Xue-Peng
Wei‡
a,
Rui-Qian
Zhang‡
a,
Le-Bin
Wang
b,
Yan-Ling
Luo
*a,
Feng
Xu
*a and
Ya-Shao
Chen
a
aKey Laboratory of Macromolecular Science of Shaanxi Province, School of Chemistry and Chemical Engineering, Shaanxi Normal University, Xi’an 710062, P. R. China. E-mail: luoyanl@snnu.edu.cn; fengxu@snnu.edu.cn; Fax: +86 29 81530727
bSchool of Materials Chemistry, Xiangtan University, Xiangtan 411105, P. R. China
First published on 24th November 2018
With the increasing development of science and technology, food analysis and detection techniques are continouosly being updated, consummated, and are booming. To meet the demands for high efficiency, speediness, and accuracy in food detection, new rapid detection technology needs to be developed for ensuring food safety and human heath. For this purpose, multi-walled carbon nanotubes decorated with gold nanoparticles-grafted poly(2-methacryloyloxyethyl ferrocenecarboxylate) (MWCNTs@Au-g-PMAEFc) nanohybrids were prepared through ATRP of MAEFc, with the MWCNTs@Au nanocomposites prepared via an in situ reduction route. The chemical structure and composition of the nanohybrids were characterized by 1H NMR, FTIR, Raman, XRD, TGA, UV-vis, and XPS techniques. The dispersion behavior and morphologies were investigated by UV-vis, TEM, and SEM observations. The electrochemical properties were studied by cyclic voltammetry (CV) and differential pulse voltammetry (DPV). The experimental results indicated that the nanohybrid-modified electrodes possessed clearly improved electrochemical properties and good reversibility of the redox process, which could be tuned by altering the composition proportions, including the mass ratios of MWCNTs to Au NPs, and the graft percentage of PMAEFc chain segments. The resultant modified electrode sensors could efficiently detect trace poisonous and harmful pesticide residues, and presented a good linear relationship between the concentration and the peak currents, giving a low limit of detection of about 2.7 × 10−8 mol L−1. The developed nanohybrids could therefore be fabricated into electrochemical sensors to detect trace pesticide for ensuring food safety.
At present, the food detection analysis techniques include chemical analysis (CA), infrared spectroscopy, and various chromatographic techniques, including thin layer chromatography (TCL), gas chromatography (GC), high-performance liquid chromatography (HPLC).4,5 NMR-spectroscopy was also reported for the nontargeted screening and simultaneous quantification of melamine.6 Compared with CA and TCL, although GC and HPLG possess high sensitivities, veracity, and accuracy, they generally need expensive equipment, a tedious pre-processing process, and high professional operation skills. In addition, the complicated sample matrix background, time-consuming analysis, low analyte concentrations, and confined qualitative ability of analytical instruments are responsible for the detection difficulties of trace pesticides and food additives. Consequently, they are not suitable for on-spot rapid determination and popularization. The development and applications of molecular imprinting, electrochemical, and biosensing technologies are compensating for the shortcomings of these techniques.7–9 In particular, electrochemical sensors based on nanocomposites have the advantages of a simple design, low cost, tunable electrochemical properties, high sensitivity, and rapid response, thus they have been widely used in the detection of OPPs residues.10 Therefore, the design of novel nanocomposite modified electrodes that can enhance the properties of the electrochemical sensors will be of great importance for development of the sensors and the follow-up detection of hazardous substances. In spite of this, there exist some difficulties in the food safety detection; in most cases, the limit of detection, reproducibility, and stability need to be improved so as to efficiently and effectively detect trace residues.
Gold nanoparticles (Au NPs) have a special quantum surface effect, excellent stability and biocompatibility, unique optical, electrical, magnetic, and catalytic properties, and high electrocatalytic activities, which thus have been widely used in the field of electrochemical sensing, biological analysis, biomedical testing, catalysis, anticancer drugs, drug delivery, sensors, antioxidants, larvicides, antimicrobials, nanofluids, and agriculture.11–13 In particular, the rapid detection technique based on Au NPs immune markers has increasingly been applied in modern food analysis and in detection, having the advantages of simplicity, celerity, high sensitivity, and specificity, low cost and a small amount of samples. Carbon nanotubes (CNTs)-based electrochemical sensors have been widely used in the detection of metal ions, pesticides, and other pollutants because CNTs exhibit eminent physical, mechanical, electrochemical, and optical properties, rapid electronic transport properties, large specific surface areas, and strong absorption performances etc.14–16 The decoration of Au NPs on the surface of CNTs will construct a new class of nanocomposites with multifunctional properties, including excellent conductivity, appealing optics, catalysis, and electrochemical redox characteristics, especially the electrocatalytic activity based on a cooperative effect when compared to either material alone.17–19 This combination also contributes to the improvement of dispersity of the CNTs by a strong non-covalent interaction between CNTs and Au NPs,20 and can therefore be potentially used in optical, catalytic, sensor, solar cells, and most importantly in biosensor applications. On the other hand, ferrocene-based polymers as a new class of functional polymers possess unique electron transfer traits, redox electrochemical properties, and semiconducting, photophysical, catalytic, photoelectronic and electronical properties,21,22 and thus are widely used as semiconducting materials, phase separation materials, catalysts, redox responsive drug carriers, biosensors, magnetic ceramic precursors and smart surface.23,24 Especially in recent years, Wong's research groups have synthesized nanopatterned face-centered tetragonal Fe–CoPt and Fe–Pt phase NPs by utilizing metallopolymer precursors containing ferrocene as templates which, upon pyrolysis or photolysis, generate NPs with narrow size distribution, precisely controllable composition and density per unit area.25–27 These materials can potentially be used as a high-density magnetic data storage media, bit-patterned magnetic recording media, spintronic “switching” devices, nanogranules in gap structures, and magnetic sensing heads.26–30 The most recent progress in ferrocene derivatives was related to the realization of the lithographic patterning of ferromagnetic FePt NPs from a single-source bimetallic precursor containing a hemiphasmidic structure, which offers a promising route to develop bit-patterned media for next-generation magnetic data-recording systems.31 These studies motivated us to further graft ferrocene-containing polymers with unique properties onto the CNTs@AuNPs nanomaterials, thus constructing a novel organic–inorganic nanohybrid with improved electrical conductivity and electron-transfer properties, especially better electrochemical responses based on a synergistic effect. This will open up an exciting new horizon in the science and technology of CNTs, electrochemical sensors, and biosensors, and provide significant technical innovations for food safety detection.
In this context, we aimed to modify MWCNTs with Au NPs through an in situ reduction reaction based on strong non-covalent supramolecular interactions or electrostatic attraction interactions, and then to design and synthesize novel MWCNTs@Au graft ferrocene-based polymer poly(2-methacryloyloxyethyl ferrocenecarboxylate) (MWCNTs@Au-g-PMAEFc) organic–inorganic nanohybrids through atom transfer radical polymerization (ATRP). The MWCNTs@Au-g-PMAEFc was fabricated into electrochemical sensing films, and the effect of the content of Au NPs and the graft percentage of PMAEFc on the electrochemical properties was investigated. To the best of our knowledge, there is no relevant literature reporting similar work. We expect that the sensing materials with higher charge-transfer rates and better electrocatalytic activities based on a synergistic effect could be obtained to detect the residues of organophosphorous pesticides and food additives in vegetables and fruits, etc., thus providing health assurance for food safety.
In the third step, the ATRP initiator precursor MWCNTs@Au-OH with hydroxyl groups on the surface was prepared through the coordination interaction between Au NPs and –SH groups in ME at a mole ratio of ME:Au of 6:1. Taking MWCNTs:Au = 1:1 (w/w) for example, 0.05 g MWCNTs@Au (Au NPs: 0.105 mmol) was dispersed in 50 ml deionized water and ultrasonicated for about 30–60 min. After that, the calculated amount of ME (0.044 ml, 0.63 mmol) was added into the solution. The reaction solution was stirred at room temperature for 24 h, and then centrifuged. The solid was repeatedly rinsed with absolute ethyl alcohol to remove the unreacted ME. The crude product was dried under vacuum at 80 °C for 24 h, offering MWCNTs@Au-OH nanocomposites (yield: 78%; theoretical amount of ME: 5.56 mmol g−1). Other nanocomposites with various compositions could be prepared in the same way as the above description.
ATRP initiator MWCNTs@Au-Br was prepared through an esterification route as per the mole ratio of MWCNTs@Au-OH:BIB:TEA of 1:4:4. Specifically, 0.05 g MWCNTs@Au-OH (MWCNTs:Au = 1:1 (w/w), ME: 0.278 mmol) was dispersed in 50 ml dried DCM in a 100 ml three-neck flask, which was then sealed for ultrasonication for 30 min. Afterward, the mixture solution was cooled in an ice bath and purged with N2 for 30 min. When the reaction temperature was reduced to 0 °C, 137.5 μl (1.112 mmol) BIB dissolved in 5 ml DCM in advance was drop-wise added into the reaction system with a constant pressure funnel under the protection of N2 within 30 min. After, the mixture solution was kept at 0 °C for 30 min, then 154.1 μl TEA (1.112 mmol) dissolved in 5 ml DCM was drop-wise added into the reaction flask with a constant pressure funnel within 30 min, and then N2 was closed off. The reaction proceeded at 30 °C for 24 h with stirring. The mixture solution was centrifuged, and the solid was repeatedly rinsed with DCM to remove the unreacted BIB and TEA, and then dried at 60 °C for 24 h, giving the resultant MWCNTs@Au-Br (yield: 69%; theoretical amount of BIB: 3.39 mmol g−1).
To prepare MWCNTs@Au-g-PMAEFc organic–inorganic nanohybrids, 2-methacryloyloxyethyl ferrocenecarboxylate (MAEFc) was first prepared, as shown in Fig. S1(a–c) in ESI.† Subsequently, MWCNTs@Au-g-PMAEFc nanohybrids were prepared through the ATRP of MAEFc at mole ratios of [MWCNTs@Au-Br]:[MAEFc]:[CuBr]:[HMTETA] of 1:50:6:5 and 1:150:6:5.34,35 Typically, for [MWCNTs@Au-Br]:[MAEFc]:[CuBr]:[HMTETA] of 1:50:6:5, a certain amount of MWCNTs@Au-Br (0.05 g, BIB: 0.1695 mmol for MWCNTs:Au = 1:1 (w/w)) and MAEFc (2.8985 g, 8.475 mmol) were added to a 25 ml dried Schlenk flask and then 4 ml desiccative DMF was introduced. The reaction flask was frozen, vacuumized, and then suffused with N2, and then a certain amount of HMTETA (230.5 μl, 0.8475 mmol) was injected into the flask under N2 atmosphere via a micro-syringe, followed by an immediate freeze–pump–thaw–nitrogen filling process. The purified CuBr powder (0.1459 g, 1.017 mmol) was promptly added to the system under N2 flow, followed by repeating the above freeze–pump–thaw–nitrogen filling operation. After, cooling and reflux units were connected with the reaction system, the polymerization proceeded at 90 °C for 24 h, with persistent stirring. The resulting solution was centrifuged, and repeatedly rinsed with DMF to get rid of the unreacted MAEFc and HMTETA, and then repeatedly flushed with absolute ethyl alcohol to remove CuBr. The product was dried in a vacuum oven at 80 °C for 24 h, giving MWCNTs@Au-g-PMAEFc organic–inorganic nanohybrids (yield: 57%).
UV-vis absorption spectra were recorded on a UV-3900/3900H UV-vis spectrophotometer (Hitachi, Japan) to examine the dispersion behavior of the prepared nanohybrids in ethanol solution, and to confirm the formation of the nanohybrids. The wavelength for measurement was 325 nm. A SU-8020 cold-field emission scanning electron microscope (FESEM, Hitachi High-Technologies Corp, Tokyo, Japan) was adopted to observe the surface morphologies of the MWCNTs@Au and MWCNTs@Au-g-PMAEFc nanohybrids and to estimate the system composition. The whole operation was conducted at an operating voltage of 1.0–15 kV. A transmission electron microscope (TEM, JEM H-600, Electron Corp., Japan) was used to inspect the morphologies, sizes, and size distribution of the samples, with an accelerating potential of 200 kV. Before observation, the samples were ground into powders, and were dispersed in chloroform under ultrasonication for 30–60 min. One drop of the sample dispersion was uniformly dripped on carbon-based supporting films, and another drop was added after natural drying. An energy-dispersive X-ray spectrometer (EDX) attached to TEM was used to detect the elemental compositions.
The CV and DPV experiments were performed on a CHI660E electrochemical workstation (Chenhua Instrument Co., Ltd, Shanghai, China), with a conventional three-electrode system consisting of bare and modified glassy carbon electrodes (GCEs) (4.0 mm in diameter) as a working electrode, a saturated calomel electrode as a reference electrode, and a platinum wire electrode as a counter electrode. The detection of the bare GCE was conducted in an oxidation–reduction probe solution (ORPS) consisting of K3Fe(CN)6/K4Fe(CN)6/KCl in a molar ratio of 1:1:100 (pH = 7.0) as supporting electrolytes.36 The DPV measurements were performed at an amplitude of 25 mV; a pulse width and pulse period of 0.05 and 0.05 s, respectively; a scan rate of 15 mV s−1; an accumulation potential of 1.15 V; an accumulation time of 100 s, and a potential increment of 0.001 V.
Fig. 1(B) illustrates the FTIR spectra of the MWCNTs and the resultant nanohybrids. The original pristine MWCNTs generate characteristic absorption peaks at 2915 and 2845 cm−1, attributed to the sp3 C–H and sp2 C–H stretching vibrations originating from the defects on the MWCNTs at the sidewalls;40 this conveys there are abundant reaction sites. The vibration bands at 1535 and 1630 cm−1 are assigned to the CC stretching of the hexagonal or benzenoid (νCC) structure of the MWCNTs, indicating the graphite structure of the MWCNTs.41,42 The vibration bands at 3425, 1715, and 1025–1160 cm−1 are ascribed to the –OH, –CO, and C–O stretch modes, respectively, which may be due to the moisture absorbed from air by MWCNTs and the residues of carboxylic groups during preparation. For the MWCNTs@Au-g-PMAEFc nanohybrid, several new vibration bands emerge at 3120, 850, and 479–515 cm−1, which correspond to the C–H stretch, the C–H bending, and Fe–C or Cp–Fe stretch modes in ferrocene rings, respectively. The bands at 2850–2960, 1716, and 1015–1140 are ascribed to the C–H, CO, and C–O stretch modes, respectively. However, the peak intensity at 3100–3200 cm−1 is weakened in comparison with monomer MAEFc in Fig. S1(c) of the ESI† because the terminal double bonds turn into saturated single bonds after ATRP polymerization. In addition, the characteristic stretch vibration band at 1605 cm−1 is attributed to the benzenoid (νCC) structure in MWCNTs’ backbones, confirming the preparation of MWCNTs@Au-g-PMAEFc organic–inorganic nanohybrids.
Raman spectra were measured to further confirm the preparation of the nanohybrids, as displayed in Fig. 1(C). It can be clearly seen that the MWCNTs exhibit three typical vibration modes, including a D line at about 1346 cm−1, and G band at ca. 1587 cm−1, which correspond to the vibrations of amorphous carbon defects and disorder-induced sp3-hybridized carbon atoms, and of sp2-hybridized carbon atoms (E2g stretching mode) in a graphitic layer, respectively.43 The peak at 2690 cm−1 is assigned to the 2D frequency peak of graphene (the second-order Raman vibration peak of D* mode, also called the G′ peak).44,45 The relative peak intensity ratio of the D to G band (ID:IG) was calculated to be about 0.85, suggesting that some defects exist in MWCNTs;42,46 which could be expected to make the Au NPs more favorably load on the surface of MWCNTs. In the case of MWCNTs@Au and MWCNTs@Au-g-PMAEFc, the three vibration bands ascribed to MWCNTs remain the same. The intensities of D peaks are, however, significantly increased, and the ID:IG intensity ratios increased up to 0.94 and 1.08, respectively. This indicates that Au NPs are loaded onto the surface or defect dots of MWCNTs, forming non-covalently bonded MWCNTs@Au nanocomposites, and that PMAEFc is covalently grafted onto the surface of MWCNTs@Au and/or MWCNTs.
XRD analysis was carried out to obtain information on the crystalline phase structure of the prepared nanohybrids, as shown in Fig. 1(D). The as-grown MWCNTs generate a sharp and strong diffraction peak at 2θ of ca. 25.9°, corresponding to the (002) diffraction plane of the graphite structure. Several other characteristic diffraction peaks appear at 43.0°, 44.1°, and 51.4°, attributed to the (100), (101), and (004) diffraction planes, respectively.47 In the XRD spectra of Au NPs, several main diffraction peaks emerge at about 38.2°, 44.4°, 64.6°, 77.5°, and 81.7°, which correspond to the (111), (200), (220), (311), and (222) phases, respectively.48,49 The average crystal size was calculated to be about 11.5 nm through the Scherrer formula based on the (111) diffraction plane showing strong diffraction. In the XRD patterns of MWCNTs@Au, the characteristic diffraction peaks of both MWCNTs and Au NPs can be observed; appearing at about 25.8° and 44.2° (MWCNTs) and 38.1°, 44.2°, 64.5°, 77.6°, and 81.7° (Au NPs), respectively. However, the peak intensities are weakened due to the non-covalent interaction between MWCNTs and Au NPs, as stated before. In the presence of MWCNTs@Au-g-PMAEFc, a wide diffuse scattering peak emerges at 2θ of 14.1°–34.0° assigned to PMAEFc moieties in addition to the characteristic diffraction peaks of MWCNTs and Au NPs. Since a large number of PMAEFc moieties are grafted on the surface of the MWCNTs@Au nanocomposites, the peak intensities are weaker than their precursors.
TGA analysis was performed to investigate the thermal decomposition behavior of MWCNTs@Au-g-PMAEFc nanohybrids, as illustrated in Fig. 2(A). It is clearly noticed that both MWCNTs and Au NPs are thermostable, and mass losses of only about 5.0% and 2.1% are produced separately until 800 °C. As such, it is understandable that MWCNTs@Au nanocomposites also have good thermostability with only approximately 8.7% mass loss up to 800 °C. A slight increase in the mass loss is maybe caused by the absorbed moisture, dust, and thermo-labile contaminants or functional groups during the preparation process.50 The thermal events of MWCNTs@Au-g-PMAEFc can be divided into two stages: a mass loss of ca. 3.1 for MWCNTs@Au-g-PMAEFc-1 and 10.2% for MWCNTs@Au-g-PMAEFc-2 until 200 °C, which is ascribed to the volatilization of the residual solvents and reagents, etc. The follow-up weight loss is attributed to the decomposition of the side-chain carbonyl groups and the skeleton in the nanohybrids. Until 800 °C, the mass loss reaches about 17.2% for MWCNTs@Au-g-PMAEFc-1 and 47.8% for MWCNTs@Au-g-PMAEFc-2. Considering that the theoretical content of Fe in PMAEFc is about 17%, it is estimated that the graft percentage of PMAEFc on the surface of MWCNTs@Au or MECNTs is about 7.0% and 33.2% for feed ratios of MWCNTs@Au:MAEFc of 1:50 and 1:150, respectively. These values are slightly lower than those by 1H NMR.
TEM was used to observe the morphologies, sizes, and size distribution of the prepared MWCNTs@Au-g-PMAEFc, as depicted in Fig. 3. The original pristine MWCNTs were randomly intertwined together due to the van der Waals forces between the MWCNTs, with a tubular diameter of 12–22 nm and a mean diameter of 17 nm, as specified by the manufacturer. Au NPs assume homogeneous globular mophologies, with a uniform particle size distribution, with most of them ranging from about 7 to 15 nm, with an average size of ca. 12 nm. After the in situ reduction, it could be observed that the spherical Au NPs were not evenly deposited and decorated on the tube walls of the MWCNTs, as demonstrated in Fig. 3(c). On this occasion, the defect points on the surface of MWCNTs were exactly the growth points of the Au NPs, leading to the growth of a mass of Au NPs grains on the ektexines of MWCNTs.51 Moreover, since the MWCNTs possess strong adsorptivity, large micropores, large specific areas, particularly the π-electrons on the surface, residual –COOH groups during preparation, and moisture absorbed from air (as proved by FTIR), Au3+ cations are able to attach onto the surface of the MWCNTs via electrostatic attraction interactions or strong non-covalent supramolecular interactions.52,53 After the Au3+ ions are reduced, Au NPs are tightly decorated onto the MWCNTs; whereas the heterogeneity of distribution for Au NPs is probably due to the unevenness of the oxygen moieties distribution. Anyway, they are indeed decorated on the surface of MWCNTs, and meanwhile not discovered elsewhere. To further verify the growth of Au NPs on the surface of MWCNTs, the element composition was analyzed using an energy-dispersive X-ray (EDX) spectrometer, as depicted in Fig. S2 of the ESI.† The observed sample was made of gold and carbon elements ascribed to MWCNTs and Au NPs. This manifests how the MWCNTs@Au nanocomposites were prepared via an in situ reduction way. In the TEM image of the MWCNTs@Au-g-PMAEFc nanohybrids in Fig. 3(d), the tubular topologies of MWCNTs can still be observed, but the boundaries between the inside and outside tubes become blurred, and the diameter of the tubes is significantly widened, which is an indicator of MWCNTs coated or covered by polymer matrices. Further observation reveals that there are some spherical grains that are uniformly decorated or scattered on the surface of the MWCNTs or MWCNTs coating with PMAEFc, which is proof of the existence of Au NPs in PMAEFc moieties covering the MWCNTs. EDX was also used to confirm the chemical composition of the nanohybrid sample, as illustrated in Fig. S3 (ESI†). The appearance of the elements C, O, and Fe indicates the formation of PMAEFc covering layers on the surface of MWCNTs, while the element Au is ascribed to the Au NPs. The mass percentages of C, O, Fe, and Au were representatively 78.92%, 10.84%, 2.31%, and 7.93%, which construct the MWCNTs@Au-g-PMAEFc nanohybrid. Considering the strong non-covalent binding of Au NPs with MWCNTs, the grafting PMAEFc moieties also bond with the MWCNTs via strong non-covalent supramolecular interactions.53–55 Therefore, the separation between MWCNTs and the functional polymers does not exist, by and large. Moreover, we did not observe any precipitates at the bottom of the container with the naked eye or by UV-vis transmittance measurements during a considerably long time period.
Fig. 3 TEM images of (a) MWCNTs, (b) Au NPs, (c) MWCNTs@Au nanocomposites, and (d) MWCNTs@Au-g-PMAEFc nanohybrids. |
FESEM was further used to observe the morphological features of the MWCNTs, MWCNTs@Au, and MWCNTs@Au-g-PMAEFc, as depicted in Fig. 6. MWCNTs can be observed to assume a randomly-distributed, intertwined, and jumbled status, with a pipe diameter ranging from about 15 to 20 nm. The Au NPs present uniform spherical morphologies, and give a globular size of approximately 7–13 nm, as demonstrated in Fig. 4(b). These observations are consistent with the results estimated by TEM. In the case of MWCNTs@Au nanocomposites in Fig. 4(c), it can be clearly observed that Au NPs are uniformly decorated and loaded on the surface of MWCNTs along its length, by and large, and form rough surfaces, which is significantly different from the smooth surface of the original pristine MWCNTs. Our observations indicate that Au NPs are in situ deposited onto the MWCMTs. MWCNTs@Au-g-PMAEFc shows a unique morphological trait. A layer of thick polymers is observed to tightly wrap the MWCNTs@Au nanocomposites or MWCNTs, and the pipe diameter of MWCNTs is remarkably thickened. Although the MWCNTs@Au nanocomposites are almost covered with the polymer layer, some Au NPs can be clearly seen to be exposed on the polymer coating layer covering the MWCNTs@Au. A large fraction of Au NPs are wrapped in whole polymer layers. The MWCNTs@Au-g-PMAEFc nanohybrid with this morphology can be well dispersed, and is expected to produce good electrochemical properties via a synergistic effect among these components.
Fig. 4 FESEM images of (a) MWCNTs, (b) Au NPs, (c) MWCNTs@Au nanocomposites, and (d) MWCNTs@Au-g-PMAEFc nanohybrids. |
Fig. 5 UV-vis absorption spectra of (A) various materials and (B) MWCNTs@Au with various mass ratios of MWCNTs to Au NPs in anhydrous ethanol (concentration: 0.01 mg ml−1). |
In consideration of the poor reversibility of the electrochemical process of the aforementioned MWCNTs@Au nanocomposites, the electrochemical properties were modulated by changing the composition ratios of MWCNTs to Au NPs to acquire better redox characteristics, and the results are shown in Fig. 7(B). It can be clearly seen that all the MWCNTs@Au nanocomposites with various component ratios exhibit obvious redox electrochemical properties. With increasing the mass ratios of MWCNTs to HAuCl4·3H2O or the contents of Au NPs, the redox peaks are more obvious, and the peak currents are stronger, offering better electrochemical responsiveness; this is consistent with the increase in the peak intensities in the UV-vis absorption spectra. However, as the contents of Au NPs increase, the potentials of the oxidation peaks and reduction peaks shift for the anodes and cathodes, respectively, and the ΔEp value is increased from about 245 to 303 mV, and the Ip,a/Ip,c ratios decrease from 0.9 to 0.83 and 0.77; this makes the redox process harder, and the reversibility becomes poorer. Clearly, to obtain MWCNTs@Au with superior comprehensive properties, it is necessary to reasonably modulate the composition proportions of the two constituents or the contents of the Au NPs.
The effect of the mass ratios of MWCNTs to Au NPs on the redox electrochemical properties of the nanohybrids was further investigated in Fig. 7(C). It can be noticed that with increasing the content of Au NPs, the symmetry of the redox peaks is increased, and the redox peak currents generated by Au NPs and the grafted ferroncene segments are enhanced, whereby the oxidation peak potentials decrease while the reduction peak potentials increase. This finding further reveals that the covalent interaction between PMAEFc and MWCNTs@Au makes the redox process easily occur, and consequently the nanohybrids bear better electrochemical responsiveness. The redox potentials and ΔEp values of the nanohybrids with various compositional ratios are summarized in Table S1 (ES1†). As the mass percentage of Au NPs is increased in the nanohybrids, the ΔEp values based on Au NPs and ferrocene-containing units gradually decrease, and the peak current ratios of anodes to cathodes Ip,a/Ip,c approach to integer 1, signifying that the prepared nanohybrids possess improved symmetry and reversibility. It is hence deduced that the nanohybrids with excellent electrochemical responsiveness and responsive reversibility can be achieved by modulating the component proportions. In particular, the nanohybrid with the mass ratio of MWCNTs to HAuCl4·3H2O of 1:4 possesses optimized redox properties and electrochemical reversibility.
The effect of the graft percentage of PMAEFc chains on the electrochemical properties of the nanohybrids was examined in Fig. 7(D). In comparison with the oxidation potential of the monomer MAEFc (Epa,Fc = 0.420 V), the oxidation peak potentials of the ferrocene-containing polymers after the graft polymerization decrease to 0.18 V for a low graft percentage and 0.25 V for the graft percentage of 38.0%; this indicates that the ferrocene groups or moieties are more easily oxidized after the graft polymerization. As the chain lengths of the graft ferrocene monomer units increase, the oxidation peak potential Ep,a and the reduction peak potential Ep,c generated by the ferrocene units and Au NPs obviously increase, and shift toward the anodes and cathodes, leading to the enlargement of the peak potential difference from 150 and 195 mV for a low graft percentage to 290 and 350 mV for a high graft percentage. This may be due to the grafting and participation of more PMAEFc redox components, which decreases the rate of mass diffusion and the charge transfer between the active sites, making the redox process become difficult.66 Hence, in spite of these obviously increased redox peak currents with increasing the length of the graft ferrocene chains, the higher ΔEp values make the reversibility of the redox process reduce. Therefore, the nanohybrid with the graft percentage of 8.1% and the mass ratio of MWCNTs to Au NPs of 1:4 was selected as the electrode modified material for use in the detection of trace poisonous and harmful substances in real samples in this study.
Ip,a (μA) = 5.6979(−logC) − 72.6582 (R2 = 0.9916) | (1) |
The limit of detection (LOD) is estimated using three times noise, i.e., signal/noise = 3 (S/N = 3):36
LOD = KSb/r | (2) |
The repeatability of the MWCNTs@Au-g-PMAEFc nanohybrid films for the detection of trichlorfon was assessed by measuring 5 × 10−8 and 5 × 10−7 M trichlorfon response for six successive measurements in the same sample under identical experimental conditions, giving an intra-assay relative standard deviation (RSD) of about 0.67 and 1.21%, respectively. To simultaneously assess the sensor-to-sensor reproducibility, five modified electrodes were individually fabricated and then used to detect the DPV current response at trichlorfon concentration of 2.5 × 10−8 mol L−1, giving an inter-assay relative standard deviation (RSD) of about 1.36%. This suggests that this method has good reproducibility, and the sensor-to-sensor repeatability results are acceptable for the trace detection of trichlorfon. The long-term stability of the electrochemical sensor was evaluated by measuring the electrode response with 2.5 × 10−8 M trichlorfon in PBS of pH 7.0, and the current response of the sensor based on DPV was found to maintain about 95.3% of the initial value after storage for 15 days at 4 °C. The experimental results are displayed in Fig. S5 (ESI†).
To detect pesticide residues in real samples, apple, tomatoes, and cucumber samples of 1.5 g were cut into small pieces and put into a 50 ml beaker, and then immersed in PBS buffer solutions containing trichlorfon concentrations of 0.5 × 10−8, 1.0 × 10−8, 2.0 × 10−8, and 4.0 × 10−8 mol L−1 for 6 h. After the spiked samples were ultrasonicated in a 30 ml PBS solution of pH 7.0 for 1–2 h, they were filtrated through a 0.45 μm filter membrane to obtain extractions. The extractions were then transferred into a 50 ml volumetric flask, and diluted to the scale mark with PBS buffer solution, and then stored at 4 °C. The anodic peak current (Ip,a) of each sample was determined five times by DPV to give a mean value and then to estimate the residual amount in food, the percentage of recovery, and the relative standard deviations, as summarized in Table S2 (ESI†). It is noticed that the nanohybrid modified electrodes bear almost similar data between the measured values and the added amount of trichlorfon residues when they were used to detect a certain concentration of trichlorfon in apple, tomato, and cucumber sample solutions, offering a high recovery of 92.0–101.5%, 89.0–99.0%, and 87.0–102.5% with a low RSD value of 0.9–4.3%, 0.6–6.4%, and 1.6–5.1%, respectively. Consequently, the modified electrode sensor developed in this study was manifested to be a promising and reliable tool for the rapid, convenient, and efficient determination of trichlorfon residues in real samples, for example, food and fruits.
Footnotes |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c8tc05294h |
‡ Xue-Peng Wei and Rui-Qian Zhang contribute equally to this work. |
This journal is © The Royal Society of Chemistry 2019 |