WO2012154028A1 - A phosphate sensor and method of formation thereof - Google Patents
A phosphate sensor and method of formation thereof Download PDFInfo
- Publication number
- WO2012154028A1 WO2012154028A1 PCT/MY2012/000092 MY2012000092W WO2012154028A1 WO 2012154028 A1 WO2012154028 A1 WO 2012154028A1 MY 2012000092 W MY2012000092 W MY 2012000092W WO 2012154028 A1 WO2012154028 A1 WO 2012154028A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- phosphate
- cobalt nanoparticles
- sensor
- phosphate sensor
- cellulose acetate
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Ceased
Links
Classifications
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N27/00—Investigating or analysing materials by the use of electric, electrochemical, or magnetic means
- G01N27/26—Investigating or analysing materials by the use of electric, electrochemical, or magnetic means by investigating electrochemical variables; by using electrolysis or electrophoresis
- G01N27/28—Electrolytic cell components
- G01N27/30—Electrodes, e.g. test electrodes; Half-cells
- G01N27/333—Ion-selective electrodes or membranes
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N33/00—Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
- G01N33/18—Water
- G01N33/1826—Organic contamination in water
- G01N33/184—Herbicides, pesticides, fungicides, insecticides or the like
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N33/00—Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
- G01N33/18—Water
- G01N33/182—Specific anions in water
Definitions
- the present invention relates to a phosphate sensor and a method of formation thereof.
- Phosphate is a frequently analysed substance in the water treatment industry. Phosphate analysis is also common in environmental monitoring, in clinic diagnosis, and in other industrial places such as mining and metallurgical processes.
- Phosphate fertilizers are widely used to increase nutrient level for most crops and lawn plants. When properly applied the inorganic phosphate binds well with soil components, and will not contribute to water pollution. However, inorganic phosphate is commonly applied on soil surface and it is easily washed away to rivers, lakes, drainage and ground water.
- Inorganic and organic phosphate pollutant from fertilizer runoff causes eutrophication in rivers and lakes, where the nutrients cause excessive growth of algae and weeds. This results in oxygen deficiency in the aquatic eco system and makes it unsuitable for fish and other species. Therefore, monitoring of phosphate level in sources of fresh water is important to ensure water quality for drinking, household use, as well as to keep proper balance in the aquatic eco-system.
- a conventional phosphate sensor device comprises a sensing membrane that embeds chemical components in the polymeric matrix.
- An example of the phosphate sensor device is disclosed in US 6,540,894 which relates to a phosphate ion selective electrode, with the detection limit is made small to enable measurement of phosphate ion concentrations of down to low concentration, and a method of manufacturing the abovementioned phosphate ion selective electrode, wherein a sensing membrane of an ion selective electrode A is comprised of a solid membrane having a slightly soluble metal salt as the main component thereof.
- the chemical component of the phosphate sensor of this device tends to leach out, and results in functional failure of the sensor device.
- prolonged exposure in harsh environment causes delamination of the sensing membrane whereby the polymeric matrix is peeled off from the transducer electrode surface of the sensor device.
- the present invention relates to a phosphate sensor (100) for measuring inorganic phosphate anions and a method for producing the phosphate sensor (100).
- the phosphate sensor (100) is characterised by a substrate (160); a conductor layer (140) disposed on the substrate; and a cobalt nanoparticles composite layer (120) disposed on the conductor layer (140).
- the phosphate sensor (100) is suitably used for detecting inorganic phosphate in dibasic inorganic phosphate form.
- the conductor layer (140) is selected from the following materials: screen printed silver, electrode deposited silver, electroplated silver, screen printed carbon, electroplated platinum or a combination thereof.
- the cobalt nanoparticles composite layer (120) is prepared by embedding cobalt nanoparticles in low impedance nano-porous material.
- the cobalt nanoparticles composite layer (120) comprises of 10% to 50% cobalt nanoparticles by weight and 50% to 90% cellulose acetate by weight.
- a method for producing the phosphate sensor (100) includes the steps of preparing and disposing a conductor layer (140) onto a substrate (160); preparing a cobalt nanoparticles-cellulose acetate paste; coating the cobalt nanoparticles- cellulose acetate paste onto the conductor layer (140) to produce the phosphate sensor (100); and characterising the phosphate sensor (100).
- disposing the conductor layer (140) on the substrate (160) comprises the steps of screen printing a silver paste on a substrate (160); and curing the silver paste at approximately 120°C for 30 minutes.
- the cobalt nanoparticles-cellulose acetate paste is prepared by the steps of dissolving and mixing cellulose acetate solution in tetrahydrofuran; stirring the mixture of cellulose acetate solution and tetrahydrofuran under nitrogen atmosphere; and adding cobalt nanoparticles into the mixture with a continuous stirring and under continuous flow of nitrogen gas.
- a method for regenerating an oxidised phosphate sensor (100) comprises the steps of providing the oxidised phosphate sensor (100) as working electrode; providing a reference electrode; providing a platinum rod as a counter electrode; connecting the working electrode, reference electrode and counter electrode into an electrochemical condition; immersing the working electrode, reference electrode and counter electrode into an acidic solution; applying a cyclic voltammetry method; and repeating the cyclic voltammetry method until the oxidised cobalt nanoparticles of the phosphate sensor (100) return to an original uncharged state.
- the acidic solution used for immersing the working electrode, reference electrode and counter electrode is 0.1 M hydrochloric solution.
- the cyclic voltammetry method is suitably swept between 1.2V to 0V for at least once.
- the phosphate sensor of the present invention does not tend to delaminate under prolonged exposure to harsh environment.
- FIGURE 1 illustrates a cross sectional view of a phosphate sensor (100) in accordance to an embodiment of the present invention.
- FIGURE 2 illustrates a flow chart for a method of producing a phosphate sensor (100) in accordance to an embodiment of the present invention.
- FIGURE 3 illustrates a graph plot of an electromotive force (emf) signals versus log activity of dibasic phosphate of a phosphate sensor buffered at pH 8 with reference electrode in calibration solution.
- emf electromotive force
- FIGURE 4 illustrates a cyclic voltammetry graph plot of cobalt nanoparticles-cellulose acetate composite of a phosphate sensor of the present invention in 0.1 M hydrochloric (HCI) solution during regeneration.
- the phosphate sensor (100) comprises of a substrate (160), a conductor layer (140) disposed on the substrate and a cobalt nanoparticles composite layer (120) disposed on the conductor layer (140).
- the conductor layer (140) is of the following materials: screen printed silver, electrode deposited silver, electroplated silver, screen printed carbon, electroplated platinum or a combination thereof.
- the cobalt nanoparticles composite layer (120) is fabricated by embedding cobalt nanoparticles in low impedance nano- porous material.
- nanoparticles generally describes particles with diameters of about 1 to 100 nm.
- Metal nanoparticles can have electromagnetic properties different from the bulk metal. This can be caused by surface effects due to the high surface area to volume ratio.
- Inorganic phosphate anions in water are detected in three forms of ionic and mainly dependent on pH level. Among others, monobasic inorganic phosphate (H 2 P0 4 ), dibasic inorganic phosphate (HP0 4 2 ), and tribasic inorganic phosphate (P0 3 " ).
- the phosphate sensor of the present invention is used to detect inorganic phosphate in dibasic inorganic phosphate form i.e. the predominant species detected at pH 6-8.
- Figure 2 illustrates a flow chart for a method of producing a phosphate sensor (100) in accordance to an embodiment of the present invention.
- a conductor layer (140) is disposed on the substrate (160).
- the conductor layer (140) is disposed on the substrate by screen printing silver paste on a FR4 or PCB substrate and curing the silver paste at approximately 120°C for 30 minutes to give a final dry thickness of 100 pm.
- the silver paste printed on the substrate is shaped in a circular form with 2 to 3 mm diameter and it is printed on copper-gold wire trace of the substrate that is connected to at least one electrical contact for connecting the phosphate sensor (100) with an external circuit.
- the advantage of the screen printed silver paste covering the wire trace is that it minimizes copper corrosion of the wire trace.
- an insulator layer is disposed on the substrate surface while exposing the screen printed silver paste and the electrical contact.
- the insulator layer is suitably made of solder mask paste or red epoxy glue printed on the substrate and cured in the oven at approximately 120°C for 30 minutes. A silver electrode is now ready to be used.
- cobalt nanoparticles composite paste is prepared by mixing cobalt nanoparticles with cellulose acetate (CA) solution in tetrahydrofuran to afford a cobalt nanoparticles-cellulose acetate paste.
- the mixture of cobalt nanoparticles having cellulose acetate comprising of 10 to 50% by weight of cobalt nanoparticles and 50 to 90% by weight of cellulose acetate.
- the cobalt nanoparticles composite paste is prepared by initially weighing, dissolving and adding the cellulose acetate solution into 10 ml tetrahydrofuran in a glass vial to provide a mixture with 5% by weight of cellulose acetate.
- the glass vial is tightly capped and the mixture is magnetically stirred under nitrogen atmosphere for approximately 1 hour until homogenous clear solution is achieved.
- the cobalt nanoparticles are then gradually added into the mixture under continuous stirring to afford 40% weight of cobalt nanoparticles.
- the mixture is magnetically stirred for approximately 3 hours under continuous flow of nitrogen gas to produce the cobalt nanoparticles-cellulose acetate paste.
- cobalt nanoparticles are mixed with cellulose acetate (CA) solution in tetrahydrofuran to afford a thick black paste wherein it comprises 50% by weight of cobalt nanoparticles.
- CA cellulose acetate
- the cobalt nanoparticles-cellulose acetate paste as prepared in step 222 is applied and coated on top of the screen printed silver to completely cover the silver surface of the silver electrode as prepared in step 220. It has to be ensured that no part of the silver material is exposed to the analyte solution when used in measuring the phosphate concentration.
- the electrode coated with cobalt nanoparticles-cellulose acetate paste is dried at ambient temperature under continuous flow of nitrogen gas for approximately 20 minutes to 1 hour to completely dry the paste to produce the phosphate sensor (100).
- the metal nanoparticles coated substrate may be made in a variety of ways, including but not limited to contacting the substrate with a metal nanoparticles composition to give the metal nanoparticles coated substrate.
- a potentiometric measurement and characterization of the phosphate sensor (100) to detect dibasic phosphate ion are tested during this step.
- the phosphate sensor (100) as formed in step 224 and a reference electrode are connected to an ion meter. Both electrodes are immersed in calibration solution of potassium dibasic phosphate buffered by acetic acid at pH 7-8.
- the electromotive force (emf) responses at each calibration solution are recorded and the data are plotted as illustrated in Figure 3.
- Table 1 EMF readings of the phosphate sensor prepared from cobalt nanoparticles composite with dibasic phosphate solutions
- the cobalt nanoparticles of the composite layer (120) of the phosphate sensor (100) are in tendency to be oxidised as shown in the equation below.
- the oxidisation of the cobalt nanoparticles produces potential difference based on the potential of a reference electrode such as silver-silver chloride or chloride reference cell which is shown in the equation below.
- Step 228 illustrates a regeneration step of the oxidised phosphate sensor (100) after it has been used for detecting dibasic phosphate ion.
- a cyclic voltammetry method is used for regeneration of the oxidised phosphate sensor (100) by reducing the oxidised cobalt material of the phosphate sensor (100) to return to an original uncharged state of cobalt as shown in the equation below.
- This method is used to reduce cobalt (II) to cobalt (0).
- the oxidised phosphate sensor (100) is used as the working electrode, whereas silver-silver chloride and platinum rod are used as reference electrode and counter electrode, respectively. All three electrodes are connected in electrochemical condition and immersed in 0.1 M solution of hydrochloric acid and repeated sweeps between -1.2V to 0.0V are performed three to six times as illustrated in Figure 4. After the regeneration treatment, the phosphate sensor (100) is recycled and reused for detection of dibasic phosphate ion.
- Silver paste was screen printed on FR4 or PCB substrate and oven cured at
- Cellulose acetate was weighed and dissolved and added into 10 ml_ tetrahydrofuran in a glass vial to afford 5% solution by weight.
- the glass vial was tightly capped and the mixture magnetically stirred under nitrogen atmosphere for hour until homogenous clear solution was achieved.
- Cobalt nanoparticles were gradually added into the mixture under continuous stirring to afford a thick black paste with 40% cobalt nanoparticles by weight.
- the mixture was magnetically stirred for additional 3 hours under continuous flow of nitrogen gas.
- the cobalt nanoparticles-cellulose acetate composite phosphate sensor used for detecting dibasic inorganic phosphate as described earlier was electrochemically treated to regenerate the oxidized surface.
- the used sensor, double-junction silver- silver chloride reference electrode and platinum counter electrode were immersed in 0.1 M hydrochloric solution and the cyclic voltammetry voltage was repeatedly swept between -1 ,2V and 0V for 3 to 6 times at slow sweep rates to reduce the oxidized cobalt nanoparticles to its original uncharged state.
- the regenerated phosphate sensor is now ready for next use.
- the phosphate sensor (100) can be deployed in the field for measuring plant nutrient levels as well as chemical pollution due to fertilizers run-off to rivers and ground water.
- the phosphate sensor (100) is incorporated into a sensing system that sends data using a transmitter device to a central database.
- the data at the database can be analysed to understand trends and relationship with other parameters such as crop yield, in order to optimize the use of fertilizers and monitor contamination caused by fertilizer run-off.
Landscapes
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Health & Medical Sciences (AREA)
- Pathology (AREA)
- General Physics & Mathematics (AREA)
- Immunology (AREA)
- Physics & Mathematics (AREA)
- Analytical Chemistry (AREA)
- Biochemistry (AREA)
- General Health & Medical Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Electrochemistry (AREA)
- Molecular Biology (AREA)
- Engineering & Computer Science (AREA)
- Food Science & Technology (AREA)
- Medicinal Chemistry (AREA)
- Investigating Or Analyzing Materials By The Use Of Fluid Adsorption Or Reactions (AREA)
- Measurement Of The Respiration, Hearing Ability, Form, And Blood Characteristics Of Living Organisms (AREA)
Abstract
The present invention relates to a phosphate sensor (100) for detecting and measuring inorganic phosphate anions. The phosphate sensor (100) is characterised by a substrate (160), a conductor layer (140) disposed on the substrate, and a cobalt nanoparticles composite layer (120) disposed on the conductor layer (140). A method of forming the phosphate sensor (120) is also provided.
Description
A PHOSPHATE SENSOR AND METHOD OF FORMATION THEREOF
FIELD OF INVENTION
The present invention relates to a phosphate sensor and a method of formation thereof.
BACKGROUND OF THE INVENTION
Phosphate is a frequently analysed substance in the water treatment industry. Phosphate analysis is also common in environmental monitoring, in clinic diagnosis, and in other industrial places such as mining and metallurgical processes.
Phosphate fertilizers are widely used to increase nutrient level for most crops and lawn plants. When properly applied the inorganic phosphate binds well with soil components, and will not contribute to water pollution. However, inorganic phosphate is commonly applied on soil surface and it is easily washed away to rivers, lakes, drainage and ground water.
Inorganic and organic phosphate pollutant from fertilizer runoff causes eutrophication in rivers and lakes, where the nutrients cause excessive growth of algae and weeds. This results in oxygen deficiency in the aquatic eco system and makes it unsuitable for fish and other species. Therefore, monitoring of phosphate level in sources of fresh water is important to ensure water quality for drinking, household use, as well as to keep proper balance in the aquatic eco-system.
A conventional phosphate sensor device comprises a sensing membrane that embeds chemical components in the polymeric matrix. An example of the phosphate sensor device is disclosed in US 6,540,894 which relates to a phosphate ion selective electrode, with the detection limit is made small to enable measurement of phosphate ion concentrations of down to low concentration, and a method of manufacturing the abovementioned phosphate ion selective electrode, wherein a sensing membrane of an ion selective electrode A is comprised of a solid membrane having a slightly soluble metal salt as the main component thereof.
However, the chemical component of the phosphate sensor of this device tends to leach out, and results in functional failure of the sensor device. Moreover, prolonged exposure in harsh environment causes delamination of the sensing membrane whereby the polymeric matrix is peeled off from the transducer electrode surface of the sensor device.
Hence, there is a need to provide a phosphate sensor that obviates from the functional failure of the sensor device due to the delamination of the sensing membrane under prolonged exposure to harsh aqueous environment.
SUMMARY OF INVENTION
The present invention relates to a phosphate sensor (100) for measuring inorganic phosphate anions and a method for producing the phosphate sensor (100). The phosphate sensor (100) is characterised by a substrate (160); a conductor layer (140) disposed on the substrate; and a cobalt nanoparticles composite layer (120) disposed on the conductor layer (140). The phosphate sensor (100) is suitably used for detecting inorganic phosphate in dibasic inorganic phosphate form.
Preferably, the conductor layer (140) is selected from the following materials: screen printed silver, electrode deposited silver, electroplated silver, screen printed carbon, electroplated platinum or a combination thereof.
Preferably, the cobalt nanoparticles composite layer (120) is prepared by embedding cobalt nanoparticles in low impedance nano-porous material.
Preferably, the cobalt nanoparticles composite layer (120) comprises of 10% to 50% cobalt nanoparticles by weight and 50% to 90% cellulose acetate by weight.
A method for producing the phosphate sensor (100) includes the steps of preparing and disposing a conductor layer (140) onto a substrate (160); preparing a cobalt nanoparticles-cellulose acetate paste; coating the cobalt nanoparticles- cellulose acetate paste onto the conductor layer (140) to produce the phosphate sensor (100); and characterising the phosphate sensor (100).
Preferably, disposing the conductor layer (140) on the substrate (160) comprises the steps of screen printing a silver paste on a substrate (160); and curing the silver paste at approximately 120°C for 30 minutes. Preferably, the cobalt nanoparticles-cellulose acetate paste is prepared by the steps of dissolving and mixing cellulose acetate solution in tetrahydrofuran; stirring the mixture of cellulose acetate solution and tetrahydrofuran under nitrogen atmosphere; and adding cobalt nanoparticles into the mixture with a continuous stirring and under continuous flow of nitrogen gas.
A method for regenerating an oxidised phosphate sensor (100) is also provided. The method comprises the steps of providing the oxidised phosphate sensor (100) as working electrode; providing a reference electrode; providing a platinum rod as a counter electrode; connecting the working electrode, reference electrode and counter electrode into an electrochemical condition; immersing the working electrode, reference electrode and counter electrode into an acidic solution; applying a cyclic voltammetry method; and repeating the cyclic voltammetry method until the oxidised cobalt nanoparticles of the phosphate sensor (100) return to an original uncharged state.
Preferably, the acidic solution used for immersing the working electrode, reference electrode and counter electrode is 0.1 M hydrochloric solution.
Moreover, the cyclic voltammetry method is suitably swept between 1.2V to 0V for at least once.
Advantageously, the phosphate sensor of the present invention does not tend to delaminate under prolonged exposure to harsh environment. BRIEF DESCRIPTION OF THE DRAWINGS
The accompanying drawings, which are incorporated in and constitute a part of the specification, illustrate embodiments of the invention and, together with the description, serve to explain the principles of the invention.
FIGURE 1 illustrates a cross sectional view of a phosphate sensor (100) in accordance to an embodiment of the present invention.
FIGURE 2 illustrates a flow chart for a method of producing a phosphate sensor (100) in accordance to an embodiment of the present invention.
FIGURE 3 illustrates a graph plot of an electromotive force (emf) signals versus log activity of dibasic phosphate of a phosphate sensor buffered at pH 8 with reference electrode in calibration solution.
FIGURE 4 illustrates a cyclic voltammetry graph plot of cobalt nanoparticles-cellulose acetate composite of a phosphate sensor of the present invention in 0.1 M hydrochloric (HCI) solution during regeneration. DESCRIPTION OF THE PREFFERED EMBODIMENT
A preferred embodiment of the present invention will be described herein below with reference to the accompanying drawings. In the following description, well known functions or constructions are not described in detail since they would obscure the description with unnecessary detail. In the following specification and the claims which follow, the singular forms "a", "an" and "the" include plural referents unless the context clearly dictates otherwise.
Referring now to Figure 1 , there is shown a phosphate sensor (100) according to an embodiment of the present invention.The phosphate sensor (100) comprises of a substrate (160), a conductor layer (140) disposed on the substrate and a cobalt nanoparticles composite layer (120) disposed on the conductor layer (140). Preferably, the conductor layer (140) is of the following materials: screen printed silver, electrode deposited silver, electroplated silver, screen printed carbon, electroplated platinum or a combination thereof. The cobalt nanoparticles composite layer (120) is fabricated by embedding cobalt nanoparticles in low impedance nano- porous material. The term "nanoparticles" generally describes particles with diameters of about 1 to 100 nm. Metal nanoparticles can have electromagnetic properties different from the bulk metal. This can be caused by surface effects due to the high surface area to volume ratio. Inorganic phosphate anions in water are detected in three forms of ionic and mainly dependent on pH level. Among others,
monobasic inorganic phosphate (H2P04 ), dibasic inorganic phosphate (HP04 2 ), and tribasic inorganic phosphate (P0 3 "). Preferably, the phosphate sensor of the present invention is used to detect inorganic phosphate in dibasic inorganic phosphate form i.e. the predominant species detected at pH 6-8.
Figure 2 illustrates a flow chart for a method of producing a phosphate sensor (100) in accordance to an embodiment of the present invention.
Initially, as in step 220, a conductor layer (140) is disposed on the substrate (160). Preferably, the conductor layer (140) is disposed on the substrate by screen printing silver paste on a FR4 or PCB substrate and curing the silver paste at approximately 120°C for 30 minutes to give a final dry thickness of 100 pm. The silver paste printed on the substrate is shaped in a circular form with 2 to 3 mm diameter and it is printed on copper-gold wire trace of the substrate that is connected to at least one electrical contact for connecting the phosphate sensor (100) with an external circuit. The advantage of the screen printed silver paste covering the wire trace is that it minimizes copper corrosion of the wire trace. Preferably, an insulator layer is disposed on the substrate surface while exposing the screen printed silver paste and the electrical contact. The insulator layer is suitably made of solder mask paste or red epoxy glue printed on the substrate and cured in the oven at approximately 120°C for 30 minutes. A silver electrode is now ready to be used.
Thereon, as in step 222, cobalt nanoparticles composite paste is prepared by mixing cobalt nanoparticles with cellulose acetate (CA) solution in tetrahydrofuran to afford a cobalt nanoparticles-cellulose acetate paste. The mixture of cobalt nanoparticles having cellulose acetate comprising of 10 to 50% by weight of cobalt nanoparticles and 50 to 90% by weight of cellulose acetate. Preferably, the cobalt nanoparticles composite paste is prepared by initially weighing, dissolving and adding the cellulose acetate solution into 10 ml tetrahydrofuran in a glass vial to provide a mixture with 5% by weight of cellulose acetate. Thereon, the glass vial is tightly capped and the mixture is magnetically stirred under nitrogen atmosphere for approximately 1 hour until homogenous clear solution is achieved. The cobalt nanoparticles are then gradually added into the mixture under continuous stirring to afford 40% weight of cobalt nanoparticles. The mixture is magnetically stirred for approximately 3 hours under continuous flow of nitrogen gas to produce the cobalt
nanoparticles-cellulose acetate paste. In a preferred embodiment cobalt nanoparticles are mixed with cellulose acetate (CA) solution in tetrahydrofuran to afford a thick black paste wherein it comprises 50% by weight of cobalt nanoparticles.
In step of 224, the cobalt nanoparticles-cellulose acetate paste as prepared in step 222 is applied and coated on top of the screen printed silver to completely cover the silver surface of the silver electrode as prepared in step 220. It has to be ensured that no part of the silver material is exposed to the analyte solution when used in measuring the phosphate concentration. The electrode coated with cobalt nanoparticles-cellulose acetate paste is dried at ambient temperature under continuous flow of nitrogen gas for approximately 20 minutes to 1 hour to completely dry the paste to produce the phosphate sensor (100). The metal nanoparticles coated substrate may be made in a variety of ways, including but not limited to contacting the substrate with a metal nanoparticles composition to give the metal nanoparticles coated substrate.
In the step 226, a potentiometric measurement and characterization of the phosphate sensor (100) to detect dibasic phosphate ion are tested during this step. The phosphate sensor (100) as formed in step 224 and a reference electrode are connected to an ion meter. Both electrodes are immersed in calibration solution of potassium dibasic phosphate buffered by acetic acid at pH 7-8. The electromotive force (emf) responses at each calibration solution are recorded and the data are plotted as illustrated in Figure 3. Sensor response of the phosphate sensor (100) reaches to near ideal Nernstian behaviour of -22.8 mV/decade for dibasic inorganic phosphate, and with a good correlation coefficient of 0.99 is observed when the phosphate sensor (100) is successfully prepared and calibrated. The emf readings of the phosphate sensor are shown in Table 1. The phosphate sensor (100) is now ready to be used.
[HP04 2 ] m l m 2 m 3 AVG
-1 -11.1 -14.6 -12.3 -12.7
-2 9.3 6.3 5.6 7.1
-3 37.8 26.9 34.4 33.0
M -22.9
C 36.6 r2 0.99
Table 1 : EMF readings of the phosphate sensor prepared from cobalt nanoparticles composite with dibasic phosphate solutions
For measuring and detecting dibasic phosphate ion, the cobalt nanoparticles of the composite layer (120) of the phosphate sensor (100) are in tendency to be oxidised as shown in the equation below. Cobalt (s) ► Cobalt (II) + 2e
The oxidisation of the cobalt nanoparticles produces potential difference based on the potential of a reference electrode such as silver-silver chloride or chloride reference cell which is shown in the equation below.
AgCI (s) ► Ag(s) + 1e
In order for the phosphate sensor to be re-used, the oxidised phosphate sensor (100) is required to be regenerated. Step 228 illustrates a regeneration step of the oxidised phosphate sensor (100) after it has been used for detecting dibasic phosphate ion. A cyclic voltammetry method is used for regeneration of the oxidised phosphate sensor (100) by reducing the oxidised cobalt material of the phosphate sensor (100) to return to an original uncharged state of cobalt as shown in the equation below.
Cobalt (II) + 2e ► Cobalt (s)
This method is used to reduce cobalt (II) to cobalt (0). The oxidised phosphate sensor (100) is used as the working electrode, whereas silver-silver chloride and
platinum rod are used as reference electrode and counter electrode, respectively. All three electrodes are connected in electrochemical condition and immersed in 0.1 M solution of hydrochloric acid and repeated sweeps between -1.2V to 0.0V are performed three to six times as illustrated in Figure 4. After the regeneration treatment, the phosphate sensor (100) is recycled and reused for detection of dibasic phosphate ion.
The following examples are included to provide additional guidance to those skills in the art. These examples are not intended to limit the scope of the invention in any manner.
EXAMPLES
Examples of the experiments conducted for steps 220 to 228 of Figure 2 are described herein below.
1) Preparation of Screen Printed Silver Electrode
Silver paste was screen printed on FR4 or PCB substrate and oven cured at
120°C for 30 minutes to give a final dry thickness of ΟΟμιτι. A round shaped silver electrode with 2 to 3mm diameter was printed on copper-gold wire trace that functions as electrical contact for the phosphate sensor. Small portion of the wire trace overlapped with the silver layer to provide electrical contact but to minimize copper corrosion. Solder mask paste or red epoxy glue was then printed over the whole sensor surface with the sensor window and pin contacts were open to expose the silver circular structure and pin traces. The insulator layer was cured in the oven at 120°C for 30 minutes.
2) Preparation of Cobalt Nanoparticles Composite Paste
Cellulose acetate was weighed and dissolved and added into 10 ml_ tetrahydrofuran in a glass vial to afford 5% solution by weight. The glass vial was tightly capped and the mixture magnetically stirred under nitrogen atmosphere for hour until homogenous clear solution was achieved. Cobalt nanoparticles were gradually added into the mixture under continuous stirring to afford a thick black paste with 40% cobalt nanoparticles by weight. The mixture was magnetically stirred for additional 3 hours under continuous flow of nitrogen gas.
3) Preparation and Characterization of Cobalt Nanoparticles Phosphate Sensor
The cobalt nanoparticles-cellulose acetate paste was applied on top of screen printed silver electrode to completely cover the silver surface. Special care needed to be taken to ensure that no part of the silver material was exposed to the analyte solution. The electrode covered with cobalt nanoparticles-cellulose paste was dried at ambient temperature under continuous flow of nitrogen gas for 1 hour to give a completely dry composite electrode. The cobalt nanoparticles-cellulose composite electrode and a double-junction Ag-AgCI reference electrode were attached to an ion meter and both electrodes were immersed in freshly prepared calibration solutions of potassium dibasic phosphate buffered by acetic acid at pH 7-8. The emf response at each calibration solution was recorded and the data plotted as shown in Figure 3. Sensor response near to ideal Nernstian behavior of -22.8 mV/decade for dibasic inorganic phosphate, and with a correlation coefficient of 0.99 is observed. 4) Regeneration of Cobalt Nanoparticles Composite Sensor Surface by Cyclic Voltammetrv
The cobalt nanoparticles-cellulose acetate composite phosphate sensor used for detecting dibasic inorganic phosphate as described earlier was electrochemically treated to regenerate the oxidized surface. The used sensor, double-junction silver- silver chloride reference electrode and platinum counter electrode were immersed in 0.1 M hydrochloric solution and the cyclic voltammetry voltage was repeatedly swept between -1 ,2V and 0V for 3 to 6 times at slow sweep rates to reduce the oxidized cobalt nanoparticles to its original uncharged state. The regenerated phosphate sensor is now ready for next use.
The phosphate sensor (100) can be deployed in the field for measuring plant nutrient levels as well as chemical pollution due to fertilizers run-off to rivers and ground water. The phosphate sensor (100) is incorporated into a sensing system that sends data using a transmitter device to a central database. The data at the database can be analysed to understand trends and relationship with other parameters such as crop yield, in order to optimize the use of fertilizers and monitor contamination caused by fertilizer run-off. While embodiments of the invention have been illustrated and described, it is not intended that these embodiments illustrated and describe all possible forms of
the invention. Rather, the words used in the specifications are words of description rather than limitation and various changes may be made without departing from the scope of the invention.
Claims
1. A phosphate sensor (100) for measuring inorganic phosphate anions is characterised by:
a) a substrate (160);
b) a conductor layer (140) disposed on the substrate; and
c) a cobalt nanoparticles composite layer (120) disposed on the conductor layer (140).
2. The phosphate sensor (100) as claimed in Claim 1, wherein the conductor layer (140) is selected from the following materials: screen printed silver, electrode deposited silver, electroplated silver, screen printed carbon, electroplated platinum or a combination thereof.
3. The phosphate sensor (100) as claimed in Claim 1, wherein the cobalt nanoparticles composite layer (120) is prepared by embedding cobalt nanoparticles in low impedance nano-porous material.
4. The phosphate sensor (100) as claimed in Claim 1, wherein the cobalt nanoparticles composite layer (120) comprises of 10% to 50% cobalt nanoparticles by weight and 50% to 90% cellulose acetate by weight.
5. The phosphate sensor (100) as claimed in any of the preceding claims, wherein the phosphate sensor (100) is used to detect inorganic phosphate in dibasic inorganic phosphate form.
6. A method for producing a phosphate sensor (100), comprising the steps of:
a) preparing and disposing a conductor layer (140) onto a substrate (160); b) preparing a cobalt nanoparticles-cellulose acetate paste;
c) coating the cobalt nanoparticles-cellulose acetate paste onto the conductor layer (140) to produce the phosphate sensor (100); and d) characterising the phosphate sensor (100).
7. The method as claimed in step (a) of Claim 6, wherein the conductor layer (140) is disposed on the substrate (160) comprising the steps of:
a) screen printing a silver paste on a substrate (160); and b) curing the silver paste at approximately 120°C for 30 minutes.
8. The method as claimed in step (b) of Claim 6, wherein the cobalt nanoparticles- cellulose acetate paste is prepared by the steps of:
a) dissolving and mixing cellulose acetate solution in tetrahydrofuran;
b) stirring the mixture of cellulose acetate solution and tetrahydrofuran under nitrogen atmosphere; and
c) adding cobalt nanoparticles into the mixture with a continuous stirring and under continuous flow of nitrogen gas.
9. A method for regenerating an oxidised phosphate sensor (100) as claimed in Claim 1, comprising the steps of:
a) providing the oxidised phosphate sensor (100) as working electrode; b) providing a reference electrode;
c) providing a platinum rod as a counter electrode;
d) connecting the working electrode, reference electrode and counter electrode into an electrochemical condition;
e) immersing the working electrode, reference electrode and counter electrode into an acidic solution;
f) applying a cyclic voltammetry method; and
g) repeating the cyclic voltammetry method until the oxidised cobalt nanoparticles of the phosphate sensor (100) return to an original uncharged state.
10. The method as claimed in step (e) of Claim 9, wherein the acidic solution is 0.1 M hydrochloric solution.
11. The method as claimed in step (g) Claim 9 wherein the cyclic voltammetry method is swept between 1.2V to 0V for at least once.
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| MYPI2011700071A MY181674A (en) | 2011-05-12 | 2011-05-12 | A phosphate sensor and method of formation thereof |
| MYPI2011700071 | 2011-05-12 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO2012154028A1 true WO2012154028A1 (en) | 2012-11-15 |
Family
ID=47139378
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/MY2012/000092 Ceased WO2012154028A1 (en) | 2011-05-12 | 2012-04-27 | A phosphate sensor and method of formation thereof |
Country Status (2)
| Country | Link |
|---|---|
| MY (1) | MY181674A (en) |
| WO (1) | WO2012154028A1 (en) |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| GB2503689A (en) * | 2012-07-04 | 2014-01-08 | Compact Instr Ltd | Phosphate Detection |
| WO2014177856A1 (en) | 2013-04-30 | 2014-11-06 | Cranfield University | A phosphate sensor, its use and its method of preparation |
| WO2016139218A1 (en) * | 2015-03-02 | 2016-09-09 | Bilfinger Water Technologies Gmbh | Phosphate electrode and a method for determining the phosphate concentration |
| CN114965659A (en) * | 2022-04-20 | 2022-08-30 | 中国科学院空天信息创新研究院 | Method for detecting phosphate concentration and electrochemical sensor |
| US20220326171A1 (en) * | 2019-09-13 | 2022-10-13 | University Of Florida Research Foundation, Inc. | COMBINED ELECTROCHEMICAL PHOSPHATE/pH SENSORS AND SYSTEMS |
| US11959875B2 (en) | 2017-08-11 | 2024-04-16 | Uwm Research Foundation, Inc. | Composition, electrode, and fabrication method for phosphate sensing |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1098502A (en) * | 1993-08-06 | 1995-02-08 | 湖南大学 | Phosphoric acid radical ion-selective electrode and uses thereof |
| US20100035047A1 (en) * | 2008-08-07 | 2010-02-11 | William Marsh Rice University | Metal and metal oxide nanoparticle-embedded composites |
| CN101915793A (en) * | 2010-08-18 | 2010-12-15 | 中国科学院半导体研究所 | Sensor structure integrated with microelectrode array and microfluidic channel and its manufacturing method |
-
2011
- 2011-05-12 MY MYPI2011700071A patent/MY181674A/en unknown
-
2012
- 2012-04-27 WO PCT/MY2012/000092 patent/WO2012154028A1/en not_active Ceased
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1098502A (en) * | 1993-08-06 | 1995-02-08 | 湖南大学 | Phosphoric acid radical ion-selective electrode and uses thereof |
| US20100035047A1 (en) * | 2008-08-07 | 2010-02-11 | William Marsh Rice University | Metal and metal oxide nanoparticle-embedded composites |
| CN101915793A (en) * | 2010-08-18 | 2010-12-15 | 中国科学院半导体研究所 | Sensor structure integrated with microelectrode array and microfluidic channel and its manufacturing method |
Cited By (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| GB2503689A (en) * | 2012-07-04 | 2014-01-08 | Compact Instr Ltd | Phosphate Detection |
| GB2503689B (en) * | 2012-07-04 | 2016-12-07 | Compact Instr Ltd | Phosphate detection |
| WO2014177856A1 (en) | 2013-04-30 | 2014-11-06 | Cranfield University | A phosphate sensor, its use and its method of preparation |
| WO2016139218A1 (en) * | 2015-03-02 | 2016-09-09 | Bilfinger Water Technologies Gmbh | Phosphate electrode and a method for determining the phosphate concentration |
| CN107430084A (en) * | 2015-03-02 | 2017-12-01 | 埃奎塞普特斯集团有限公司 | Phosphate electrode and method for determining phosphate concentration |
| JP2018507423A (en) * | 2015-03-02 | 2018-03-15 | アクセプテンス グループ ゲゼルシャフト ミット ベシュレンクテル ハフツングAqseptence Group Gmbh | Phosphate measuring electrode and method for determining phosphate concentration |
| US11959875B2 (en) | 2017-08-11 | 2024-04-16 | Uwm Research Foundation, Inc. | Composition, electrode, and fabrication method for phosphate sensing |
| US20220326171A1 (en) * | 2019-09-13 | 2022-10-13 | University Of Florida Research Foundation, Inc. | COMBINED ELECTROCHEMICAL PHOSPHATE/pH SENSORS AND SYSTEMS |
| US12270779B2 (en) * | 2019-09-13 | 2025-04-08 | University Of Florida Research Foundation, Inc. | Combined electrochemical phosphate/pH sensors and systems |
| CN114965659A (en) * | 2022-04-20 | 2022-08-30 | 中国科学院空天信息创新研究院 | Method for detecting phosphate concentration and electrochemical sensor |
Also Published As
| Publication number | Publication date |
|---|---|
| MY181674A (en) | 2020-12-31 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| Kabir et al. | Electrochemical phosphate sensors using silver nanowires treated screen printed electrodes | |
| Wang et al. | L-Aspartic acid/L-cysteine/gold nanoparticle modified microelectrode for simultaneous detection of copper and lead | |
| WO2012154028A1 (en) | A phosphate sensor and method of formation thereof | |
| Chow et al. | Voltammetric detection of cadmium ions at glutathione-modified gold electrodes | |
| Karim et al. | Amperometric phenol biosensor based on covalent immobilization of tyrosinase on Au nanoparticle modified screen printed carbon electrodes | |
| Sedaghat et al. | Development of a nickel oxide/oxyhydroxide-modified printed carbon electrode as an all solid-state sensor for potentiometric phosphate detection | |
| Wang et al. | Electrochemical sensor using molecular imprinting polymerization modified electrodes to detect methyl parathion in environmental media | |
| US20230072883A1 (en) | Apparatus and methods for measuring phosphate in water | |
| Alizadeh et al. | Graphite/Ag/AgCl nanocomposite as a new and highly efficient electrocatalyst for selective electroxidation of oxalic acid and its assay in real samples | |
| Alvarez et al. | Cathodic stripping voltammetry of paraquat on a carbon paste electrode modified with amberlite XAD-2 resin | |
| Azizi et al. | Fabricating a new electrochemically modified pencil graphite electrode based on acetophenone (2, 4-dinitrophenyl) hydrazone for determining selenium in food and water samples | |
| Liang et al. | Phytate functionalized multi-walled carbon nanotubes modified electrode for determining trace Cu (II) using differential normal pulse anodic stripping voltammetry | |
| Ghanbary et al. | The development of a new modified graphite pencil electrode for quantitative detection of Gibberellic acid (GA3) herbal hormone | |
| CN101344501A (en) | Screen printing electrode, preparation process and application thereof | |
| Ben Messaoud et al. | Development of electrochemical sensors based on silver nanoparticles electrodeposited on gold screen-printed electrodes: application to nitrate trace analysis in water | |
| CN102636538A (en) | Microelectrode array sensor as well as preparation method and stripping voltmeter detection method thereof | |
| Lakard et al. | Optimization of the structural parameters of new potentiometric pH and urea sensors based on polyaniline and a polysaccharide coupling layer | |
| Lee et al. | A cobalt-coated needle-type microelectrode array sensor for in situ monitoring of phosphate | |
| Inam et al. | Integrated sensor platform for real-time monitoring of nitrate, ammonium, temperature, and pH in aquatic environments | |
| Faisal et al. | Efficient nitrite determination by electrochemical approach in liquid phase with ultrasonically prepared gold-nanoparticle-conjugated conducting polymer nanocomposites | |
| Pal et al. | The detection of mercury, cadium, and arsenic by the deactivation of urease on rhodinized carbon | |
| CN104237361B (en) | Detect Cd based on Cys/graphene modified electrode simultaneously2+、Pb2+Electrochemical method | |
| US20200393400A1 (en) | Electrochemical Sensor for Detection and Quantification of Heavy Metals | |
| Fanta et al. | Differential Pulse Anodic Stripping Voltammetric Determination of Cadmium (II) with N‐p‐Chlorophenyl‐cinnamohydroxamic Acid Modified Carbon Paste Electrode | |
| WO2013109135A1 (en) | A sensor for dissolved ammonia and a process of preparation thereof |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| 121 | Ep: the epo has been informed by wipo that ep was designated in this application |
Ref document number: 12782158 Country of ref document: EP Kind code of ref document: A1 |
|
| NENP | Non-entry into the national phase |
Ref country code: DE |
|
| 122 | Ep: pct application non-entry in european phase |
Ref document number: 12782158 Country of ref document: EP Kind code of ref document: A1 |