α-CD-Fe3O4 (5.0 nm based on the TEM results), ρ is the density of the nanoparticle (4.8 g/cm3), NA is Avogadro's number, WCD and WFe3O4 are the weight losses of the CM-α-CD-Fe3O4 and Fe3O4 respectively, MCD is the molar mass of CM-α-CD immobilized on CM-α-CD-Fe3O4. The calculated number of CM-α-CD molecules immobilized on each CM-α-CD-Fe3O4 is about 70.
Selection of adsorption solvent
The solvent for phenylarsonic acid solutions is an important factor affecting the adsorption efficiency. Five candidate solvents, i.e., water, methanol, ethanol, acetone and toluene, were compared (Fig. 5). The adsorption efficiency of all target arsenic species could reach 100% in ethanol, acetone and toluene. Ethanol was selected as the solvent in the following experiments due to the relatively low toxicity. In water and methanol, the adsorption efficiencies of the five target compounds are very poor, which might be because of the water and methanol possess higher polarity than ethanol, acetone and toluene.
The concentration of each phenylarsonic acids was 50 ng/mL. Adsorption time was 30 min. 5 mg adsorbent was used. (n = 3, with RSD<4.5%).
Static adsorption
Saturation of adsorption.
The adsorption saturation curve is shown in Fig. 6. The point of saturation was reached at 40 µg for p-HPAA, p-APAA, and AAPAA, whereas it was 60 µg for p-NPAA and ROX, corresponding to about 0.2 µmol of each phenylarsonic acid.
5 mg adsorbent was used for each solution. Adsorption time was 30 min. Desorption was in water for 10 min. (n = 3, with RSD<5.7%).
The amount of CM-α-CD coated on the surface of Fe3O4 could be estimated from the saturation of adsorption. Since one phenylarsonic acid molecule was supposed to fit one CD cavity, there should be approximately equal amount of CD and phenylarsonic acid. Thus, the amount of CM-α-CD might be calculated through its molecular mass of 1029 according to equation (2). The estimated amount of grafted CM-α-CD was about 41.2 mg/g, which was similar to 43 mg/g calculated by TGA in 3.2.3. (2)
Enrichment factors of low concentration.
The lowest concentrations of phenylarsonic acids that could be absorbed by CM-α-CD-Fe3O4 as well as enrichment factors were investigated. Ultimately, the enrichment factors of p-APAA, AAPAA, ROX, p-HPAA and p-NPAA were 414, 426, 581, 606 and 349 (theoretical enrichment factor was 500) at the concentration of 0.1 µg/L. Enrichment efficiency was 69.8%-121.2% and experimental results are shown in Table 2.
Dynamic adsorption
Optimization of adsorption time and desorption time.
The water was selected as desorption solvent. The adsorption efficiency was optimized by varying the adsorption time in the range of 1–40 min with all other parameters held constant. The adsorption efficiency increased with the adsorption time from 1 to 30 min followed by a plateau. The rate of adsorption was so high that 5 min was enough to adsorb the target compounds. Similarly, desorption efficiency was optimized by varying desorption time in the range of 1–10 min. The desorption efficiency increased with desorption time till 10 min, at which point it plateaued. Therefore, 10 min was selected as desorption time and desorption efficiency was achieved above 75%.
The tolerance of coexisting inorganic ions and organic analogues.
By fixing the concentration of each phenylarsonic acids at 50 µg/L and 12 coexisting inorganic ions including Mn2+, Cu2+, K+, Zn2+, Ba2+, Fe3+, Mg2+, Ca2+, Pb2+, Cr3+, Cd2+, and Sn2+ at concentrations of 500, 5000, and 50000 µg/L for each inorganic ions respectively, interference of inorganic ions on the adsorption of phenylarsonic acids was studied. No significant interferences were observed under the optimum conditions described above in the presence of inorganic ions as high as 50000 µg/L. The influence of four organic analogues including phenol, benzoic acid, p-hydroxbenzoic and m-hydroxbenzoic acid at concentrations of 50, 250 and 500 µg/L for each organic analogues respectively on the adsorption of target arsenic species was investigated. As shown in Table 3, the allowed concentrations of coexisting analogues were about 500 µg/L or 250 µg/L with a tolerance factor of less than 5%. However, p-NPAA was an exception. The tolerance concentration of p-hydroxybenzoic acid was only 50 µg/L. Possible explanation is shown in Fig. 7. Despite other interactions, the hydrogen bonding between hydroxyl on the surface of CM-α-CD-Fe3O4 and amino groups of p-APAA and AAPAA was very strong but there was hardly any hydrogen bonding between the hydroxyl and nitro of p-NPAA. In any case, phenylarsonic acid could form inclusion complex with α-CD and therefore the arsenate, hydroxyl or amino group were forced closer to the magnetic particles, leading to stronger interactions between the modified material and phenylarsonic acids. Both selectivity and adsorption efficiency were improved compared to that of Fe3O4 nanoparticles without modification.
Analytical performance
Optimization of UPLC-MS-MS chromatograph separation condition.
A mixture of five arsenic compound standards, each at a concentration of 2.0 µg/L, was successfully separated and analyzed by UPLC-MS/MS in less than 3 min on a C18 column. Under the optimal separation conditions, baseline separation was achieved for every arsenic compound. The multi-reaction monitoring (MRM) chromatograms of arsenic compounds are shown in Fig. 8.
Optimization of sample pretreatment condition.
To extract phenylarsonic acids from chicken tissue samples, different extraction methods (including ultrasonic extraction, microwave extraction), extraction time (10, 20, 30, 40, 50 and 60 min) and extraction solvents (methanol, ethanol and toluene) were studied. The optimal recovery was above 75% with the ultrasonic extraction method and toluene as the extraction solvent. The proper extraction time was found to be 30 min and extraction should be conducted twice.
Method evaluation
The developed method was validated by determining the linearity and LOD of arsenic species listed in Table 4. A linear response can be seen in the concentration range of 0.20–10 µg/L (enrichment factor 2.5), with the R2 ranging from 0.9951 to 1.0000. The repeatability study was performed for each of the phenylarsonic acids under the optimal conditions. The LOD of each phenylarsonic acid was estimated by analyzing blank samples spiked at 0.2 µg/kg of each target analytes and they were determined as the lowest concentrations of the analyte for which signal-to-noise ratios were 3 respectively. The resultant repeatabilities expressed as RSD varied from 0.85% to 4.49%. These results show that the method has a high sensitivity and good repeatability.
Sample analysis
The phenylarsonic acid in tissue was stored with the prototype compound. So the sample preparation of real tissue samples is same as the spiked samples [17]. In order to validate the suitability of the developed method, the method was applied to analyze spiked chicken tissue samples. For comparison, the total arsenic in these samples was also determined.
In the samples of chicken meat and liver, 0.2, 2 and 20 µg/kg of each phenylarsonic acids were spiked, respectively. The recoveries of five phenylarsonic acids in chicken tissue samples, as shown in Table 5, fell in the ranges of 77.2%–110.2%, with a RSD less than 12.5%. The chromatograms of spiked chicken meat sample (2.0 µg/kg) and blank chicken meat sample are shown in Fig. 9. To confirm the selectivity of CM-α-CD-Fe3O4, five phenylarsonic acids were spiked individually in each sample at 0.2 µg/kg and determined by ICP-MS. Recoveries were in the range of 81.5%–119.2% which agreed with the UPLC-MS/MS results. This shows that the CM-α-CD-Fe3O4 nanoparticles have high selectivity for phenylarsonic acid and can be used for sample clean-up. Combining CM-α-CD-Fe3O4 nanoparticles clean-up procedure with UPLC-MS-MS technique would potentially result in practical application in the analysis of trace phenyl arsenic acids.
Conclusions
In this work, CM-α-CD-Fe3O4 nanoparticles were synthesized to selectively extract and enrich phenylarsonic acids. CM-α-CD- Fe3O4 nanoparticles exhibited excellent selectivity and adsorption efficiency for five phenylarsonic acids because of the size selectivity of α-CD and the affinity of Fe3O4 to arsenic. In the sub ppb level of phenylarsonic acids, the enrichment factor was higher than 400 and the extraction efficiency higher than 70%. Coupled with UPLC-MS/MS, a fast, selective and convenient analytical method for the determination of phenylarsonic acid was developed. Comparing with published method [14], the developed method showed satisfactory sensitivity due to the selectively adsorption of CM-α-CD-Fe3O4 nanoparticles for phenylarsonic acids in complex sample matrix.
Supporting Information
Figure S1.
FTIR spectra of Fe3O4 magnetic nanoparticles (a), CM-α-CD (b) and CM-α- CD- Fe3O4 (c).
https://doi.org/10.1371/journal.pone.0107147.s001
(TIF)
Author Contributions
Conceived and designed the experiments: PW RZ. Performed the experiments: JJ. Analyzed the data: JW PW. Contributed reagents/materials/analysis tools: WZ PW. Contributed to the writing of the manuscript: PW RZ.
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