A Fully Integrated and Miniaturized Heavy-metal-detection Sensor Based on Micro-patterned Reduced Graphene Oxide.

For this paper, a fully integrated and highly miniaturized electrochemical sensor was designed and fabricated on a silicon substrate. A solvothermal-assisted reduced graphene oxide named "TRGO" was then successfully micro-patterned using a lithography technique, followed by the electrodeposition of bismuth (Bi) on the surface of the micro-patterned TRGO for the electrochemical detection of heavy metal ions. The fully integrated electrochemical micro-sensor was then measured and evaluated for the detection of cadmium and lead-heavy metal ions in an acetic-acid buffered solution using the square wave anodic stripping voltammetry (SWASV) technique. The fabricated micro-sensor exhibited a linear detection range of 1.0 μg L(-1) to 120.0 μg L(-1) for both of the metal ions, and detection limits of 0.4 μg L(-1) and 1.0 μg L(-1) were recorded for the lead and cadmium (S/N = 3), respectively. Drinking-water samples were used for the practical assessment of the fabricated micro-sensor, and it showed an acceptable detection performance regarding the metal ions.

Heavy-metal-ion sensors are significant tools for environmental and food-analysis research because of the severe damage caused by toxic heavy metals to the organ systems of the human body1. Among the known toxic metals, lead and cadmium have received particular recognition due to their toxicity and related environmental pollution2. Low cost electrochemical sensors that can be operated easily have been developed for the detection of these and other heavy metal ions34. Further, the use of square wave anodic stripping voltammetry (SWASV) for heavy-metal-ion detection has gained popularity due to its effective selectivity and high sensitivity56.

In most cases, mercury-film electrodes are preferred for their excellent stripping characteristics in heavy n class="Chemical">metal ions recognition. However, the toxicity of mercury limits the applicability of these electrodes, especially in cases that involve water contact. Recently, the bismuth-film electrode was recognized as a promising substitute to the mercury electrode due to its low toxicity, large cathodic-potential range, and insensitivity to dissolved oxygen78. The sensitivity and low detection limit of bismuth-based electrochemical sensors are inadequate compared with those of conventional techniques such as atomic-absorption spectrophotometry, mass spectrometry, and inductively-coupled-plasma mass spectrometry9. Therefore, the development of a heavy-metal-ion sensor with high sensitivity is significant for point-of-care detection. Previously, a large amount of work has been undertaken regarding electrode-surface modifications to increase the sensitivity of metal-detection methods10111213. Among these works, the graphene-material-based working electrode has emerged as a promising alternative due to its unique thermal, mechanical, and electrochemical properties14.

Recently, reduced graphene oxide (RGO) has received inn class="Chemical">creasing attention due to its applicability for the production of electronics, electrochemical, and biosensors151617. Among different synthesis techniques for RGO, the solvothermal reduction of graphite oxide is the most attractive due to a simple setup for synthesis, sound scalability, and the ability to recover π-conjugation networks at a high temperature and pressure1819. However, several problems arise from the solvothermal process. First, unreacted reducing agent remains on the RGO surface20. To resolve this issue, RGO gel was treated in acidic solution to remove the reduction agent on the RGO sheet21. Second, although RGO film directly patterned with a lithographic process is necessary for the development of high performing and miniaturized electrochemical sensors. A reliable and simple micro-fabrication process has not been developed yet because the solvent used for RGO suspension can be easily reacted with some negative or positive photoresists.

In this work, a simple and reliable micro-fabrication process is developed for the min class="Chemical">cro-patterning of TRGO film without affecting the electrochemical property of the film. An epoxy negative photoresist (SU-8) mold is applied for the lift off process of TRGO due to its good chemical resistance such as being highly resistant to solvents, acids, and corrosive environments2223. After in situ deposition of the bismuth film on the working TRGO/Au electrode, a fully integrated heavy metal ions sensor with three electrodes is developed and characterized using SWASV. The fabricated sensor is small in size, cheap, and reliable in comparison with the existing and commercial sensors. It also provides quick response and full device integration on various substrates.

Results

Design and fabrication of the device

The fabrication sequences of the heavy-metal-ion detection device on a n class="Chemical">silicon substrate are shown in Fig. 1(a). First, three different electrodes were patterned by using the wet-etching technique. Next, the TRGO was patterned in macro-scale on the top of the working electrode using the thick photoresist as a sacrificial layer. Finally, commercial Ag/AgCl paste was screen-printed on the top of the Au electrode surface as a reference electrode24. The gold paste sputtered on the substrate was used as the counter electrode. Photographs of the fabricated device are shown in Fig. 1(b).

Figure 1

(a) Schematic illustration for the fabrication sequences of the micro-patterned TRGO film on the Au electrode and the proposed heavy-metal-detection sensor with three electrodes (working, counter, and reference electrodes); and (b) photomicrograph of fully integrated and miniaturized sensor.

Physical characterization of the TRGO

Figure 2(a) shows the surface morphology of the TRGO/n class="Chemical">Au electrode, whereby it is clearly observed that a rippled crumpling structure is on the TRGO sheets. This crumpling structure is supposedly caused by the reduction of the oxide groups in the RGO sheet.

Figure 2

(a) Scanning-electron images showing the morphology of the TRGO/Au electrode (top and cross-section views); and (b) wide-range XPS spectra of the fabricated TRGO.

An XPS analysis was carried out to determine the functional groups that are contained in the TRGO. The typical C1s spectra for the n class="Chemical">TRGO are shown in Fig. 2(b). Five different peaks indicate a considerable degree of oxidation, corresponding to the carbon atoms in the different functional groups. The peaks are centered at binding energies of 284.58 eV, 285.88 eV, 287.26 eV, 288.71 eV, and 290.74 eV. The peak at 284.58 eV corresponds to the non-oxygenated ring C involved in the C=C bonds for the production of sp2 hybridized carbon. Another peak (285.88 eV) is from the sp3 hybridized carbon and includes the C-C bond. The C in the C-O bonds (287.26 eV) includes hydroxyl and epoxy groups, the C in the C=O bonds (288.71 eV) includes carbonyl groups, and carbolic acids or ester groups are incorporated for the C in the O-C=O bonds (290.74 eV).

Analytical performance of the sensor

Cyclic voltammograms (scan rate = 50 mV/s) of the modified TRGO/n class="Chemical">Au electrode and gold electrode in a 0.1 M KCl solution containing 5 mM [Fe (CN)6]3−/4− are shown in Fig. 3. On the Au electrode, a pair of weak redox peaks was observed. While on the TRGO/Au electrode, a pair of significantly-high peak currents was observed during the CV analysis. The performance of the fabricated sensor can be evaluated by the shapes and positions of the redox peaks in a 0.1 M KCl solution containing 5 mM [Fe (CN) 6]3−/4−. Groups of CV curves were obtained by measuring the current of the TRGO working electrode using the fabricated electrode and a commercial reference electrode. The reference electrode was calibrated against commercial Ag/AgCl (3 M NaCl) electrode (Figure S4). In order to check the stability, we performed cyclic voltammetry over 10 cycles. Figure S5 shows the CV curves of the 1st and 10th cycle. The two CV curves are almost the same. This indicates that the as-fabricated sensor shows good stability. Figure S6 shows the CV curves of the fabricated sensor at different scan rates (25 mV/s, 50 mV/s, 75 mV/s, 100 mV/s). The shapes of all the CV curves are nearly identical and show clear redox peaks. The peaks show regular gradient slopes with increasing scan rates, and there is no obvious potential shift between the peaks. Figure S7 shows the CV curves of the TRGO working electrode before and after the patterning process. These curves are nearly the same, which indicates that the patterning process did not damage the electrochemical performance of the TRGO modified working electrode. In addition, no residues from the SU-8 photoresist were found on the TRGO layer, as clearly shown in the FESEM image in Figure S3.

Figure 3

Cyclic voltammograms of TRGO/Au and Au electrodes in 0.1 M KCl containing 5 mM [Fe (CN)6]3−/4− (Scan rate of 50 mV/s).

Figure 4(a) shows the SWASV of a 200 μg L−1 Cd-and-Pb-ion solution containing 600 μg of L−1 n class="Chemical">Bi ions on different electrodes. The striping peaks on the Bi/TRGO/Au-electrode-based sensor are higher than those on the Au/Bi-electrode-based sensor. This improved performance could be due to the presence of the TRGO, which offers abundant anchor sites for the deposition of heavy metal ions. The as-fabricated Bi/TRGO/Au electrochemical sensor was used for the detection of the Cd and Pb ions.

Figure 4

(a) Stripping voltammograms of Bi/Au and Bi/TRGO/Au in acetate-buffer solution containing 200 μg L−1 of Cd and Pb ions. Effects of the deposition potential for sensing target ions (b), pH value of the test solutions (c), and deposition time for sensing target ions (d) on the stripping-peak current of 200 μg L−1 of Cd and Pb ions. Data are presented with the mean of three replicates.

Figure 4(b) demonstrates the effect of deposition potentials that vary within a range of −1.1 V to −1.6 V on the stripping responses of the Cd and n class="Chemical">Pb ions at a deposition time of 150 s. When the deposition potential changed from −1.1 V to −1.6 V, the peak currents increased tremendously due to the more-complete reductions of the Cd and Pb ions. The highest stripping peak was observed when a −1.4 V deposition potential was used. With further negative shifting of the potential, the stripping response began to decrease gradually due to the enhancement of hydrogen evolution; furthermore, the hydrogen evolution was partially suppressed by the deposition of alloys on the electrode surface. A deposition potential of −1.4 V was therefore selected during the electrochemical analysis of the sensor.

The investigation results for the effect of pH on the determination of the Cd and n class="Chemical">Pb ions are shown in Fig. 4(c). The pH of the buffer solution has an extreme influence on the formation of the bismuth-metal alloy25. As the best signals appeared at pH 4.5, this pH level was used in subsequent experiments.

Figure 4(d) shows the influence of the stripping response on the deposition time within a range of 30 s to 250 s at a deposition potential of −1.4 V. The peak currents increased linearly with the extension of the deposition time. However, when the deposition time became longer than 150 s, the peak-current curve began to inn class="Chemical">crease slightly in relation to the time, and this is probably due to the working electrode-surface saturation. Under the consideration of sensitivity, a determination time of 150 s was selected for the deposition of the ions.

Calibration curves for the simultaneous determination of the Cd and n class="Chemical">Pb ions were investigated under the optimal conditions in 0.1 M of the acetate-buffer solution. Figure 5(a) shows the stripping response of the as-fabricated device without any interference while the concentrations of the target metal ions were simultaneously increased from 0 μg L−1 to 120 μg L−1. The stripping-peak current and the concentrations of the Cd and Pb ions exhibited a favorable linear relationship. For the Cd ion (Fig. 5(b)), the linear-regression equation is calibrated as Icd (current/μA) = 0.01 + 0.045CCd (concentration/μg L−1) (CCd = 0–120 μg L−1), with a correlation coefficient of 0.9828 (R2) and a sensitivity of 0.05 ± 0.01 μA μg−1L. For the Pb ion (Fig. 5(c)), the linear-regression equation is calibrated as Ipb (current/μA) = 0.02 + 0.065Cpb (concentration/μg L−1) (Cpb = 0–120 μg L−1), with a correlation coefficient of 0.9922 (R2) and sensitivity of 0.07 ± 0.01 μA μg−1L. Further, the fabricated micro-sensor also possesses satisfactory detection limits (S/N = 3) of 1.0 μg L−1 for the Cd ion and 0.4 μg L−1 for the Pb ion. The detection limits are lower than those of the other reported works, including the Bi Nps/SPCE detection limits of 5 μg L−1 for the Cd ion and 2 μg L−1 for the Pb ion26, the Bi/Au (with motor) detection limits of 0.7 μg L−1 for the Cd ion and 1.2 μg L−1 for the Pb ion27, and the Bi/ERGNO/SPE detection limits of 0.5 μg L−1 for the Cd ion and 0.8 μg L−1 for the Pb ion28.

Figure 5

(a) Square-wave anodic-stripping voltammograms for different concentrations of Cd and Pb ions with the in-situ-plated Bi/TRGO/Au in 0.1 mol L−1 of acetate-buffer solution (pH 4.5) containing 600 μg L−1 of Bi ion. From bottom to top, 0 μg L−1, 10 μg L−1, 20 μg L−1, 40 μg L−1, 60 μg L−1, 80 μg L−1, 100 μg L−1, and 120 μg L−1. (b,c) Show the corresponding calibration curves of the Cd and Pb ions, respectively. Data are presented with the mean of three replicates.

To evaluate the feasibility of the fabricated sensor for routine analysis, this sensor was applied to detect n class="Chemical">Cd and Pb ions in a drinking-water sample. Figure 6 illustrates the typical stripping voltammograms of the device when used for drinking-water-sample analysis. As shown, the stripping response for three standard additions exhibits good linearity, indicating the viability of the fabricated sensor in real sample analysis. The sensitivities for the Cd and Pb ions are 0.06 ± 0.01 μA μg−1L and 0.05 ± 0.01 μA μg−1L, respectively. The reproducibility of the fabricated micro-sensor was evaluated according to a repetitive measurement of 200 μg L−1 for both ions. The results show that our device is inexpensive and easily fabricated, while a wide range, low detection limit, and high sensitivity are also provided.

Figure 6

Typical stripping voltammograms for the detection of heavy metals in drinking water using the standard addition method under optimized conditions.

The concentration of both Cd and Pb ions for each addition is 50 μg L−1. Inset: corresponding calibration curve. Data are presented with the mean of three replicates.

Discussion

The sound film-forming ability of n class="Chemical">TRGO facilitates large surface coverage on the substrate, which is suitable for the large-scale production of TRGO. FESEM images (Figs S1 and S2) show that the TRGO covered all of the surfaces and is well patterned on the gold-coated substrate from the use of the developed technique. Figure S3 shows the FESEM image of the TRGO/Au surface after lithography. This figure clearly shows that there is no photoresist remaining on the TRGO surface.

According to the XPS-analysis data, the oxygenated peaks are much lower than the non-n class="Chemical">oxygenated peak. These results indicate that a high-quality RGO was developed through the use of the proposed techniques.

In Fig. 3, a pair of weak redox peaks can be observed on the Au electrode, whereas on the n class="Chemical">TRGO/Au electrode, a pair of significantly-high peak currents was found during CV analysis. These results indicate that reaction reversibility is possible in the developed microelectrode and the active surface area is enlarged. Clearly, the improved performance could be attributed to the unique nano-structure29. The CV peaks on the anodic curve are different for Au and TRGO/Au, while they are almost the same on the cathodic curve. This result may be due to the efficient electrocatalytic activity of TRGO, which facilitated the fast electron transfer kinetics30.

The electrochemical behaviors of the Pb and n class="Chemical">Cd heavy metal ions are different in different electrolytes such as HCl, HNO3, HClO4, N2SO4, acetate-buffer solution (NaAc-HAc), and phosphate-buffer solution (Na2HPO4-NaH2PO4). Among these electrolytes, the stripping performances of the Cd and Pb ions in 0.1 M of the acetate-buffer solution are the best due to the occurrence of well-defined peaks with the largest peak current31. To obtain the maximum sensitivity for the detection of heavy metal ions, this work investigated the effects of different parameters in 0.1 M of an acetate-buffer solution containing 200 μg L−1 of the Cd and Pb ions.

The fabricated micro-sensor shows correlation coefficients of 0.9828 and 0.9922 for the n class="Chemical">Cd (Fig. 4(b)) and Pb (Fig. 4(c)) ions, respectively; moreover, the fabricated micro-sensor exhibited satisfactory detection limits of 1.0 μg L−1 and 0.4 μg L−1 for the Cd and Pb ions, respectively. Lower detection limits could be achieved for both of the target metal ions by prolonging the detection time. Drinking-water samples were used to test the suitability of the proposed electrochemical sensor for real-life applications. The sensor exhibited acceptable performance in terms of the detection of both Cd and Pb ions in drinking water.

In conclusion, a working Bi/n class="Chemical">TRGO/Au-modified electrode based on a fully integrated electrochemical sensor was developed and subsequently used for a simultaneous SWASV determination of Cd and Pb ions. The developed sensor exhibited a high and sharp peak current for the target heavy metal ions due to the outstanding properties of the TRGO film and the sound stripping characteristics of the bismuth film. Due to the unique properties of TRGO, the fabricated device exhibited sound sensitivity and high stability with simple and green preparation methods.

Methods

Materials and apparatus

The standard solutions of all of the metals (n class="Chemical">Cd ion, Pb ion, Bi ion), the graphite powder (44-μm size), the β-D (+) glucose, the N, N-dimethylformamide (DMF), the sodium acetate, Ag/AgCl paste (ALS Co, Japan), and the glacial acetic acid were purchased from Aldrich Co. (St. Louis, USA). Acetate-buffer solution (0.1 M) served as the supporting electrolyte for the detection of the heavy metals. Deionized water (resistivity ≥ 18 MΩ.cm) was used for all of the experiments and all of the electrochemical measurements were carried out in a 20 mL cell.

An electrochemical analyzer (Model 660D series, CH Instruments Inc., USA) was used for the electrochemical experiments on the fabricated electrode at room temperature. A three-electrode system, including a fabricated electrode that functioned as a working electrode, was used, while an Ag/AgCl electrode with 3 M of n class="Chemical">NaCl and a flat Pt-bar electrode were utilized as the reference and counter electrodes, respectively. The physical characteristics of the TRGO and the sensor electrodes were investigated using high-resolution XPS and field emission scanning electron microscopy (FESEM).

Synthesis of the TRGO

The graphite oxide was prepared using a modified Hummer’s method32. n class="Chemical">TRGO was synthesized using a modified hydrothermal reduction technique2133. Briefly, 52 mg of the graphite oxide was added to 26 mL of deionized water, followed by ultrasonication for approximately 30 min. The as-prepared mixture solution and 0.1 M of glucose were then mixed and the resultant mixture was allowed to stand for 1 h. Next, the mixture was sealed in a teflon-lined autoclave and maintained at 180 °C for 2 h in a convection oven. When the autoclave had cooled, the as-prepared gel was dispersed again in 1 M of an acetic-acid aqueous solution, after which time it was left for 5 h. Finally, the mixture was washed with doubly-distilled water until a pH of 7 was reached. It was then dried overnight in an oven at 90 °C under a vacuum.

Fabrication of micro-patterned TRGO/Au-based electrochemical sensor

Figure 1(a) shows the fabrication sequence of the proposed micro-sensor. An insulation layer was first deposited on top of the n class="Chemical">silicon substrate. After a Cr and Au film was sputtered on top of the SiO2 layer, it was patterned with three different electrodes using the wet-etching technique. Next, the photolithography technique was used to cover the sample with an SU-8 photoresist, whereby the working electrode was excluded. Then, following drop-casting of 50 μl of the TRGO suspension, the working electrode was dried in the air at room temperature for 2 h. Next, the photoresist was removed from the sample using a PG-remover, and washed away with IPA and deionized water. Finally, Ag/AgCl paste was screen-printed on top of the reference Au electrode and dried at 120 °C for 5 min. Figure 2(b) shows a photograph of the fabricated heavy-metal-ion micro-sensor with the working TRGO/Au electrode.

Measurement procedure

The micro-sensor was applied using an in situ electroplating n class="Chemical">Bi, whereby the fabricated device was immersed in 20 mL of a metal-ion standard solution. The SWASV analyses of the Cd and Pb ions were performed in 0.1 M acetate-buffer solutions in the presence of 600 μg L−1 of Bi3+. The sensing principle for the heavy metal ions using SWASV is shown in Figure S8. The SWASV mode contains a time-controlled electrochemical deposition (Figure S8(a)) and a positively-applied-potential square-wave stripping scan (Figure S8(b)). The parameters are as follows: Edep = 150 s; teq = 20 s; Ebegin = −1.4 V, Eend = −0.4 V, Estep = 5 mV, Eampl = 25 mV, and ƒ = 25 Hz. Prior to the next cycle, a 60 s clean step at 0.1 V was performed to remove the residual bismuth. A magnetic stirrer was used to stir the test solutions during the electrodeposition and cleaning steps.

Additional Information

How to cite this article: Xuan, X. et al. A Fully Integrated and Miniaturized Heavy-metal-detection Sensor Based on Min class="Chemical">cro-patterned Reduced Graphene Oxide. Sci. Rep. 6, 33125; doi: 10.1038/srep33125 (2016).