SENSOR DEVICE WITH BIOPOLYMER-METAL COMPOSITE FILM AND RELATED METHODS

TECHNICAL FIELD

The present disclosure relates to the field of sensors, and, more particularly, to chemical sensors and related methods.

BACKGROUND

Among available analytical methods for water quality monitoring, those based on electrochemistry are considered complementary to the traditional techniques (e.g., inductively coupled plasma (ICP) and atomic absorption spectroscopy (AAS)), promising less expensive and portable instruments. Particularly, square-wave anodic stripping voltammetry (SWASV) sensors with metallic mercury have been developed for heavy metal detection. However, due to the toxicity of mercury, environmentally benign materials that can replace mercury for heavy metal sensing materials may be helpful.

One alternative to mercury electrode materials for microsensors for water quality monitoring is bismuth. This is due to bismuth's ability to form alloys with a variety of heavy metals, wide potential window applicable to electrochemical detection, and low toxicity. Bismuth is a pentavalent post-transition metal, and is one of the pnictogens with chemical properties resembling its lighter homologs being arsenic and antimony.

SUMMARY

Generally, a sensor device for detecting metal may include a substrate, at least one electrode on the substrate, and a biopolymer-metal composite film on the at least one electrode. The biopolymer-metal composite film may comprise a metal and a biopolymer. The sensor device may further comprise circuitry coupled to the at least one electrode and configured to apply a sensing signal to the at least one electrode.

In some embodiments, the biopolymer comprises at least one of a polysaccharide material, a chitosan material, and a chitin material. The metal may comprise at least one of iron, copper, and bismuth.

Additionally, the at least one electrode may include a multi-layer electrode. The multi-layer electrode may include an electrically conductive layer on the substrate, an electrode layer on the electrically conductive layer, and an insulator layer over the electrically conductive layer. The electrode layer may comprise carbon. The electrode layer may include gold. The circuitry may be configured to generate the sensing signal to comprise a SWASV sensing signal. For example, the substrate may comprise a dielectric material, such as a polymer plastic material.

Another aspect is directed to a method for making a sensor device for detecting metal. The method may include forming at least one electrode on a substrate, and forming a biopolymer-metal composite film on the at least one electrode. The biopolymer-metal composite film may include a metal and a biopolymer. The method may comprise coupling circuitry to the at least one electrode. The circuitry may be configured to apply a sensing signal to the at least one electrode.

The forming of the biopolymer-metal composite film on the at least one electrode may include an electrodeposition process. The electrodeposition process may include positioning the at least one electrode and the substrate in a solution. The solution may comprise ions of the metal, and the biopolymer. The electrodeposition process may include applying an electrical current between the at least one electrode defining a cathode and an anode electrode. The forming of the at least one electrode may include a screen printing process.

BRIEF DESCRIPTION OF THE DRAWINGS

FIGS. 1A-1C are images of layer patterns for a sensor device, and FIG. 1D is an image of a sensor device, according to an example embodiment of the present disclosure.

FIG. 2 is a schematic diagram of a method for making an example embodiment of the sensor device, according to the present disclosure.

FIGS. 3A-3C are diagrams of effects of deposition time, amplitude, and frequency, respectively, on the stripping peak currents of Zn²⁺, Cd²⁺ and Pb²⁺ of a bismuth/chitosan-coated carbon electrode in an example embodiment of the sensor device, according to the present disclosure.

FIGS. 4A-4C are diagrams of differential pulse SWASV for Pb²⁺, Cd²⁺ and Pb²⁺, respectively, in 0.1 M acetate buffer during a method for making the sensor device, according to the present disclosure.

FIGS. 4D-4F are diagrams of calibration curves of Pb²⁺, Cd²⁺ and Pb²⁺, respectively, in 0.1 M acetate buffer during a method for making the sensor device, according to the present disclosure.

FIGS. 5A-5D are diagrams of effects of deposition time, amplitude, frequency and deposition time, respectively, on the stripping peak currents of As³⁺ of the iron/chitosan-coated carbon electrode in an example embodiment of the sensor device, according to the present disclosure.

FIGS. 6A-6B are diagrams, respectively, of differential pulse SWASV and a corresponding calibration curve of As³⁺ in 0.1 M acetate buffer at a pH of 4.5 during a method for making the sensor device, according to the present disclosure.

FIG. 7 is a schematic diagram of the sensor device, according an example embodiment of the present disclosure.

FIGS. 8A-8F are schematic diagrams of the sensor device of FIG. 7 during manufacture.

FIG. 9 is a flowchart illustrating a method for making the sensor device of FIGS. 8A-8D, according to an example embodiment of the present disclosure.

FIGS. 10A-10B are microscopic images of an example embodiment of the electrode from the sensor device before and after formation of the biopolymer-metal composite film, respectively.

FIGS. 11A and 11B are diagrams of a SWASV waveform for a three-electrode system illustrating deposition and stripping potentials with time and a voltammogram during a stripping step in an example embodiment of the sensor device, respectively, according to the present disclosure.

FIG. 12 is a diagram of a Fourier-transform infrared spectroscopy (FTIR) spectrum of chitosan deposited on the carbon electrode in 4000 cm⁻¹to 1000 cm⁻¹range in an example embodiment of the sensor device, according to the present disclosure.

FIGS. 13A, 13B, and 13C are diagrams of deposition time, amplitude, and frequency on the stripping peak currents of Zn²⁺ and Pb²⁺ of the biopolymer-coated carbon electrode in an example embodiment of the sensor device, respectively, according to the present disclosure.

FIGS. 14A and 14B are diagrams of SWASV and corresponding calibration curves, respectively, of Zn²⁺ and Pb²⁺ in an example embodiment of the sensor device, according to the present disclosure.

FIG. 15 is a diagram of reproducibility of Zn²and Pb²⁺ detection using the chitosan-coated carbon electrode in an example embodiment of the sensor device, according to the present disclosure.

FIG. 16A is a diagram of simultaneous detection of Zn²⁺ and Pb²⁺ in a tap water environment with SWASV using a biopolymer-coated carbon electrode in an example embodiment of the sensor device, according to the present disclosure.

FIG. 16B is a diagram of calibration curves with error bars for Zn²⁺ and Pb²⁺ for simultaneous detection of Zn and Pb²⁺ in a tap water environment in an example embodiment of the sensor device, according to the present disclosure.

FIGS. 17A and 17B are diagrams of simultaneous detection of Zn²⁺ and Pb²⁺ in mine wastewater and soil wastewater, respectively, using an example embodiment of the sensor device, according to the present disclosure.

DETAILED DESCRIPTION

The present disclosure will now be described more fully hereinafter with reference to the accompanying drawings, in which several embodiments of the invention are shown. This present disclosure may, however, be embodied in many different forms and should not be construed as limited to the embodiments set forth herein. Rather, these embodiments are provided so that this disclosure will be thorough and complete, and will fully convey the scope of the present disclosure to those skilled in the art. Like numbers refer to like elements throughout.

Generally, the brittleness and detachment of conventional microsensors that use bismuth as an electrode is recognized to impose practical problems for industrial applications including for water quality monitoring. The microsensors disclosed herein may provide an approach to this issue. A thin film sensing device may include a substrate, at least one electrode (e.g., planar screen-printed carbon electrode) on the substrate, and a biopolymer-metal composite thin film on the electrode comprising at least one metal intermixed with a polysaccharide, which may be formed by co-electroplating metal and biopolymer on the substrate.

As a biopolymer is water soluble in adjusted pH conditions, it has a high mechanical strength and shows good adhesion to traditional electrochemical surfaces. The co-electroplating of the biopolymer-metal composite thin film prevents detachment problems of metal. In addition, the thin film of the biopolymer-metal composite improves ability to adsorb metal ions and thus increases the sensor detection sensitivity.

The biopolymer-metal composite may comprise integrated chitosan and bismuth, integrated chitosan and iron, integrated chitosan and other metals, which can be used for the simultaneous detection of a variety of heavy metal ions (e.g., Cd, Pb, Zn and As), such as using SWASV. Multiple heavy metal ions can be simultaneously detected including their concentrations with the presence of other ions in mining water, municipal wastewater, soil leachate and drinking water samples.

To form the biopolymer-metal composite on an electrode, a screen-printed carbon electrode can be used, as shown in the carbon patterns 800-803 of FIG. 1. The screen-printed carbon electrode is prepared by screen printing of silver, carbon, and an insulation layer serially on a polymer substrate. Generally, any patterns or configuration of a carbon electrode can be used to form a disclosed biopolymer-metal composition on it. In the screen-printed carbon electrode platform, a carbon electrode exposed with a 2 μm to 10 mm diameter can be used as the working electrode.

A nanostructured biopolymer/metal composite film can be formed by co-electrodeposition on this working electrode, and then patterned to form the biopolymer-metal pattern shown used for in situ determination of multiple heavy metals. The present disclosure also provides a simple electrodeposition method for an integrated biopolymer/metal composite film, which can be used aquatically to monitor the concentration of heavy metal ions, or for in situ analysis of leachate heavy metal ions in water. Although the biopolymer-metal composite is generally described as being deposited by an electrochemical deposition, other deposition methods are also possible, such as sputtering.

The electrolytes used during the electro co-deposition process have a metal ions source and polysaccharide. Polysaccharides, as will be appreciated by those skilled in the art, are polymeric carbohydrate molecules composed of long chains of monosaccharide units bound together by glycosidic linkages, which on hydrolysis give the constituent monosaccharides or oligosaccharides.

Metals that can be sensed comprise iron, copper, or bismuth, but are not limited to these metals. Polysaccharides include but is not limited to chitosan, and chitin. The metal source in an electrolyte is a salt (M_xBy) of a respective metal where, X, Y are numbers, and M is a metal ion of the metals described above, and B is an anion such as NO₃, Cl, or HCO₃. In some cases, salts may not be directly soluble in the low acetic acid solution but can be made soluble by using organic solvent. The organic solvent can compromise glycol, glycerol or any derivatives of these, or other organic solvents.

Different species of metal components in the composite film were used for the detection of different specific heavy metal ions. As an example, an iron based-composite for detecting arsenic and Bismuth-based composite for detecting zinc, cadmium and lead exhibited excellent representativeness and reproducibility for in situ multi heavy metal ions detection in concentrations as low as fraction of ppb.

As noted above, SWASV can be used for the simultaneous detection of a variety of heavy metal ions. SWASV involves adsorption of the analyte on the electrode surface, which is quantified by scanning or applying a square wave scan in the negative or positive direction to give a peak-shaped voltammetric response with an amplitude proportional to the concentration. The excitation signal in square-wave voltammetry comprises a symmetrical square-wave pulse of amplitude E_swsuperimposed on a staircase waveform of step height AE, where the forward pulse of the square wave coincides with the staircase step. The differential current (difference between the forward and reverse currents centered on the redox potential) is then plotted as a function of potential, and the reduction or oxidation of species is measured as a peak or trough. The peak height is directly proportional to the concentration of the electroactive species. Direct detection limits down to the ppb is possible. Square-wave voltammetry provides several advantages because of its excellent speed, enhanced sensitivity and the rejection of background currents.

An example electrode fabrication process for forming a bismuth/chitosan coated microsensor is shown in the diagram 810 of FIG. 2. An electrolyte can be prepared by dissolving 0.1M bismuth nitrate and 24 mg of chitosan in 20 mL of 0.1 M acetic acidy. Then, with a screen-printed carbon electrode as the cathode and embedded carbon electrode as anode, a current (100 mAcm⁻²) was applied between electrodes for 30 s to deposit a bismuth/chitosan film on the carbon electrode surface using a potentiostat, such as the PalmSens EIS (as available from PalmSens Compact Electrochemical Interfaces from BASi Corporation of West Lafayette, Ind.). Other additives, such as glycerol, can be added into the electrolyte to enhance the quality of the co-electrodeposited biopolymer/metal composite film. To form an iron/chitosan coated biosensor, 0.1 M ferric chloride can be substituted for the 0.1M bismuth nitrate described above.

After plating bismuth/chitosan on the electrode, the surface of the carbon electrode is washed with deionized (DI) water to remove any residues on the electrode and then dried. The mechanism of chitosan/bismuth co-electrodeposition process is shown below in Equation (1)-(4), where chitosan is shown as ‘Chi’.

Chi-NH₂+H₃O⁺→Chi-NH₃₊+H₂O (1)

2H₂O+2e⁻→H₂+2OH⁻ (2)

Chi-NH₃⁺+OH⁻→Chi-NH₂+H₂O (3)

Bi³++3e⁻→Bi (4)

Chitosan generally has better dissolvability under acidic condition (Equation (1)) but forms a gel under alkaline condition (Equation (3)). Therefore, the electrochemistry process in Equation (2) was used that consumes the hydrogen ions at the electrode surface and forms a local high pH region that dissolved chitosan from the gel at the local region. At the same time, reaction in Equation (4) is also carried out. By combining the reactions in Equations (3) and (4) at the same time, the chitosan/bismuth composite film is co-electrodeposited on the electrode surface.

The bismuth, iron or other metal-chitosan coated carbon electrode electrodeposition working parameters include varying the deposition time, amplitude, and frequency for initial deposition which were evaluated. FIGS. 3A-3C and diagrams 820-822 show the influence of working on the stripping peak of Zn²⁺, Cd²⁺ and Pb²⁺ ions. Experimentally defined −1.4 and +0.0 V were used as deposition and cleaning potentials, respectively. The peak currents of Zn²⁺, Cd²⁺ and Pb²⁺ increased linearly from 1.2, 0.8 and 0.7 to 4.2, 2.6 and 2.2 μA with prolonged deposition time, respectively. The peak current for Zn²⁺ and Cd²⁺ initially increased with deposition time, then slightly increased after 120 s, probably due to the saturation of Zn²⁺ and Cd²⁺ on the electrode surface in FIG. 3A. In the case of Pb²⁺, after 300 s of deposition time, the increase of peak currents was not significant compared to the currents measured after less than 300 s of deposition time. Thus, 300 s was selected for a deposition time for Zn²⁺, Cd²⁺ and Pb²⁺ measurements.

The amplitude and frequency showed significant effects on the stripping response as shown in FIGS. 3B and 3C. The highest current was observed using 0.1 V amplitude and a 40 Hz frequency. Finally, 0.05 V of pulse amplitude and 20 Hz of frequency were selected for further evaluation of the biopolymer-coated sensor performance for in situ heavy metal detection.

The analytical performance of the bismuth-chitosan-coated carbon electrode was investigated by simultaneous analysis of Zn²⁺, Cd²⁺ and Pb²⁺ concentrations from 1 ppb to 10 ppb in a 0.1 M acetate buffer solution. The deposition time was 300 s with a −1.4 V deposition potential, 0.004 V potential step, 0.5 V amplitude, and 20 Hz frequency. The well-defined sharp peaks for Zn²⁺, Cd²⁺ and Pb²⁺ are located at ca. −1.0, −0.63 and −0.45V, respectively, shown in diagrams 823-828 of FIGS. 4A-4F, and the peak currents were proportionally increased with positive shifts of peak potentials as the concentration of heavy metal ions increase. The SWASV peak currents were obtained with correction to the baseline and then the calibration plots were evaluated from the peak currents. The corresponding calibration plots and correlation coefficients showed R²=0.97, 0.98 and 0.99 for Zn²⁺, Cd²⁺ and Pb²⁺. The limit of detection (LOD) was determined to be 1.5 ppb for Zn²⁺ and 1.5 ppb for Cd²⁺ and 1 ppb for Pb²⁺ for simultaneous analysis.

FIGS. 5A-5D include diagrams 830-833, which show effects of parameters on the stripping peak current of arsenic ion of the iron-chitosan microsensor, the sensor was fabricated by electroplating (100 mA/cm²of current density was used for deposition of the Fe-chitosan electroplating). The effect of different parameters (i.e. deposition potentials, deposition time and frequency) on the stripping peak current in a solution containing 10 ppb of As³⁺ ions. A similar trend of deposition time was observed regarding iron/chitosan sensor compared to bismuth/chitosan. The frequency and amplitude have a significant effect on the stripping response (diagrams 831, 832: FIGS. 5B and 5C). The highest current of 47 μA of amplitude at 0.1 V and 23 μA of frequency at 80 Hz was showed, but the peak had an ambient noise due to amplitude property. Thus, 0.05 V of amplitude and 60 Hz of frequency was chosen to be the conditions for the iron/chitosan sensor.

Deposition potential is generally one of the critical parameters in stripping voltammetry. The currents for stripping of As³⁺ at −0.6 V and above were lower than the ones obtained at −1.4 V. However, the evolution of hydrogen and oxygen at the working electrode at negative potentials more than −1.0 V reduced reproducibility of the measurements. −0.6 V was selected as an appropriate deposition potential, which provides the maximum As³⁺ stripping peak current without hydrogen and oxygen interference.

The SWASV responses of the iron-chitosan sensor to As³⁺ ions were investigated in the range of 1.5 to 7.5 ppb under the conditions defined previously. The well-defined sharp peaks for As³⁺ is located at 0.1 V. The correlations in the range of 1.5 to 7.5 ppb is: I_p=4.7x−2.618 (R2=0.948) and LOD was 1.5 ppb as shown in diagrams 834-835 of FIGS. 6A and 6B.

Conventional bulk sensors may be costly. The disclosed metal-biopolymer coated sensors can decrease the fabrication/production cost per sensor with improved sensitivity due to a synergetic effect of biopolymer on heavy metal holding. A disclosed metal-biopolymer coated sensor is expected to be manufactured at a cost of less $1. Uses for disclosed metal-biopolymer coated sensors include heavy metal ion detection in various water resources (city tap water and well water) and wastewater (industrial, municipal, and mining).

EXAMPLES

Disclosed embodiments of the invention are further illustrated by the following specific experimental examples, which should not be construed as limiting the scope or content of this present embodiments in any way.

To evaluate its accuracy in an example practical application, disclosed bismuth-chitosan and iron-chitosan composite-based sensors were used to the determine Cd²⁺ and Pb²⁺ and As3+ concentrations in real mining wastewater. The LOD in parts per billion (ppb) observed was 0.5 of Cd²⁺, 1 of Pb²⁺ and 3.75 of As in mining wastewater under bismuth/chitosan and Fe/chitosan sensor, respectively. The Relative Standard Deviation of Repeatability (RSD) percentage of the biopolymer coated carbon electrode for consecutive 8 measurements is 2.6% for Cd²⁺ and 4.3% for Pb²⁺, and 2.4% for As³⁺ detection under 4 measurements, suggesting that coating material (e.g., bismuth and ferric) may have enhanced stability of electrodes for heavy metal ion detection in real wastewater.

The results of SWASV determination were compared to those obtained by Cd²⁺, Pb²⁺ and As³⁺ using conventional inductively coupled plasma mass spectrometry (ICP-MS), shown in Table 1 below. It was found that the bismuth-chitosan and iron-chitosan did not have a strong impact on the interference under high dilution of heavy metal ions in mining water and it was possible to detect heavy metal ions in real-time. The appeal of the SWASV method using the bismuth-chitosan and iron-chitosan composite films for Cd²⁺, Pb²⁺ and As³⁺ analysis is its simplicity and rapidity.

TABLE 1

Performance of bismuth/chitosan sensor in mining

wastewater applications

Relative

Limits of

standard
bismuth/
Fe/chitosan

Mining
detection
Reproducibility
deviation
chitosan
Sensor

Recovery

wastewater
(ppb)
(n)
(%)
Sensor
(ppb)
ICP-MS
(%)

Cd²⁺
0.5
8
2.6
106.7 ± 2.1

100
106

Pb²⁺
1
8
4.3
76.2 ± 4.1

70
108.8

As³⁺
3.75
4
2.4

292.7 ± 4.1
300
97.5

Table 1: Performance of Bismuth/Chitosan Sensor in Mining Wastewater Applications

Referring now to FIGS. 7 and 8A-8F, a sensor device 100 for detecting metal is now described. As noted above, the sensor device 100 may be used for in situ detection of metals in fluids (e.g. water). The sensor device 100 illustratively comprises a substrate 101, an electrode 102 on the substrate, and a biopolymer-metal composite film 103 on the electrode. For example, the substrate 101 may comprise a dielectric material, such as a polymer plastic material.

The biopolymer-metal composite film 103 comprises a metal and a biopolymer. In some embodiments, the biopolymer comprises one or more of a polysaccharide material, a chitosan material, and a chitin material. The metal may comprise one or more of iron, copper, and bismuth, for example. The biopolymer-metal composite film 103 may comprise a thin film composite having a thickness in the range of 0.1-20 μm.

The sensor device 100 illustratively includes circuitry 104 coupled to the electrode 102 and configured to apply a sensing signal to the electrode. In the illustrated embodiment, the electrode 102 comprises a single electrode. In other embodiments, the electrode 102 may comprise a plurality of electrodes.

As perhaps best seen in FIG. 8F, the electrode 102 illustratively includes a multi-layer electrode. The multi-layer electrode 102 comprises an electrically conductive layer 108 (e.g. silver, copper, gold, aluminum) on the substrate 101, an electrode layer 105 (e.g. silicon dioxide, polymer dielectric) on the electrically conductive layer, and an insulator layer 106 over the electrically conductive layer. For example, the electrode layer 105 may comprise one or more of carbon and gold.

The sensor device 100 illustratively comprises a counter electrode 107a, and a reference electrode 107b. The counter electrode 107a illustratively comprises an electrically conductive base layer (e.g. silver, copper, gold, aluminum), and a cover layer over the electrically conductive base layer, the cover layer including carbon. The reference electrode 107b may comprise an electrically conductive base layer (e.g. silver, copper, gold, aluminum), and a cover layer over the electrically conductive base layer, the cover layer comprise one or more of silver, and silver chloride. In some embodiments, the circuitry 104 is configured to generate the sensing signal to comprise a plurality of SWASV sensing signals.

As will be appreciated by those skilled in the art, the plurality of SWASV sensing signals is applied to the electrode 102, the counter electrode 107a, and the reference electrode 107b. Advantageously, the sensor device 100 may provide a high number of SWASV sensing operations during a lifetime.

The sensor device 100 illustratively comprises first, second, and third electrically conductive traces 110a-110c respectively coupled on their first ends to the counter electrode 107a, the reference electrode 107b, and the electrode 102. The sensor device 100 illustratively comprises first, second, and third contact pads coupled to second ends of the first, second, and third electrically conductive traces 110a-110c.

Referring now to FIGS. 2, 8A-8F, and 9, a method for making the sensor device 100 is now described, which begins at Block 901 in flowchart 900. The method illustratively comprises forming an electrode 102 on a substrate 101. For example, the forming of the electrode 102 may include a screen printing process, a sputtering process, or a deposition process. (Block 903).

The method illustratively includes forming a biopolymer-metal composite film 103 on the electrode 102. (Blocks 904, 905, 907). The biopolymer-metal composite film 103 includes a metal and a biopolymer.

In an example embodiment depicted in a diagram 810 of FIG. 2, the forming of the biopolymer-metal composite film 103 on the electrode 102 illustratively includes an electrodeposition process (i.e. co-electrodeposition process). The electrodeposition process includes generating the biopolymer-metal solution (e.g., the illustrated chitosan/Bi³⁺). (Blocks 811-813). In this illustrative example, chitosan powder is stirred at 60° C. with acetate acid to produce a chitosan solution. (Blocks 811-812). The chitosan solution is combined with bismuth(III) nitrate to produce a chitosan/Bi³⁺ solution. (Block 813).

The electrodeposition process includes positioning the electrode 102 and the substrate 101 in a solution. (Blocks 814-815, 904). The solution comprise ions of the metal, and the biopolymer. The electrodeposition process includes applying an electrical current between the electrode 102 defining a cathode and an anode electrode (i.e. the illustrated counter electrode 107a). (Block 905).

The method illustratively comprises coupling circuitry 104 to the electrode 102. (Blocks 909, 911). The circuitry 104 is configured to apply a sensing signal to the electrode 102. The method concludes at Block 911.

In the following, an exemplary discussion of an example embodiment of the sensor device is now provided.

INTRODUCTION

Water and soil contamination by heavy metals has gained much attention due to its significant impact on public health. Heavy metal ions (e.g., zinc, copper, cadmium and lead) are used in several industrial applications and are recognized as agents that present various toxic effects to humans, animals and other living organisms. These metals are well-known water pollutants, which are not biodegradable, and have long biological half-lives; hence, they tend to bio-accumulate in higher trophic levels of the food chain. Due to growing rigorous environmental regulations, the legal limits for heavy metals in drinking water (e.g., 5 ppm of zinc [Zn²⁺] and 0.015 ppm of lead [Pb²⁺]) is becoming stricter [1]. Particularly, Pb²⁺leaching from galvanic corrosion and elevation of lead levels in household plumbing systems have increasingly drawn public attention [2]. The lead in drinking water has been regulated by Lead and Copper Rule (LCR) with the permissible Pb²⁺ concentration less than 15 ppb [3] and thus fast and simple detection of lead in drinking water is imperative for public health.

Among currently available analytical methods, environmental monitoring systems based on electrochemistry are considered complementary to the traditional techniques (e.g., Inductively coupled plasma (ICP) and Atomic absorption spectroscopy (AAS)), promising inexpensive and portable instruments [4, 5]. Particularly, square-wave anodic stripping voltammetry (SWASV) based on metallic mercury (Hg) has been well-defined for heavy metal detection. However, due to the toxicity of Hg, environmentally benign materials that can replace Hg for heavy metal sensing materials are highly sought after. One of the most well-studied electrode materials is bismuth due to its ability to form alloys with various heavy metals, wide potential window applicable to electrochemical detection, and low toxicity [6]. Despite the excellent compatibility of bismuth, when fabricating microsensors using bismuth, the brittleness and detachment still impose practical problems for industrial applications [7].

Chitosan is a biopolymer [8] that can form stable chelates with many transition metal ions through its hydroxyl and amino groups. This characteristic can be exploited for the development of electroanalytical procedures to detect heavy metal ions where chitosan is employed as an electrode modifier to adsorb metals ions and improve the sensitivity [9-12]. Furthermore, the useful characteristics of chitosan in terms of electrochemistry for the design of modified electrodes include biocompatibility, a high mechanical strength, good adhesion on traditional electrochemical surfaces, and a relatively low cost, as it is from a renewable resource [13-15]. Chitosan films have been deposited by an ex-situ plating method, particularly, on glassy carbon [16] and screen-printed ink [17], which have been mostly studied due to their high surface to volume ratio, high electron mobility and compatibility to stripping voltammetry for heavy metal detection. However, only single ion detection (primarily Pb²⁺) has been tested and multi heavy metal ions detection was not fully explored. In addition, the sensor performance in terms of real-time and in situ heavy metal detection for effective monitoring and managements of water systems still needs to be studied for field applications [18].

Materials and Methods
A. Preparation of Biopolymer-Coated Electrode

A screen-printed carbon electrode with a 2-mm diameter (RRPE1001C, as available from Pine Instrument Company of Grove City, Pa.) was used as a base (substrate) working electrode. A biopolymer solution was prepared by dissolving 24 mg chitosan in 20 mL of 0.1M acetic acid solution (pH 4.5) and stirred using a magnetic stirrer at 700 rpm for 24 hrs. Then, 5 μL of 0.78 mM chitosan solution was drop casted over the working electrode and completely dried by a heat gun for 4 min. The drop casting and drying process was repeated 4 times which was determined from our preliminary test. Then, the biopolymer-coated carbon electrode was tested using cyclic voltammetry (CV) to confirm the electrochemical properties. The CV scan was performed between −1.2 and 0.0 V at a rate of 50 mV/s using a potentiostat (PalmSens3, as available from PalmSens Compact Electrochemical Interfaces from BASi Corporation of West Lafayette, Ind.). The surface morphology of the biopolymer-coated electrode was investigated under a microscopic observation (Revelation III DIN, Microscope, as available from LW scientific, Inc., Lawrenceville, Ga.). The images 836, 837 are shown in FIGS. 10A-10B (Microscopy images (×400) of chitosan on a modified carbon electrode: image 836 before versus image 837 after chitosan biopolymer coating).

B. Sample Preparation

Analytical grade Lead (II) nitrate and Zinc (II) chloride (Sigma-Aldrich) were used without further purification. A 0.1 M acetate buffer (pH 4.6), prepared by mixing appropriate amounts of acetic acid and sodium acetate, was used to prepare solutions of the supporting electrolyte. The stock solutions of 0.1 M Pb²⁺ and Zn²⁺ were prepared by dissolving the appropriate amount of lead (II) nitrate and Zinc (II) chloride in deionized (DI) water. The real mining wastewater and extraction leachate of heavy metal contaminated soil were obtained Il-gang mine and Yong-san industrial estate in South Korea. All experiments were conducted at room temperature (23° C.) with a relative humidity of 45%.

C. SWASV Procedure

Sensor performance was tested in an electrochemical cell (e.g., Compact Voltammetry Cell-Starter Kit, as available from Pine Instrument Company of Grove City, Pa.). The developed biopolymer-coated carbon electrode was used as a working electrode, a co-planar carbon electrode was used as a counter electrode (e.g., RRPE1001C, as available from Pine Instrument Company of Grove City, Pa.), and a separate Ag/AgCl electrode filled with 3 M KCl (e.g., MI-401, as available from Microelectrodes, Inc., Bedford, N.H.) was used as a reference electrode. The electrochemical cell included a generic mini-USB connector to banana jack cell cables, a cell cap and a cell grip. FIGS. 11A-11B include a diagram 838 of a SWASV waveform illustrating deposition and stripping potentials with time and a diagram 839 of a voltammogram during a stripping step.

First, Pb²⁺ and Zn²⁺ were deposited at −1.2 V vs. Ag/AgCl for 300 s, unless specified otherwise, in 0.1 M acetate buffer (pH 4.6) containing Pb²⁺ and Zn²⁺. After the deposition step, the reduced metals were stripped off by SWASV with step potential of 4 mV, amplitude of 50 mV, and frequency of 20 Hz. The stripping potential was applied in the range of −1.2 V to 0 V. A cleaning step was performed prior to ex-situ electrodeposition by biasing the working electrode at +0.2 V for 30 s. A PalmSens EIS (as available from PalmSens Compact Electrochemical Interfaces from BAST Corporation of West Lafayette, Ind.) was used as a potentiostat for all experiments. All data are expressed as the mean±standard deviation (SD) unless indicated otherwise.

D. Materials Characterization

FTIR spectra were obtained using a Vector-22 FTIR spectrometer (as available from Bruker Corporation of Billerica, Mass.) in the range of 4000 cm⁻¹to 1000 cm⁻¹at a resolution of 2 cm⁻¹. The FTIR spectrum of the chitosan deposited carbon electrode in diagram 840 of FIG. 12 showed the important peaks to identify functional groups. The oscillation of O—H and C—H is observed at 3420 cm⁻¹and 2901 cm⁻¹, respectively. Similarly, stretching vibration of C═O and N—H of the sample is observed at 1629 cm⁻¹and 1558 cm⁻¹, respectively. In the wave number range, 1300 cm⁻¹to 1500 cm⁻¹, two oscillation characteristics were observed at 1461 cm⁻¹and 1372 cm⁻¹which represent CH—OH and CH₂—OH, respectively. The presence of O—H, C—H, C═O, N—H, CH—OH, and CH₂—OH functional groups in the fabricated electrode shows that chitosan was effectively deposited on the carbon electrode [19].

Results and Discussion
A. Optimization of Biopolymer-Coated Carbon Electrode Working Parameters for Detection of Heavy Metal

In order to determine optimal current outputs and peak shapes for detecting Zn²⁺ and Pb²⁺ ions by SWASV, the developed electrodes were tested under different operational conditions which include: varying deposition time, amplitude and frequency for initial deposition of heavy metal ions on the electrode. FIGS. 13A-13B shows the influence of deposition time (diagram 841), amplitude (diagram 842), and frequency (diagram 843) on the stripping peak of Zn²⁺ and Pb²⁺ using the chitosan-coated carbon electrode. Experimentally defined −1.2 and +0.0 V were used as deposition and cleaning potentials, respectively. The peak currents of Zn²⁺ and Pb²⁺ increased linearly from 0.19±0.03 and 0.21±0.02 to 1.31±0.04 and 2.13±0.06 μA with prolonged deposition time, respectively. Although the sensitivity was improved with longer deposition time, it also reduced the upper detection limit due to the surface saturation at high metal ion concentrations [20]. The peak current for Zn²⁺ initially increased with deposition time, then slightly increased after 300 s probably due to the saturation of Zn²⁺ on the electrode surface (diagram 341: FIG. 13A). In the case of Pb²⁺, a linear correlation between peak currents and deposition time until 1500 s was observed. Thus, 300 s was chosen to be the optimal and practical co-deposition time for Zn²⁺ and Pb²⁺ measurements.

The amplitude and frequency showed significant effects on the stripping response (diagrams 842-843: FIGS. 13B and 13C). The highest current was observed using 0.1 V amplitude and a 40 Hz frequency; however, the peaks had ambient noise under those conditions due to amplitude and frequency properties of vibration [21]. Finally, 0.05 V of pulse amplitude and 20 Hz of frequency were selected for further evaluation of the biopolymer-coated sensor performance for in situ Zn²⁺ and Pb²⁺ detection.

B. Detection of Heavy Metals by SWASV

The preliminary test on the detection range of the Zn²⁺ and Pb²⁺ using the developed biopolymer-coated carbon electrode showed the measurement ranges up to 200 ppb for Zn²⁺ and 500 ppb for Pb²⁺, respectively. However, for improving the sensor accuracy in simultaneous heavy metal detection, the analytical performance was evaluated in the lower range between 1 and 10 ppb in a 0.1 M acetate buffer solution. The SWASV responses (diagrams 844, 845) for different concentrations of heavy metal ions are illustrated in FIGS. 14A-14B. In particular, differential pulses are shown for SWASV (diagram 844) and corresponding calibration curves (diagram 845) of Zn2+ and Pb2+ in 0.1 M acetate buffer (pH 4.6). Deposition time is 300 s with a −1.2V deposition potential, 0.004 V potential step, 0.05 V amplitude, and 20 Hz frequency.

Deposition time was 300 s with a −1.2V deposition potential, 0.004 V potential step, 0.025 V amplitude, and 20 Hz frequency. The hydrogen evolution potential and the electrode oxidation potential were observed throughout the applied stripping potentials. The electrolytic hydrogen evolution at around −1.0V and the oxidation of the chitosan electrode at about −0.2 V was determined as shown in FIGS. 14A-14B. The well-defined sharp peaks for Zn²⁺ and Pb²⁺ are located at ca. −0.86 and −0.37V, respectively, (FIGS. 14A-14B) and the peak currents were proportionally increased with positive shifts of peak potentials as the concentration of heavy metal ions increase. The SWASV peak currents were obtained with correction to the base line and then the calibration plots were evaluated from the peak currents. The corresponding calibration plots and correlation coefficients are y=0.268x+0.006 and R²=0.989 for Zn²⁺, y=0.417x+0.192 and R²=0.982 for Pb²⁺ (x: concentration (ppb), y: current (μA)), based on three times of the background noise (S/N=3). LOD were calculated based on the method by Lee et al [22] using calibration curves. LOD was determined to be 0.6 ppb for Zn²⁺ and 1.0 ppb for Pb²⁺ for simultaneous analysis. Compared to a screen-printed bare carbon electrode (using, e.g., RRPE1001C, as available from Pine Instrument Company of Grove City, Pa.) without chitosan coating (LOD: 2-4 ppm), the chitosan biopolymer-coated planar carbon electrode showed greater improvement of LOD (2,000-4,000 times) in Pb²⁺ detection.

Table 2 shows the comparison of the developed biopolymer-coated carbon electrodes with other formerly reported polymer-modified electrodes. The results show that the developed biopolymer-coated carbon electrode using chitosan exhibits an excellent and reliable performance for simultaneous determination of two heavy metal ions compared to limited, single heavy metal detection done by others. This demonstrates the applicability of biopolymer-coated carbon electrode to multiple heavy metal detection in cost-effective manners without using a bulk electrode or Bismuth modification.

TABLE 2

Comparison of heavy metal detection between the

developed biopolymer-coated carbon electrodes and other

materials previously reported.

Detection limit

Measurement
(ppb)
Reproducibility
RSD

Electrode substrate
technique
Zn²⁺
Pb²⁺
(n)
(%)
Ref.

chitosan/carbon
SWASV
—
500
—
—
[16]

nanotubes

film electrodes

chitosan-modified
DPASV
—
0.03
15
7
[17]

screen-printed

carbon electrode

chitosan-modified
DPV
—
60
10
3.5
[23]

glassy carbon

electrode

chitosan-coated
SWASV
1.2
1
30
4.8
This

screen-printed

(Zn²⁺)
study

carbon electrode

5.4

(Pb²⁺)

C. Reproducibility of the Biopolymer-Coated Electrode

A series of repetitive SWASV response measurements for 10 ppb of Zn²⁺ and Pb²⁺ ions in a 0.1 M acetate buffer solution were performed to further evaluate the stability of the biopolymer-coated carbon electrode. SWASV parameters were 300 s of deposition time, −1.2V of deposition potential, 0.004 V of potential step, 0.05 V of amplitude, and 20 Hz of frequency. The biopolymer-coated electrode displayed an excellent relative standard deviation (RSD) and reproducibility compared to previous studies (Table 2). In the previous reports, which used chitosan-coated electrodes [17, 23], the successive measurements with the same electrodes was limited to 15 times when differential pulse anodic stripping voltammetry (DPASV) was used. However, in this study, 30 successive measurements with a stable peak current at 300 s deposition time were recorded by the present biopolymer coated electrode using SWASV (diagram 846: FIG. 15; The reproducibility of Zn²⁺ and Pb²⁺ detection using the chitosan-coated carbon electrode. Both Zn²⁺ and Pb²⁺ concentration was 10 ppb.). Highly reproducible stripping currents were observed, with a RSD of 4.8% for Zn²⁺ and 5.4% for Pb²⁺. Therefore, the biopolymer-coated electrode has demonstrated an excellent stability for repetitive SWASV measurements.

D. Application to a Tap Water and Real Wastewater Environment

The sensor reliability was examined by applying the pre-defined SWASV method for simultaneous measurements of Zn²⁺and Pb²⁺ in a prepared drinking water using a local tap-water in which a certain amount of Zn²⁺ and Pb²⁺ were added (2 to 10 ppb for Zn²⁺ and 0.5 to 10 ppb for Pb²⁺) (diagrams 847, 848: FIGS. 16A-16B; simultaneous detection of Zn²⁺ and Pb²⁺ in a tap water environment: diagram 847 shows SWASV using a biopolymer-coated carbon electrode in a 0.1 M acetate buffer solution (pH 4.6) (background solution was tap-water), and diagram 848 shows calibration curves with error bars for Zn²⁺ and Pb²⁺).

A Zn²⁺ peak could not be obtained for concentrations lower than 2 ppb which may be attributed to the proximity of its stripping peak to the hydrogen evolution background current and/or to a low Zn deposition efficiency (e.g., lower diffusivity of Zn²⁺ compared to Pb²⁺) in water samples [24]. However, the slopes of the standard addition curves were 0.242 μA/μM of Zn²⁺ and 0.359 μA/μM of Pb²⁺ (the range of the spiked concentrations were 2 to 10 ppb for Zn²⁺ and 0.5 to 10 ppb for Pb²⁺) with correlation coefficients 0.983 and 0.987 under the measurement conditions found with the proposed method (SWASV, 300 s deposition time with a −1.2V deposition potential, 0.004 V potential step, 0.05 V amplitude, and 20 Hz frequency). The application results showed that the biopolymer-coated carbon electrode is reliable and suitable for sensitive and selective determination in situ of Zn²⁺ and Pb²⁺ in a real water environment.

To evaluate sensor performance in a real wastewater environment, the biopolymer-coated sensor was tested for the determination of Pb²⁺ in mining wastewater and extraction leachate of heavy metal contaminated soil. First, pre- and post-calibration curves were constructed using the same wastewater by spiking various concentrations of Pb²⁺ between 0 and 2 ppb to the diluted mining wastewater sample and soil leachate sample (diagrams 850, 851: FIGS. 17A-17B; simultaneous detection of Zn²⁺ and Pb²⁺ in a real heavy metal environment: diagram 850 shows mine wastewater, and diagram 851 shows soil waste). The concentrations of Pb²⁺ in the wastewater samples were then determined in several times (Table 3). The results of SWASV determination of Pb²⁺ in the samples were validated using AAS. A relative standard deviation (RSD) and recovery were 4.3% and 108.8% for the mining wastewater and 13.7% and 96% for the soil leachate, respectively, indicating that the developed biopolymer-coated sensor displayed acceptable reproducibility in real environmental samples containing heavy metals. However, the developed sensor showed limitation of Zn²⁺ detection in the wastewater samples probably due to the presence of Cu²⁺ within the samples (e.g., 10.5 ppm for mining wastewater and 38.1 ppm for soil leachate). It is well known that the Cu—Zn intermetallic species, which develop during the deposition step, can interfere with sensor performance [25].

TABLE 3

Heavy metal detection in real environmental samples and sensor performance validation

LOD
No. of

Validation

(ppb)
measurements
RSD
This

Recovery

Sample
Zn²⁺
Pb²⁺
(n)
(%)
study
AAS*
(%)

Mining
—
1
8
4.3
76.2 ± 4.1
ppb
67 ± 0.9
ppb
108.8

wastewater

Soil leachate
—
1
3
13.7
1632 ± 12
ppm
1640 ± 16
ppm
96

*Atomic absorption spectroscopy

CONCLUSION

Biopolymer-coated carbon electrodes were successfully applied for in situ determination of heavy metals using SWASV. The proposed method was able to detect both Zn²⁺ and Pb²⁺ simultaneously with good sensitivity and detection limit. The RSD of the biopolymer coated carbon electrode for consecutive 30 measurements is 4.8% for Zn²⁺ and 5.4% for Pb²⁺ detection, suggesting that biopolymer may have enhanced stability of electrodes for heavy metal ion detection compared to a bare carbon electrode. Using tap water, mining wastewater, and soil leachate samples in which dissolved organic carbon (DOC) and various ionic species are present, the developed biopolymer coated carbon electrode was successfully tested for the detection of heavy metals. The overall results demonstrate that, with its simplicity and rapidity of the measurement, the biopolymer-coated planar screen-printed carbon electrode is applicable to in situ heavy metal analysis in water or on contaminated sites without the need for sample transportation to the laboratory or complex sample preparation steps.

Many modifications and other embodiments of the present disclosure will come to the mind of one skilled in the art having the benefit of the teachings presented in the foregoing descriptions and the associated drawings. Therefore, it is understood that the present disclosure is not to be limited to the specific embodiments disclosed, and that modifications and embodiments are intended to be included within the scope of the appended claims.

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SENSOR DEVICE WITH BIOPOLYMER-METAL COMPOSITE FILM AND RELATED METHODS

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