WO2020215600A1 - 一种痕量磷酸盐与pH联合检测仪及其方法 - Google Patents

一种痕量磷酸盐与pH联合检测仪及其方法 Download PDF

Info

Publication number
WO2020215600A1
WO2020215600A1 PCT/CN2019/106537 CN2019106537W WO2020215600A1 WO 2020215600 A1 WO2020215600 A1 WO 2020215600A1 CN 2019106537 W CN2019106537 W CN 2019106537W WO 2020215600 A1 WO2020215600 A1 WO 2020215600A1
Authority
WO
WIPO (PCT)
Prior art keywords
electrode
phosphate
solution
tested
trace
Prior art date
Application number
PCT/CN2019/106537
Other languages
English (en)
French (fr)
Inventor
梁新强
张楚璇
卢圆圆
王子琬
Original Assignee
浙江大学
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by 浙江大学 filed Critical 浙江大学
Publication of WO2020215600A1 publication Critical patent/WO2020215600A1/zh

Links

Images

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
    • G01N27/302—Electrodes, e.g. test electrodes; Half-cells pH sensitive, e.g. quinhydron, antimony or hydrogen electrodes

Definitions

  • the invention relates to the field of electrochemical detection, in particular to a trace phosphate and pH combined detector and a method thereof.
  • Phosphate is one of the most important inorganic salt components in the ecosystem. It can not only provide necessary nutrients and nutrient elements for agricultural production and the growth and development of animals and plants, but also cause eutrophication pollution to the water environment due to excessive content. Series adverse effects. Therefore, it is very important to develop a fast and sensitive method for detecting phosphate concentration in different environments including water and soil.
  • the current standard laboratory method for phosphate testing is the colorimetric method, that is, a certain proportion of ammonium molybdate, ascorbic acid and antimony (III) are added to the test sample containing orthophosphate, and then a blue phosphomolybdate complex is formed. Compound.
  • the detection limit of this method is 0.01mg L -1 .
  • chromatography, optical fluorescence, and spectrophotometry can also be used for the detection of phosphate, but these technologies require high operator operation during the detection process, and the instrument costs are expensive, which is not conducive to the in-situ detection of phosphate ions .
  • electrochemical detection technology In recent years, with the development of electrochemical detection technology, more and more substances can be quickly and quantitatively detected in situ by electrolysis, potentiometric and conductivity methods. Therefore, the use of electrochemical voltammetry for chemical analysis of phosphate ions has certain market potential.
  • the principle of electrochemical detection of phosphate is mainly based on the complex reaction of phosphate ions and molybdate, which can generate electrochemically active complexes, thereby indirectly obtaining the concentration of phosphate ions.
  • the specific reaction equation (1) is as follows :
  • Inorganic phosphates have different existence forms in aqueous solutions due to different pH Exist in aqueous solution.
  • H 3 PO 4 and H 2 PO 4 - In an acidic environment, it exists in the structure of H 3 PO 4 and H 2 PO 4 - , while HPO 4 2- is its main ionic structure in an alkaline environment.
  • the neutral condition all three forms exist.
  • the pH of the electrolyte solution In order that the response peak current presented in the electrochemical reaction can completely reflect the presence of all soluble phosphate ions in the sample, it is necessary to adjust the pH of the electrolyte solution to the conditions for the orthophosphate activity to be more suitable for the complex reaction. Therefore, if phosphate and pH can be combined with electrochemical detection, electrochemical voltammetry will have a good effect on the detection of trace phosphate ions.
  • the purpose of the present invention is to solve the problems existing in the prior art and provide a trace phosphate and pH combined detector, which can simultaneously detect the pH and phosphate concentration of the solution, and can determine the pH value of the solution in advance. Whether it is strong acid, to ensure the accuracy of phosphate concentration detection.
  • a combined detector for trace phosphate and pH which includes a dual-channel screen-printed electrode.
  • the dual-channel screen-printed electrode is arranged on a substrate with two working electrodes, a reference electrode and a counter electrode.
  • the four electrodes are respectively It is connected to the contact through a wire; the reference electrode and the counter electrode are arranged at intervals, and two symmetrical areas for placing the working electrode are formed between the two working electrodes.
  • the two working electrodes share one reference electrode and one counter electrode; Among the two working electrodes, the surface of the first working electrode is modified with pH-sensitive nanomaterials, and the surface of the second working electrode is modified with phosphate-sensitive nanomaterials.
  • the pH-sensitive nano material is nano metal oxide.
  • the nano metal oxide includes nano-scale ruthenium dioxide, nickel oxide, manganese oxide, cobalt oxide, lead oxide and titanium oxide.
  • the phosphate-sensitive nanomaterial is ZrO2-ZnO/multi-wall carbon nanotube/ammonium heptamolybdate tetrahydrate nanocomposite, and its preparation method is as follows:
  • the modification solution is applied to the surface of the second working electrode by dripping and drying.
  • the pretreatment process of the multi-walled carbon nanotubes is: reflux the multi-walled carbon nanotubes in concentrated HNO3 for 5 hours.
  • the wiring is a conductive silver layer
  • the working electrode is a carbon electrode
  • the reference electrode is an Ag/AgCl electrode or a carbon electrode
  • the counter electrode is a platinum wire electrode or a silver electrode.
  • the substrate mentioned is a PET substrate.
  • Another object of the present invention is to provide a combined detection method of trace phosphate and pH using the detector of any one of the above solutions, which is used to simultaneously detect the pH and phosphate concentration of the solution to be tested, and the steps are as follows:
  • Another object of the present invention is to provide a combined detection method of trace phosphate and pH using the detector of any one of the above solutions for detecting the concentration of phosphate in the solution to be tested, and the steps are as follows:
  • step 2) Add the test solution in step 1) quantitatively to the surface of the three-electrode system containing the first working electrode, and detect the pH value of the test solution by electrochemical method to confirm that the solution pH is ⁇ 1;
  • the pretreatment of the sample solution to be tested is determined according to actual conditions. For example, water samples need to be filtered in advance and the filtrate is used for subsequent testing. However, if the sample to be tested is a soil sample, the phosphate in the soil sample needs to be extracted in advance.
  • the specific steps are: dry the soil sample and sieve it, add it to the centrifuge tube quantitatively, use acetic acid as the extractant, and perform shaking extraction ; Use an ultracentrifuge for solid-liquid separation of the extract, and filter the supernatant after centrifugation as the sample solution to be tested.
  • the time for the shaking extraction is preferably 1 h.
  • the acetic acid concentration is preferably 0.50 mol L -1 .
  • the beneficial effect of the present invention is to provide a trace phosphate and pH combined detector, which has a dual-channel screen printing electrode and can be used as a portable device to independently perform two independent pH and phosphate detections.
  • the test proved that in a strong acid environment, phosphate can be converted to the form of orthophosphate to the greatest extent, and then form the form of phosphomolybdate complex to undergo subsequent redox reactions. Therefore, the combined detector can be used in the detection Before phosphate ions, determine in advance whether the pH value of the solution to be tested is strongly acidic to reduce measurement errors.
  • a new type of modified material ZrO 2 -ZnO/MWCNTs composite nano material is used for the detection of phosphate ions.
  • ZrO 2 -Zn composite nanoparticles have a large specific surface area and abundant hydroxyl functional groups.
  • the material after doping with multi-walled carbon nanotubes shows good conductivity.
  • the working electrode is complexed with phosphomolybdate during the potential scanning process.
  • the material exhibits excellent sensitivity, selectivity and stability.
  • the formation of the characteristic redox peak and its current peak effectively prove the occurrence of the complex reaction of the phosphate and molybdate and the content of the reaction product, thereby indirectly obtaining the corresponding added concentration of the phosphate ion.
  • the beneficial effect of the present invention is to provide a combined detection method of trace phosphate and pH.
  • a new type of modified material ZrO 2 -ZnO/MWCNTs/AMT composite nanomaterial is provided.
  • ZrO 2 -Zn composite nanoparticles have a large specific surface area and abundant hydroxyl functional groups.
  • the material after doping with multi-walled carbon nanotubes shows good conductivity.
  • the working electrode is complexed with phosphomolybdate during the potential scanning process.
  • the material exhibits excellent sensitivity, selectivity and stability.
  • the formation of the characteristic redox peak and its current peak effectively prove the occurrence of the complex reaction of the phosphate and molybdate and the content of the reaction product, thereby indirectly obtaining the corresponding added concentration of the phosphate ion.
  • Figure 1 is a schematic diagram of the structure of a combined trace phosphate and pH detector of the present invention
  • Figure 2 is a design diagram of a dual-channel wire mesh electrode screen in the present invention.
  • Figure 3 is a scanning electron microscope image of different materials in the present invention
  • (A)-(C) are ZrO 2 -ZnO nanocomposites (A), ZrO 2 -ZnO individually modified screen printing electrodes (B) and ZrO 2- ZnO/MWCNTs/AMT composite modification screen printed electrode surface (C);
  • Figure 4 shows the cyclic voltammetry of ZrO 2 -ZnO/MWCNTs/AMT composite modified electrode with 3.7 ⁇ 10 -7 ⁇ mol L -1 H 2 PO 4- (a) and without H 2 PO 4- (b) Electrochemical behavior (-0.067v is the oxidation peak of molybdenum valence change).
  • the core structure of a combined trace phosphate and pH detector in this embodiment is a dual-channel screen-printed electrode.
  • the dual-channel screen-printed electrode is arranged with two working electrodes, a reference electrode and a counter electrode on the substrate, and the four electrodes are respectively connected with the contacts through wires.
  • the reference electrode is formed by two 1/4 circles tangentially connected, and the counter electrode is formed by two 1/2 circles tangentially connected.
  • the reference electrode and the counter electrode are arranged at a certain distance, and the two are clamped to form two A mirror-symmetrical area where the working electrode is placed.
  • Two working electrodes share a reference electrode and a counter electrode to form two three-electrode systems.
  • the two working electrodes can be divided into a first working electrode and a second working electrode.
  • the surface of the first working electrode is modified with pH-sensitive nanomaterials, and the surface of the second working electrode is modified with phosphate-sensitive nanomaterials.
  • the first working electrode can be used for pH detection; the second working electrode can be used for phosphate detection, and the two can be used for two independent pH and phosphate detection.
  • the wiring is a conductive silver layer
  • the working electrode is a carbon electrode
  • the reference electrode is an Ag/AgCl electrode (carbon electrode can also be used)
  • the counter electrode is platinum Wire electrodes (silver electrodes can also be used)
  • the substrate is a PET substrate.
  • the printed electrode requires four screens in the printing process, which are conductive silver layer, carbon electrode, Ag/AgCl reference, platinum wire electrode and insulating layer. The screen design is shown in Figure 2. The modification materials on the two working electrodes can be selected as required.
  • pH-sensitive nanomaterials can be nano metal oxides, including nano-scale ruthenium dioxide, nickel oxide, manganese oxide, cobalt oxide, lead oxide, and titanium oxide, etc.
  • the modification process can be any feasible in the prior art. Ways to achieve, such as spraying, doping, etc.
  • Phosphate-sensitive nano-materials can also use existing phosphate-sensitive membranes in the prior art as required.
  • the ZrO 2 -ZnO/MWCNTs/AMT nanocomposite material in the subsequent embodiments is only one of the preferred implementation methods.
  • the first working electrode can be used to detect the pH of the original solution to be tested, and can also be used to detect the pH of the acidified solution to be tested to ensure that the solution to be tested added to the surface of the second working electrode is strong.
  • the response peak current presented in the electrochemical reaction can completely reflect the presence of all soluble phosphate ions in the sample. Therefore, based on the above detector, two methods of use can be designed.
  • the first combined detection method of trace phosphate and pH is used to simultaneously detect the pH and phosphate concentration in the solution to be tested.
  • the method is as follows:
  • the second combined detection method of trace phosphate and pH is used to accurately detect the concentration of phosphate in the solution to be tested.
  • the method is as follows:
  • step 2) Add the test solution in step 1) quantitatively to the surface of the three-electrode system containing the first working electrode, and detect the pH value of the test solution by electrochemical method to confirm that the pH of the solution is ⁇ 1. If the pH is less than or equal to 1, proceed to the next step, otherwise, continue to add acid to lower the pH according to the pH.
  • test solution with pH ⁇ 1 is quantitatively dropped on the surface of the three-electrode system containing the second working electrode, using cyclic voltammetry or square wave voltammetry (considering the peak of trace phosphate, square wave is preferred Voltammetry) conduct potential scanning to obtain the redox peak current of the phosphomolybdate complex; according to the linear relationship between the current and the phosphate concentration, the phosphate concentration in the sample solution to be measured is converted.
  • the first method is suitable for situations where the pH and phosphate concentration of the sample need to be measured simultaneously.
  • the second method is suitable for in-situ rapid quantitative detection of phosphate concentration in the field environment. It is impossible to accurately determine the pH of the water sample to be tested in a non-laboratory environment, and the pH of the water sample body is fluctuating, so the amount of acid cannot be added. Accurate control. In addition, the phosphate itself in the water sample is a trace amount. If it is lower than the detection limit, it may be necessary to increase the mixing ratio of the water sample and the electrolyte, which is likely to cause insufficient acidity of the mixed solution. However, through the combined trace phosphate and pH detector of the present invention, it can be determined that the test solution is already in a strong acid environment when it is added to the second working electrode, so as to ensure the accuracy of the measurement result.
  • the linear relationship between the current and the phosphate concentration can be obtained by measuring different dihydrogen phosphate ion H 2 PO 4- standard solutions in the same method.
  • the sample solution to be tested can be directly dripped on the surface of the second working electrode for cyclic voltammetric determination, or the sample solution to be tested can be dripped on the surface of the second working electrode first, and then it can be dried. Then drop the strengthened acid electrolyte solution for measurement. If the concentration of phosphate in the sample is too low, the test solution containing phosphate is first dropped quantitatively on the working electrode, dried and then placed in the electrolyte solution for potential scanning, which is a preferred and recommended method. This is because the detected phosphate is a trace amount, and it is not easy to produce peaks when directly mixed in the electrolyte using cyclic voltammetry for potential scanning.
  • test solution After pre-drying, it is placed in an electrolyte solution for potential scanning, which can better produce peaks and improve measurement accuracy. However, pre-drying will prolong the detection time, so it is not recommended for mass sampling.
  • the test solution can also be quantitatively mixed with the electrolyte solution, and then the mixed solution can be directly added dropwise to the three-electrode system or the three-electrode system is placed in the mixed solution, using square wave voltammetry potential Scanning is easier to produce peaks than cyclic voltammetry.
  • a phosphate-sensitive nanomaterial namely ZrO2-ZnO/multi-wall carbon nanotubes/ammonium heptamolybdate tetrahydrate is further provided (ZrO 2 -ZnO/MWCNTs/AMT) nanocomposite materials.
  • the process of preparing ZrO 2 -ZnO/MWCNTs/AMT nanocomposite is as follows:
  • the white precipitate produced by the filtration was repeatedly washed with deionized water and ethanol, and placed in an oven and dried at 100°C. After the precipitate is completely dried, put the solid precipitate in a muffle furnace, heat up to 350°C at a rate of 25°Ch -1 and heat at a constant temperature for 1 hour, and then continue to heat to 450°C at the same heating rate for high temperature oxidation for 1 hour . After the solid is completely cooled, a ZrO 2 -ZnO nanocomposite material is obtained.
  • the modification solution used it may be dispensed onto the working electrode surface, to obtain ZrO 2 -ZnO / MWCNTs / AMT composite modified screen-printed electrodes (ZrO2-ZnO / MWCNTs / AMT / SPE) after drying.
  • the composition and diameter of the JSM-5600LV scanning electron microscope were used to observe them.
  • the morphology of the ZrO 2 -ZnO nanocomposite and the structure before and after doping with multi-walled carbon nanotubes on the modified electrode were characterized.
  • Figure 3(A) is a scan of the ZrO 2 -ZnO nanocomposite
  • the electron microscope image shows that when Zn(Ac) 2 and ZrOCl 2 are mixed in an acetic acid solution containing 2.0wt% chitosan at a mass ratio of 1:1, a uniform nanorod structure will be formed after high temperature calcination, and the nanometer The rod length is in the range of 300-500nm, and the width from the tip to the bottom is about 100nm.
  • Figure 3(B) shows that when the ZrO 2 -ZnO nanocomposite is modified on the surface of the screen-printed electrode alone, its structure is compared with the previous unmodified material. After ultrasonic vibration and other treatments, the nanoparticle morphology has changed.
  • the dispersion density of nanorods is more uniform, and the specific surface area is also increased to a certain extent.
  • This change effectively promotes the increase of the diffused sites of the adsorbate.
  • the scanned image in Figure 3(C) shows that the surface of each carbon nanotube is coated with ZrO 2 -ZnO composite nanoparticles.
  • This structure can not only be used
  • the high affinity of ZrO 2 -ZnO nanocomposite to phosphate ions can also rely on the high conductivity of multi-walled carbon nanotubes to improve the reaction rate and degree of phosphomolybdate ion redox reaction.
  • the prepared ZrO 2 -ZnO/MWCNTs/AMT composite modified electrode was subjected to cyclic voltammetry electrochemical analysis and detection.
  • an integrated three-electrode system is used in the electrochemical analysis and detection: ZrO 2 -ZnO/MWCNTs/AMT/SPE is used as the working electrode, and the carbon electrode and the silver electrode are respectively used as the reference electrode and the counter electrode.
  • the three-electrode system is placed in the electrolyte solution at room temperature, and the potentials -1.0V, +1.0V and- 1.0V is the starting point, the highest point and the end potential of the potential scan respectively, and the scan rate is maintained at 50mVs -1 . It also provided the 3.7 ⁇ 10 -7 ⁇ mol L -1 dihydrogen phosphate ion H 2 PO 4 was not added - control standard solution, the same electrochemical analysis and detection.
  • the oxidation peak response current generated at the potential of -0.067V will increase with the increase of the phosphate ion concentration, so this reaction indirectly provides a feasible solution for the detection of inorganic phosphate ions by electrochemical technology, namely According to the linear relationship between the current and the phosphate concentration, the phosphate concentration in the sample solution to be tested is converted. Since the oxidation peak only appears when the electrode surface is loaded with phosphate ions, the electrode has good detection selectivity.
  • the electrochemical detection and analysis of phosphate occurs when the electrode surface potential changes from negative to positive to negative.
  • the salt compound centered on molybdenum is pre-complexed with the phosphate to generate electrochemically active phosphomolybdic acid Salt complex, the substance is forced to undergo a redox reaction to generate a response peak signal.
  • the ratio of Mo/H + content in this reaction is controllable, and the test environment must be strongly acidic.
  • the sample solutions to be tested in Examples 1 and 2 are all aqueous solutions, which can be directly used to detect the phosphate content in water samples. But if you need to determine the phosphate content in the soil sample, you need to extract the inorganic phosphate ions in the soil sample in advance. The following is based on the use of the integrated three-electrode system in Example 2 to optimize the extraction parameters to ensure that the content of inorganic phosphate in the soil sample is reflected on the cyclic voltammetry curve to the greatest extent. Therefore, the best extracting agent needed not only completely dissolves the phosphate, but also the ions contained in it will not interfere with the detection result, that is, it will not affect the potential current value of the redox peak. In this embodiment, four extractants, acetic acid, sodium bicarbonate, potassium sulfate, and MES buffer are used as extractant candidate solutions.
  • the solid-liquid separation was carried out using an ultracentrifuge (5000 rpm, 20 minutes, 25°C). Re-filter the centrifuged liquid and transfer it to a 25mL centrifuge tube, and store it in a 4°C environment before the sample is tested.
  • an ultracentrifuge 5000 rpm, 20 minutes, 25°C.
  • the test results show that the preferred order of extractant is HAc>NaHCO 3 >K 2 SO4>MES.
  • Acetic acid solvent is the best extraction agent.
  • the cyclic voltammetry curve formed by the phosphate ion extracted with acetic acid in the potential scanning stage is complete, and there is a clear redox peak, and the response signal is also very strong.
  • the extraction time the final detection effect is shown to be the best when the shaking extraction time is 1 hour. Therefore, the optimal conditions for soil shaking extraction are: 0.50mol L -1 acetic acid is used as the extractant, and the shaking extraction time is set to 1h.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Physics & Mathematics (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • Molecular Biology (AREA)
  • Analytical Chemistry (AREA)
  • Biochemistry (AREA)
  • General Health & Medical Sciences (AREA)
  • General Physics & Mathematics (AREA)
  • Immunology (AREA)
  • Pathology (AREA)
  • Investigating Or Analyzing Non-Biological Materials By The Use Of Chemical Means (AREA)

Abstract

一种痕量磷酸盐与pH联合检测仪及其方法，属于电化学领域。检测仪包括双通道丝网印刷电极，双通道丝网印刷电极在基板上布置有两个工作电极、一个参比电极和一个对电极，四个电极分别通过接线与触点相连；参比电极和对电极间隔布置，两者之间夹持形成两个放置工作电极的区域，两个工作电极共用一个参比电极和一个对电极；两个工作电极中，第一工作电极表面修饰有pH敏感纳米材料，第二工作电极表面修饰有磷酸盐敏感纳米材料。该联合检测仪可以同时检测溶液的pH和磷酸盐浓度，可通过预先确定溶液pH值是否为强酸性，确保磷酸盐浓度检测的准确性。能对磷酸盐和pH实现原位检测，具有灵敏性稳定性和再现性。

Description

一种痕量磷酸盐与pH联合检测仪及其方法 技术领域
本发明涉及电化学检测领域，具体涉及一种痕量磷酸盐与pH联合检测仪及其方法。
背景技术
磷酸盐是生态系统中最重要的无机盐成分之一，它既能对农业生产以及动植物生长发育提供必要的养分及营养元素，也会因含量超标而对水环境造成富营养化污染等一系列不良影响。因此，对研发一种能够针对不同环境包括水体、土壤进行快速、灵敏磷酸盐浓度检测方法是十分关键的。
目前关于磷酸盐的检测实验室标准方法为比色法，即一定比例的钼酸铵、抗坏血酸和锑(III)依次加入含有正磷酸盐的待测样品中，随后形成蓝色磷钼酸盐络合物。该方法其最低检出限为0.01mg L -1。此外，色谱法、光学荧光法以及分光光度法也可用于磷酸盐的检测，但这些技术在检测过程中对于工作人员的操作要求较高，且仪器成本昂贵，不利于磷酸盐离子的原位检测。
近些年，随着电化学检测技术的发展，越来越多的物质通过电解法，电位法及电导法得到原位快速定量的检测。因此，利用电化学伏安法对磷酸盐离子进行化学分析具有一定的市场潜力。电化学检测磷酸盐的原理主要是基于磷酸根离子和钼酸盐的络合反应，能够生成具有电化学活性的络合物，从而间接获得磷酸根离子的浓度，其具体反应方程式(1)如下：
Figure PCTCN2019106537-appb-000001
络合物中的[PMo 12O 40] 3-具有良好的电化学活性，其被吸附在工作电极表面后，在循环伏安法中以Mo为中心的离子会在电位变化的驱动下发生氧化还原反应，从而在扫描图像中呈现明显的氧化还原峰峰形(方程式2)，这种新型电化学检测方案相比目前普遍使用的无机磷比色测定法检测限更低、检测速度更快。
H 3PMo(VI) 12O 40+还原剂→[H 4PMo(VI) 8Mo(V) 4O 40] 3-    (2)
无机磷酸盐在水溶液中由于pH不同而有不同的存在形态
Figure PCTCN2019106537-appb-000002
Figure PCTCN2019106537-appb-000003
存在于水溶液中。在酸性环境下以H 3PO 4、H 2PO 4 -的结 构存在，而HPO 4 2-则为其在碱性环境中的主要离子结构，至于中性条件下，三种形式都有存在。为了使电化学反应中呈现的响应峰电流可以完全反应样品中所有可溶性磷酸盐离子的存在，将电解质溶液pH调节至正磷酸盐活性较适合发生络合反应的条件是十分必要的。因此，若能将磷酸盐与pH联合电化学检测，将对电化学伏安法检测痕量磷酸盐离子具有很好的效果。
发明内容
本发明的目的在于解决现有技术中存在的问题，并提供一种痕量磷酸盐与pH联合检测仪，该联合检测仪可以同时检测溶液的pH和磷酸盐浓度，可通过预先确定溶液pH值是否为强酸性，确保磷酸盐浓度检测的准确性。
本发明具体采用的技术方案如下：
一种痕量磷酸盐与pH联合检测仪，它包括双通道丝网印刷电极，双通道丝网印刷电极在基板上布置有两个工作电极、一个参比电极和一个对电极，四个电极分别通过接线与触点相连；所述的参比电极和对电极间隔布置，两者之间夹持形成两个放置工作电极的对称区域，两个工作电极共用一个参比电极和一个对电极；所述的两个工作电极中，第一工作电极表面修饰有pH敏感纳米材料，第二工作电极表面修饰有磷酸盐敏感纳米材料。
作为优选，所述的pH敏感纳米材料为纳米金属氧化物。
进一步的，所述的纳米金属氧化物包括纳米级的二氧化钌、氧化镍、氧化锰、氧化钴、氧化铅和氧化钛。
作为优选，所述的磷酸盐敏感纳米材料为ZrO2-ZnO/多壁碳纳米管/四水合七钼酸铵纳米复合材料，其制备方法为：
1)将Zn(Ac) 2和ZrOCl 2粉末以质量比1：1的比例溶解在2wt.％的醋酸溶液中，然后在80℃水浴环境下缓慢加入2.0wt％的壳聚糖，调节溶液pH至11.0～12.0，继续保持80℃水浴1小时；随后对产生的沉淀进行洗涤、干燥，将该固体置于马弗炉中，以25℃h -1的速率升温至350℃恒温加热1小时，然后再以25℃h -1的速率升温至450℃下高温氧化1小时；固体冷却后，得到ZrO 2-ZnO纳米复合材料；
2)将所述ZrO 2-ZnO纳米复合材料加入乙醇中，超声震荡形成300mg L -1的纳米分散液；然后按照100mg L -1的投加量加入经过预处理的多壁碳纳米管，维持60℃水浴环境下加热24小时，得到悬浮液；待悬浮液冷却至室温后，向该 悬浮液中加入0.064mol L -1四水合七钼酸铵和0.1％Nafion，均匀混合后得到ZrO 2-ZnO/多壁碳纳米管/四水合七钼酸铵纳米复合材料的修饰液。
作为优选，所述的修饰液通过滴涂后干燥的方式修饰于第二工作电极表面。
作为优选，所述的多壁碳纳米管的预处理过程为：在浓HNO3中将多壁碳纳米管回流5小时。
作为优选，所述的接线为导电银层，所述的工作电极为碳电极，所述的参比电极为Ag/AgCl电极或碳电极，所述的对电极为铂丝电极或银电极，所述的基板为PET基板。
本发明的另一目的在于提供一种利用上述任一方案所述检测仪的痕量磷酸盐与pH联合检测方法，用于同时检测待测溶液的pH和磷酸盐浓度，其步骤如下：
1)将待测样品溶液定量滴加到包含第一工作电极的三电极体系表面，通过电化学法检测待测样品溶液的pH值；
2)将待测样品溶液与pH≤1的强酸性电解液定量混合，得到测试液；
3)将测试液定量滴加于包含第二工作电极的三电极体系表面，进行电位扫描，获得磷钼酸盐络合物的氧化还原峰峰电流；根据电流与磷酸盐浓度之间的线性关系，得到待测样品溶液中的磷酸盐浓度。
本发明的另一目的在于提供一种利用上述任一方案所述检测仪的痕量磷酸盐与pH联合检测方法，用于检测待测溶液中的磷酸盐浓度，其步骤如下：
1)将待测样品溶液与强酸性电解液定量混合，得到测试液；
2)将步骤1)中的测试液定量滴加到包含第一工作电极的三电极体系表面，通过电化学法检测测试液的pH值，确认溶液pH≤1；
3)将pH≤1的测试液定量滴加于包含第二工作电极的三电极体系表面，进行电位扫描，获得磷钼酸盐络合物的氧化还原峰峰电流；根据电流与磷酸盐浓度之间的线性关系，得到待测样品溶液中的磷酸盐浓度。
其中待测样品溶液的预处理根据实际进行确定。例如，对于水样，需要预先进行过滤，用滤液进行后续检测。但假如待测样品为土壤样品，则需预先对土壤样品中的磷酸盐进行提取，具体步骤为：将土壤样品干燥后过筛后，定量加入离心管中，使用醋酸作为提取剂，进行震荡提取；对提取液使用超速离心机进行固液分离，将离心后的上清液过滤作为待测样品溶液。
进一步的，所述震荡提取的时间优选为1h。
进一步的，所述的醋酸浓度优选为0.50mol L -1。
本发明的有益效果在于提供了一种痕量磷酸盐与pH联合检测仪，其具有双通道丝网印刷电极，能作为便携式设备独立进行两项独立的pH与磷酸盐检测。而且，试验证明在强酸环境下，磷酸盐能最大程度的转化为正磷酸盐的形式，进而形成磷钼酸盐络合物形式发生后续氧化还原反应，因此，利用该联合检测仪，可以在检测磷酸盐离子之前，预先确定待检测溶液的pH值是否为强酸性，减少测量误差。
另外，在该检测仪的工作电极上，针对于磷酸盐离子的检测，采用了一种新型修饰材料ZrO 2-ZnO/MWCNTs复合纳米材料。ZrO 2-Zn复合纳米颗粒，其具有大比表面积、丰富的羟基官能团，掺杂多壁碳纳米管后材料表现出良好的导电性，该工作电极在电位扫描过程中针对磷钼酸盐络合物展现出了优异的灵敏性、选择性和稳定性。其所形成的特征氧化还原峰完整及其电流峰值有效证明了该磷酸盐和钼酸盐络合反应的发生及反应生成物的含量，从而间接获得磷酸盐离子的对应添加浓度。采用该材料修饰的电极，在0.2mol L -1H 2SO 4/KCl(pH＝1.0)的电解质溶液中，磷酸盐离子最低检测限达到2×10 -8mol L -1。
本发明的有益效果在于提供了一种痕量磷酸盐与pH联合检测方法。针对于磷酸盐离子的检测，提供了一种新型修饰材料ZrO 2-ZnO/MWCNTs/AMT复合纳米材料。ZrO 2-Zn复合纳米颗粒，其具有大比表面积、丰富的羟基官能团，掺杂多壁碳纳米管后材料表现出良好的导电性，该工作电极在电位扫描过程中针对磷钼酸盐络合物展现出了优异的灵敏性、选择性和稳定性。其所形成的特征氧化还原峰完整及其电流峰值有效证明了该磷酸盐和钼酸盐络合反应的发生及反应生成物的含量，从而间接获得磷酸盐离子的对应添加浓度。
附图说明
图1为本发明一种痕量磷酸盐与pH联合检测仪的结构示意图；
图2为本发明中的双通道丝网电极网版设计图；
图3为本发明中不同材料的扫描电子显微镜图；其中(A)-(C)分别为ZrO 2-ZnO纳米复合材料(A)、ZrO 2-ZnO单独修饰丝网印刷电极(B)以及ZrO 2-ZnO/MWCNTs/AMT复合修饰丝网印刷电极表面(C)；
图4为ZrO 2-ZnO/MWCNTs/AMT复合修饰电极在添加3.7×10 -7μmol L -1H 2PO 4-(a)和没有添加H 2PO 4-条件下(b)的循环伏安电化学行为(-0.067v是钼价态变化的氧化峰)。
具体实施方式
下面结合附图对本发明的优选实施进行详细阐述，已使本发明的优点和特征能更易于被本领域的技术人员理解，从而对本发明的保护范围做出更为明确清晰的界定。
实施例1
如图1所示，本实施例中的一种痕量磷酸盐与pH联合检测仪，其核心结构是一个双通道丝网印刷电极。双通道丝网印刷电极在基板上布置有两个工作电极、一个参比电极和一个对电极，四个电极分别通过接线与触点相连。参比电极由两个1/4圆相切连接而成，对电极由两个1/2圆相切连接而成，参比电极和对电极间隔一定距离布置，两者之间夹持形成两个放置工作电极的镜像对称区域，两个工作电极共用一个参比电极和一个对电极，形成两个三电极体系。两个工作电极，可分为第一工作电极和第二工作电极，第一工作电极表面修饰有pH敏感纳米材料，第二工作电极表面修饰有磷酸盐敏感纳米材料。其中第一工作电极可用于pH检测；第二工作电极可用于磷酸盐的检测，两者配合能进行两项独立的pH与磷酸盐检测。
印刷电极所采用的材料可以根据需要进行调整，在本实施例中，接线为导电银层，工作电极为碳电极，参比电极为Ag/AgCl电极(也可以采用碳电极)，对电极为铂丝电极(也可以采用银电极)，基板为PET基板。该印刷电极在印刷过程需要四块网版，分别为导电银层，碳电极，Ag/AgCl参比，铂丝电极和绝缘层，网版设计如图2所示。在两个工作电极上的修饰材料可以根据需要进行选择。例如，pH敏感纳米材料可以是纳米金属氧化物，包括纳米级的二氧化钌、氧化镍、氧化锰、氧化钴、氧化铅和氧化钛等等，其修饰过程可以采用现有技术中的任何可行方式实现，如喷涂、掺杂等。磷酸盐敏感纳米材料也可以根据需要采用现有技术中的现有磷酸根敏感膜，后续实施例中的ZrO 2-ZnO/MWCNTs/AMT纳米复合材料只是其中一种优选实现方式。
在上述检测仪中，第一工作电极可以用来检测原始待测溶液的pH，也可以用来检测经过酸化的待测溶液的pH，以保证添加到第二工作电极表面的待测溶液处于强酸性环境下，使电化学反应中呈现的响应峰电流可以完全反应样品中所有可溶性磷酸盐离子的存在。因此，基于上述检测仪，可以设计两种使用方法。
第一种痕量磷酸盐与pH联合检测方法，用于同时检测待测溶液中的pH和磷酸盐浓度，其做法为：
1)将待测样品溶液滴加到包含第一工作电极的三电极体系表面，通过外接于触点上的电化学工作站根据电位检测待测样品溶液的pH值。
2)然后将待测样品溶液与强酸性电解液(优选pH≤1)定量混合，使混合液也呈强酸性。然后将pH≤1的测试液定量滴加于包含第二工作电极的三电极体系表面，采用循环伏安法或方波伏安法(考虑痕量磷酸盐出峰情况，优选为方波伏安法)进行电位扫描，获得磷钼酸盐络合物的氧化还原峰峰电流(-0.067V处产生的氧化峰响应，下同)；根据电流与磷酸盐浓度之间的线性关系，换算得到待测样品溶液中的磷酸盐浓度。
第二种痕量磷酸盐与pH联合检测方法，用于准确检测待测溶液中的磷酸盐浓度，其做法为：
1)将待测样品溶液与强酸性电解液(优选pH≤1)定量混合，得到测试液；
2)将步骤1)中的测试液定量滴加到包含第一工作电极的三电极体系表面，通过电化学法检测测试液的pH值，确认溶液pH≤1。若pH≤1，则进行下一步，否则需要根据pH继续添加酸降低pH。
3)将pH≤1的测试液，定量滴加于包含第二工作电极的三电极体系表面，采用循环伏安法或方波伏安法(考虑痕量磷酸盐出峰情况，优选为方波伏安法)进行电位扫描，获得磷钼酸盐络合物的氧化还原峰峰电流；根据电流与磷酸盐浓度之间的线性关系，换算得到待测样品溶液中的磷酸盐浓度。
第一种方法适合于需要对样品的pH和磷酸盐浓度同时进行测定的场合。
第二种方式适合野外环境下的磷酸盐浓度原位快速定量检测，在非实验室环境下无法准确测定待测水样的pH，而水样本身的pH又存在波动性，因此加酸量无法准确控制。另外，水样中磷酸盐本身是痕量的，若低于检测限可能需要提高水样与电解液的混合比例，容易造成混合液的酸性不足。但通过本发明的痕量 磷酸盐与pH联合检测仪，可以确定测试液在加入第二工作电极时已经处于强酸环境下，保证测量结果的准确性。
上述两种方法中，电流与磷酸盐浓度之间存在的线性关系可以以相同方法测定不同的磷酸二氢根离子H 2PO 4-标准溶液获得。
另外，上述两种方法中，可以将待测样品溶液直接滴加于第二工作电极表面进行循环伏安法测定，也可以先将待测样品溶液滴加于第二工作电极表面，待其干燥后再滴加强酸性电解质溶液进行测定。假如样品中磷酸盐的浓度过低，含有磷酸盐的待测液时先定量滴加在工作电极上，干燥后再置于电解质溶液中进行电位扫描，是一种优选推荐的方法。这是由于检测的磷酸盐是痕量的，直接混合于电解质中采用循环伏安法进行电位扫描时，不容易出峰。而预先干燥后在置于电解质溶液中进行电位扫描，能够更好地出峰，提高测量准确性。但预先干燥会延长检测耗时，大批量采样时不建议使用。另外，针对痕量磷酸盐，也可以将待测液于电解质溶液定量混合，然后将混合液直接滴加到三电极体系上或将三电极体系置于混合液中，采用方波伏安法电位扫描，相比于循环伏安法更容易出峰。
实施例2
在本实施例中，基于实施例1设计的痕量磷酸盐与pH联合检测仪，进一步提供了一种磷酸盐敏感纳米材料，即ZrO2-ZnO/多壁碳纳米管/四水合七钼酸铵(ZrO 2-ZnO/MWCNTs/AMT)纳米复合材料。
本实施例中，制备ZrO 2-ZnO/MWCNTs/AMT纳米复合材料的过程如下：
1)制备ZrO 2-ZnO纳米复合材料
将1.5g的Zn(Ac) 2和1.5g的ZrOCl 2粉末(质量比1：1)溶解在30ml 2wt.％的醋酸溶液中，然后在80℃水浴环境下缓慢加入壳聚糖使壳聚糖浓度为2.0wt％，并在不断搅拌的条件下逐滴滴加30％NaOH溶液，调节溶液pH至11.0～12.0，继续保持80℃水浴1小时，溶液中产生白色沉淀。
之后用去离子水和乙醇反复洗涤过滤所产生的白色沉淀，并将其置于烘箱内，在100℃条件下干燥。待沉淀完全烘干后，将该固体沉淀放入马弗炉中，以25℃h -1的速率升温至350℃并恒温加热1小时，然后继续以相同升温速率加热至450℃高温氧化1小时。待固体完全冷却后，得到ZrO 2-ZnO纳米复合材料。
2)制备ZrO 2--ZnO/MWCNTs/AMT纳米复合修饰材料
将一定量上述所制备的ZrO 2-ZnO纳米复合材料加入乙醇中，超声震荡1h以上，形成300mg L -1的ZrO 2-ZnO纳米分散液。多壁碳纳米管预先进行预处理：在浓HNO3中将多壁碳纳米管(阿拉丁，直径＝3-5nm，长度＝50μm)回流5小时以激活其分子活性，然后将经过预处理的多壁碳纳米管(MWCNTs)加入分散液中，MWCNTs在分散液中的浓度为100mg L -1，继续维持60℃水浴环境下加热24小时，得到悬浮液。待悬浮液冷却至室温后，为了增加后期修饰膜的稳定性，向该悬浮液加入0.064mol L -1四水合七钼酸铵(AMT)和0.1％Nafion(AMT和Nafion预先溶于乙醇中再添加)，均匀混合后得到ZrO 2-ZnO/多壁碳纳米管/四水合七钼酸铵纳米复合材料的修饰液。
该修饰液使用时，可滴涂在工作电极表面，干燥后制得ZrO 2-ZnO/MWCNTs/AMT复合修饰丝网印刷电极(ZrO2-ZnO/MWCNTs/AMT/SPE)。
为了便于观察ZnO-ZrO 2复合纳米颗粒和其修饰丝网印刷电极表面的形貌特征，釆用日本JSM-5600LV扫描电子显微镜观察其组成形态和直径。本实施例中，对ZrO 2-ZnO纳米复合材料的形态面貌及其掺杂多壁碳纳米管前后在修饰电极上的结构进行了表征，图3(A)为ZrO 2-ZnO纳米复合材料扫描电镜图像，图像显示当Zn(Ac) 2和ZrOCl 2以1：1的质量比在含2.0wt％壳聚糖的醋酸溶液中混合时，经高温煅烧会形成均匀的纳米棒状结构，且该纳米棒长度介于300-500nm范围内，从尖端到底部均保持约100nm的宽度。而图3(B)显示，当单独将ZrO 2-ZnO纳米复合材料修饰于丝网印刷电极表面，其结构与之前未修饰的材料相比，经过超声震荡等处理后，纳米颗粒形态发生了一定变化，纳米棒分散密度更加均匀，比表面积也有一定地提高，该种改变有效促进了被吸附物可扩散位点的增多。同时，在掺杂了多壁碳纳米管之后的修饰膜上，扫描图像图3(C)显示，每根碳纳米管表面均包覆着ZrO 2-ZnO复合纳米颗粒，这种结构不仅可利用ZrO 2-ZnO纳米复合材料对磷酸盐离子的高亲和力，还可以依靠多壁碳纳米管的高导电率改善磷钼酸根离子氧化还原反应的反应速率和反应程度。
采用CHI660E电化学工作站，对于所制备的ZrO 2-ZnO/MWCNTs/AMT复合修饰电极进行循环伏安法电化学分析检测。本实施例在电化学分析检测时，采用一体化三电极体系：ZrO 2-ZnO/MWCNTs/AMT/SPE为工作电极，同时以碳电极和银电极分别作为参比电极和对电极。在工作电极的修饰膜表面滴涂10μL3.7×10 -7μmol L -1磷酸二氢根离子H 2PO 4 -标准溶液，干燥1小时，直至其完全涂 覆于电极表面。采用去除氧气的0.2mol L -1H 2SO 4/KCl溶液(pH＝1)作为电解质溶液，在室温条件下将三电极体系置于电解质溶液中，选取电位-1.0V、+1.0V和-1.0V分别为电位扫描的起点、最高点和终点电位，扫描速率保持为50mVs -1。同时，也设置了不添加3.7×10 -7μmol L -1磷酸二氢根离子H 2PO 4 -标准溶液的对照组，进行相同的电化学分析检测。
结果表明，在3.7×10 -7μmol L -1磷酸二氢根离子添加与不添加的条件下，ZrO 2-ZnO/MWCNTs/AMT/SPE在pH＝1电解质溶液中的循环伏安响应如图4所示，在电位扫描过程中，该电极始终会在0.101V上出现一个阳极响应峰，这归因于工作电极表面氢离子的氧化反应(曲线a)；而在加入了磷酸二氢根离子后，曲线b在电位-0.067V处又出现了一个相应的氧化峰，该峰反映了磷钼酸盐络合物中钼价态的复杂变化过程，两个氧化峰形成过程中发生的电化学反应如方程式3和4所示：
Figure PCTCN2019106537-appb-000004
Figure PCTCN2019106537-appb-000005
值得注意的是，在电位为-0.067V处产生的氧化峰响应电流将随磷酸盐离子浓度的增加而提高，因此该反应间接提供了一种电化学技术检测无机磷酸盐离子的可行方案，即根据电流与磷酸盐浓度之间存在的线性关系，换算得到待测样品溶液中的磷酸盐浓度。鉴于氧化峰仅在电极表面负载有磷酸盐离子时出现，该电极具有良好的检测选择性。
磷酸盐的电化学检测分析发生在电极表面电势由负→正→负发生变动的条件下，以钼元素为中心的盐类化合物与磷酸盐预先络合，生成了具有电化学活性的磷钼酸盐络合物，该物质被迫发生氧化还原反应从而产生响应峰信号。该反应中Mo/H +含量比例是可控的，测试环境必须保证为强酸性。
实施例3
实施例1和2中的待测样品溶液均为水溶液，可直接用于检测水样中的磷酸盐含量。但假如需要测定土壤样品中的磷酸盐含量，则需要预先对土壤样品中无机磷酸盐离子进行提取。下面基于实施例2中的采用一体化三电极体系对提取参数进行优化，以确保土壤样品中无机磷酸盐的含量最大程度化地反应在循环伏安曲线上。因此所需最佳提取剂不仅要使得磷酸盐完全溶解，并且自身所包含的离 子不会对检测结果产生干扰，即不会影响氧化还原峰的电位电流值。在本实施例中，四种萃取剂醋酸、碳酸氢钠、硫酸钾和MES缓冲液被作为提取剂候选溶液。
首先，在多支50mL离心管中加入1.0g经过晒干，并经过0.5mm直径筛孔的筛网筛选后的土壤粉末，设置多组不同提取剂的试验，不同试验组中分别添加20mL 0.50mol L -1HAc、NaHCO 3、K 2SO 4和MES溶液之一作为提取剂。然后再向各离心管中加入1mL 0.025mol L -1KHP溶液作为离子强度调节剂。将离心管置于在恒温摇床中(170rpm,，25℃)进行震荡提取，本实施例同时对震荡时间进行优化，分别为10分钟、20分钟、30分钟、1小时和2小时。在混合物完成震荡后，利用超速离心机使其固液分离(5000rpm，20分钟，25℃)。将离心后的液体重新过滤并转移至25mL离心管内，在样品被检测之前将其置于4℃环境中储存。
试验结果表明，提取剂的优选顺序为HAc>NaHCO 3>K 2SO4>MES。醋酸溶剂作为最佳提取剂，用醋酸提取的磷酸盐离子在电位扫描阶段形成的循环伏安曲线线型完整，且有清晰的氧化还原峰出现，响应信号也十分强烈。而对于提取时间而言，在震荡提取时间为1小时条件下，最终检测效果显示为最佳。因此土壤的震荡提取优化条件为：以0.50mol L -1醋酸为提取剂，震荡提取的时间设为1h。
在优化条件下，对提取后含磷酸盐离子的样品进行电化学浓度分析，用微量注射器移取10μL样品溶液滴涂至已被修饰后的丝网印刷电极表面，待在室温下干燥后，置于0.2mol L -1H 2SO 4/KCl(pH＝1)电解质溶液中，采用循环伏安法进行电位扫描，从而获得磷钼酸盐络合物的氧化还原峰峰电流，根据电流与磷酸盐浓度之间存在的线性关系，进而间接确定样品中可溶性磷酸盐离子的浓度。同时，为了评估电化学伏安法测定土壤中无机磷酸盐离子的可行性，将上述循环伏安法的检测结果与标准比色法所得结果进行比较，评估该工作电极的检测准确度。土壤样品分别取自广东、湖南和江苏三地，每地两个样品。
标准比色法和循环伏安法对于同一样品中无机磷酸盐离子浓度的检测结果如表1所示，其中循环伏安法通过调节pH值，使得无机磷酸盐主要以H 2PO 4 -的形式参与电化学反应，而标准比色法则按照常规磷酸盐与钼酸盐之间发生的络合反应进行测试。测试结果显示，比色法所得磷酸盐浓度略低于循环伏安技术，该结果猜测可能是比色法中抗坏血酸的加入所引起的，该物质会破坏氧化还原反 应过程中的电子转移，使得10％-20％的复杂磷酸盐化合物在检测过程中无法得到识别。
表1 标准比色法和循环伏安法针对土壤磷酸盐离子含量检测结果对比
Figure PCTCN2019106537-appb-000006
以上所述的实施例只是本发明的一种较佳的方案，然其并非用以限制本发明。有关技术领域的普通技术人员，在不脱离本发明的精神和范围的情况下，还可以做出各种变化和变型。因此凡采取等同替换或等效变换的方式所获得的技术方案，均落在本发明的保护范围内。

Claims (10)

  1. 一种痕量磷酸盐与pH联合检测仪，其特征在于，包括双通道丝网印刷电极，双通道丝网印刷电极在基板上布置有两个工作电极、一个参比电极和一个对电极，四个电极分别通过接线与触点相连；所述的参比电极和对电极间隔布置，两者之间夹持形成两个放置工作电极的对称区域，两个工作电极共用一个参比电极和一个对电极；所述的两个工作电极中，第一工作电极表面修饰有pH敏感纳米材料，第二工作电极表面修饰有磷酸盐敏感纳米材料。
  2. 如权利要求1所述的痕量磷酸盐与pH联合检测仪，其特征在于，所述的pH敏感纳米材料为纳米金属氧化物。
  3. 如权利要求2所述的痕量磷酸盐与pH联合检测仪，其特征在于，所述的纳米金属氧化物包括纳米级的二氧化钌、氧化镍、氧化锰、氧化钴、氧化铅和氧化钛。
  4. 如权利要求1所述的痕量磷酸盐与pH联合检测仪，其特征在于，所述的磷酸盐敏感纳米材料为ZrO2-ZnO/多壁碳纳米管/四水合七钼酸铵纳米复合材料，其制备方法为：
    1)将Zn(Ac) 2和ZrOCl 2粉末以质量比1：1的比例溶解在2wt.％的醋酸溶液中，然后在80℃水浴环境下缓慢加入2.0wt％的壳聚糖，调节溶液pH至11.0～12.0，继续保持80℃水浴1小时；随后对产生的沉淀进行洗涤、干燥，将该固体置于马弗炉中，以25℃h -1的速率升温至350℃恒温加热1小时，然后再以25℃h -1的速率升温至450℃下高温氧化1小时；固体冷却后，得到ZrO 2-ZnO纳米复合材料；
    2)将所述ZrO 2-ZnO纳米复合材料加入乙醇中，超声震荡形成300mg L -1的纳米分散液；然后按照100mg L -1的投加量加入经过预处理的多壁碳纳米管，维持60℃水浴环境下加热24小时，得到悬浮液；待悬浮液冷却至室温后，向该悬浮液中加入0.064mol L -1四水合七钼酸铵和0.1％Nafion，均匀混合后得到ZrO 2-ZnO/多壁碳纳米管/四水合七钼酸铵纳米复合材料的修饰液。
  5. 如权利要求1所述的痕量磷酸盐与pH联合检测仪，其特征在于，所述的修饰液通过滴涂后干燥的方式修饰于第二工作电极表面。
  6. 如权利要求1所述的痕量磷酸盐与pH联合检测仪，其特征在于，所述的多壁碳纳米管的预处理过程为：在浓HNO3中将多壁碳纳米管回流5小时。
  7. 如权利要求1所述的痕量磷酸盐与pH联合检测仪，其特征在于，所述的接线为导电银层，所述的工作电极为碳电极，所述的参比电极为Ag/AgCl电极或碳电极，所述的对电极为铂丝电极或银电极，所述的基板为PET基板。
  8. 一种利用如权利要求1～7任一所述检测仪的痕量磷酸盐与pH联合检测方法，用于同时检测待测溶液的pH和磷酸盐浓度，其特征在于，步骤如下：
    1)将待测样品溶液定量滴加到包含第一工作电极的三电极体系表面，通过电化学法检测待测样品溶液的pH值；
    2)将待测样品溶液与pH≤1的强酸性电解液定量混合，得到测试液；
    3)将测试液定量滴加于包含第二工作电极的三电极体系表面，进行电位扫描，获得磷钼酸盐络合物的氧化还原峰峰电流；根据电流与磷酸盐浓度之间的线性关系，得到待测样品溶液中的磷酸盐浓度。
  9. 一种利用如权利要求1～7任一所述检测仪的痕量磷酸盐与pH联合检测方法，用于检测待测溶液中的磷酸盐浓度，其特征在于，步骤如下：
    1)将待测样品溶液与强酸性电解液定量混合，得到测试液；
    2)将步骤1)中的测试液定量滴加到包含第一工作电极的三电极体系表面，通过电化学法检测测试液的pH值，确认溶液pH≤1；
    3)将pH≤1的测试液定量滴加于包含第二工作电极的三电极体系表面，进行电位扫描，获得磷钼酸盐络合物的氧化还原峰峰电流；根据电流与磷酸盐浓度之间的线性关系，得到待测样品溶液中的磷酸盐浓度。
  10. 如权利要求1所述的痕量磷酸盐与pH联合检测方法，其特征在于，所述的待测样品为土壤样品，需预先对土壤样品中的磷酸盐进行提取，具体步骤为：将土壤样品干燥后过筛后，定量加入离心管中，使用醋酸作为提取剂，进行震荡提取；对提取液使用超速离心机进行固液分离，将离心后的上清液过滤作为待测样品溶液；所述震荡提取的时间优选为1h；所述的醋酸浓度优选为0.50mol L -1。
PCT/CN2019/106537 2019-04-23 2019-09-18 一种痕量磷酸盐与pH联合检测仪及其方法 WO2020215600A1 (zh)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
CN201910329013.6A CN110133072B (zh) 2019-04-23 2019-04-23 一种痕量磷酸盐与pH联合检测仪及其方法
CN201910329013.6 2019-04-23

Publications (1)

Publication Number Publication Date
WO2020215600A1 true WO2020215600A1 (zh) 2020-10-29

Family

ID=67570806

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/CN2019/106537 WO2020215600A1 (zh) 2019-04-23 2019-09-18 一种痕量磷酸盐与pH联合检测仪及其方法

Country Status (2)

Country Link
CN (1) CN110133072B (zh)
WO (1) WO2020215600A1 (zh)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110133072B (zh) * 2019-04-23 2020-03-17 浙江大学 一种痕量磷酸盐与pH联合检测仪及其方法
CN112946047B (zh) * 2021-01-28 2023-03-21 中国科学院烟台海岸带研究所 一种快速检测水体溶解态无机磷的电化学方法
CN113740400B (zh) * 2021-08-18 2023-10-24 淮阴工学院 带有对称参比电极的封闭式双极电极阵列的分析检测装置
CN114965659B (zh) * 2022-04-20 2023-06-27 中国科学院空天信息创新研究院 检测磷酸盐浓度的方法以及电化学传感器

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20090321278A1 (en) * 2005-09-01 2009-12-31 Stephen William Birch Electrochemical sensor
CN202854091U (zh) * 2012-08-19 2013-04-03 济南大学 同时检测己烯雌酚和雌二醇的丝网印刷电极免疫传感器
CN104198555A (zh) * 2014-09-16 2014-12-10 重庆大学 一种聚卟啉/纳米金修饰玻碳电极、制备方法及其应用
CN107449815A (zh) * 2017-08-16 2017-12-08 中国科学院烟台海岸带研究所 一种可用于单细胞检测的电位型微电极传感器及其应用
CN108398474A (zh) * 2018-02-13 2018-08-14 中国科学院烟台海岸带研究所 一种可用于沉积物中离子检测的电位型微电极传感器及其应用
CN110133072A (zh) * 2019-04-23 2019-08-16 浙江大学 一种痕量磷酸盐与pH联合检测仪及其方法

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107966485A (zh) * 2017-12-07 2018-04-27 中国石油化工股份有限公司 一种基于石墨烯试纸电极构建的电化学重金属检测仪及其检测方法

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20090321278A1 (en) * 2005-09-01 2009-12-31 Stephen William Birch Electrochemical sensor
CN202854091U (zh) * 2012-08-19 2013-04-03 济南大学 同时检测己烯雌酚和雌二醇的丝网印刷电极免疫传感器
CN104198555A (zh) * 2014-09-16 2014-12-10 重庆大学 一种聚卟啉/纳米金修饰玻碳电极、制备方法及其应用
CN107449815A (zh) * 2017-08-16 2017-12-08 中国科学院烟台海岸带研究所 一种可用于单细胞检测的电位型微电极传感器及其应用
CN108398474A (zh) * 2018-02-13 2018-08-14 中国科学院烟台海岸带研究所 一种可用于沉积物中离子检测的电位型微电极传感器及其应用
CN110133072A (zh) * 2019-04-23 2019-08-16 浙江大学 一种痕量磷酸盐与pH联合检测仪及其方法

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
LI, YINHUA: "Research and Development of Phosphate Ion-selective Electrode Based on Molybdenum", CHINA MASTERS’ THESES FULL-TEXT DATABASE, 15 February 2019 (2019-02-15), pages 23 - 24, 27; 38-47 *

Also Published As

Publication number Publication date
CN110133072A (zh) 2019-08-16
CN110133072B (zh) 2020-03-17

Similar Documents

Publication Publication Date Title
WO2020215600A1 (zh) 一种痕量磷酸盐与pH联合检测仪及其方法
Zhu et al. A miniature and low-cost electrochemical system for sensitive determination of rhodamine B
CN110412095B (zh) 一种负载花球状硫化铜-钯核壳结构的氮掺杂石墨烯复合材料及其制备方法与应用
CN110297025B (zh) 一种纳米级Ni-Fe普鲁士蓝类似物材料及其制备方法与电化学检测邻硝基酚的应用
Sedaghat et al. Development of a nickel oxide/oxyhydroxide-modified printed carbon electrode as an all solid-state sensor for potentiometric phosphate detection
Yin et al. Ultra-sensitive detection of multiplexed heavy metal ions by MOF-derived carbon film encapsulating BiCu alloy nanoparticles in potable electrochemical sensing system
Zhou et al. A nanocomposite consisting of ionic liquid-functionalized layered Mg (II)/Al (III) double hydroxides for simultaneous electrochemical determination of cadmium (II), copper (II), mercury (II) and lead (II)
Xia et al. An electrochemical sensor for the sensitive detection of rutin based on a novel composite of activated silica gel and graphene
CN114636746B (zh) 一种检测Pb2+的羧基配体诱导的湮灭型比率电化学发光适配体传感方法
Zou et al. A high sensitivity strategy of nitrite detection based on CoFe@ NC nanocubes modified glassy carbon electrode
Rabie et al. A Novel Electrochemical Sensor Based on Modified Carbon Paste Electrode with ZnO Nanorods for the Voltammetric Determination of Indole‐3‐acetic Acid in Plant Seed Extracts
Huang et al. Ultrasensitive determination of metronidazole using flower-like cobalt anchored on reduced graphene oxide nanocomposite electrochemical sensor
Ouyang et al. ZIFs derived polyhedron with cobalt oxide nanoparticles as novel nanozyme for the biomimetic catalytic oxidation of glucose and non-enzymatic sensor
CN110133083B (zh) 一种对磷酸盐敏感的电极表面修饰材料及制备方法和应用
Zhang et al. Direct electrodeposition of carbon dots modifying bismuth film electrode for sensitive detection of Cd2+ and Pb2+
Karthika et al. An ultrahigh selective uric acid sensor based on SrWO4 nanocomposite using pomelo leaf extract solubilized Nafion modified glassy carbon electrode
Ali et al. A new ultrasensitive platform based on f-GCNFs@ nano-CeO2 core-shell nanocomposite for electrochemical sensing of oxidative stress biomarker 3-nitrotyrosine in presence of uric acid and tyrosine
Ghalkhani et al. Green synthesis of nonprecious metal-doped copper hydroxide nanoparticles for construction of a dopamine sensor
Tang et al. A voltammetric sensor based on multi-walled carbon nanotube–MnO 2 nanowire composite film for simultaneous determination of hydroquinone and catechol
Shi et al. Ultrasensitive detection of mercury (ii) ions on a hybrid film of a graphene and gold nanoparticle-modified electrode
Gorla et al. Development of novel nanocomposite-modified photoelectrochemical sensor based on the association of bismuth vanadate and MWCNT-grafted-molecularly imprinted poly (acrylic acid) for dopamine determination at nanomolar level
Mahieddine et al. A novel non-enzymatic electrochemical sensor based on NiS/Co3S4@ h-Ni NWs core-shell electrode for glucose detection in human serum
Singh et al. Redox electrochemistry of electrodes tuned with dimethyl ferrocene based on Co–NC–Pd nanogeometry: an impedimetric sensor for NADH sensing
Faridan et al. Simultaneous determination of trace amounts ascorbic acid, melatonin and tryptophan using modified glassy carbon electrode based on Cuo-CeO2-rGO-MWCNTS nanocomposites
Dang et al. One-step hydrothermal synthesis of a novel rare earth phosphate nanoellipsoid with high electrocatalytic activity and distinguished biosensing performance to common neurotransmitters

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: 19925984

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: 19925984

Country of ref document: EP

Kind code of ref document: A1