CN204925023U - Electrochemical detection pond - Google Patents
Electrochemical detection pond Download PDFInfo
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- CN204925023U CN204925023U CN201520698992.XU CN201520698992U CN204925023U CN 204925023 U CN204925023 U CN 204925023U CN 201520698992 U CN201520698992 U CN 201520698992U CN 204925023 U CN204925023 U CN 204925023U
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- electrode
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- detection cell
- sealing gasket
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Abstract
The utility model relates to an electrochemical detection pond, including detect cell body (1), sealedly fill up (2), working electrode (3), to electrode (6) and reference electrode (10), its characterized in that, sealed one side of filling up (2) is hugged closely in the front surface that detects cell body (1), and the another side is had vacant position at the middle part, sticis working electrode (3) through the electrode fixing device (4) in the one side that sealed pad (2) was had vacant position, thereby by detection cell body (1) working electrode (3) with sealed fill up (2) form detection chamber (7). The utility model discloses an electrochemical detection pond has very thin liquid fluid layer on the electrode surface, is favorable to increasing measuring current, improves detectivity and reduces the detectability.
Description
Technical field
The utility model relates to a kind of based on three electrode flow injection type electrochemical investigating pond.This detection cell can be used for measuring the chemical oxygen demand (COD) (ChemicalOxygenDemand, COD) in water, belongs to environmental monitoring technology field.It also may be used for the liquid detecting in other field.
Background technology
In environmental monitoring field, the contaminated degree surveying water body is essential.And chemical oxygen demand (COD) (COD) is an important indicator weighing that water body is subject to organism pollution level.The standard method of traditional survey COD is potassium dichromate method.This method needs to use a large amount of environmentally harmful chemicals and reagent, and complex steps, and the test duration is long.In recent years, the quick and method of the survey COD of environmental protection is more and more subject to people's attention.Wherein use boron-doped diamond thin-film electrode to have very large attractive force as the method for the survey COD of working electrode, because the method test speed is fast, step is simple, and does not need added regent, therefore very environmental protection.
Flow injection detection technique is a kind of efficient, highly sensitive detection method.Its principle is that carrier fluid flows through detection cell with certain flow rate, produces certain background current with working electrode contact.Can by with flowing through working electrode when sample is joined in carrier fluid in the mode of injection, can produce corresponding response current to the specific reaction occurred after working electrode contact, be generally for feature with a current peak.In general the concentration of thing to be detected sample can be drawn from the height of this current peak.This detection method have continuity good, be suitable for the advantages such as on-line monitoring, be therefore widely adopted.
In order to draw the testing result of high sensitivity, low detectability, the design comprising the electrochemical investigating pond of working electrode is particularly important.Patent of invention " a kind of electrochemical analyser based on Flow Injection Analysis " (application number: give a kind of electrochemical investigating pond 200610113139.2), it is characterized in that crossing a test chamber with a kind of O type rubber ring, its three electrode uses screen printing electrode.Screen printing electrode is more suitable for detecting the detection that number of times is low, accuracy requirement is also relatively low, but and is not suitable for repeatedly long-time and that accuracy requirement is high detection.Use that the method for rubber ring is also more difficult forms the very thin liquid fluid layer of one deck at electrode surface simultaneously.A kind of three electrode detection ponds are described in patent of invention " a kind of based on chemical oxygen demand measuring apparatus and method in the water of flow injection sample introduction " (application number: 200810010232.X).Its working electrode adopts trip bolt to be fixed in sense channel, adopts O-ring seal and sense channel to be formed and seals.Contrast electrode and fluid path adopt mode connected vertically simultaneously.This detection cell not easily forms very thin liquid layer at working electrode surface, simultaneously the connected mode of its contrast electrode also the easy bubble that accumulates in fluid path be unfavorable for detecting.
Utility model content
In view of the deficiencies in the prior art, it is simple, compact that the purpose of this utility model is to provide a kind of structure, be easy to processing and manufacturing, and the liquid fluid layer of working electrode surface can be very thin thus be conducive to improving detection sensitivity, reduce by three electrode flow injection electrochemical investigating ponds of detectability.Simultaneously in testing process, issuable bubble not easily accumulates in fluid path, thus be conducive to detecting continuous, carry out smoothly.
For achieving the above object, the technical solution adopted in the utility model is as follows.
According to electrochemical investigating pond of the present utility model, comprise detection cell body (1), sealing gasket (2), working electrode (3), to electrode (6) and contrast electrode (10).The one side of described sealing gasket (2) is close to the front surface of detection cell body (1), and another side is had vacant position at middle part.Described working electrode (3) is pressed in the one side that sealing gasket (2) has vacant position by electrode fixing device (4), thus forms test chamber (7) by described detection cell body (1), described working electrode (3) with described sealing gasket (2).
Described sealing gasket (2) has the thickness of 10 μm ~ 1000 μm, the thickness of preferably 10 μm ~ 100 μm.
Described electrode fixing device (4) is electrode fixed head; And utilize screw (5) described working electrode (3) and described sealing gasket (2) to be fastened on the front surface of described detection cell body (1).
Described electrochemical investigating pond also comprises liquid inlet duct (9), described liquid inlet duct (9) be positioned at described detection cell body upper surface and perpendicular to described upper surface.
Described contrast electrode (10) be positioned at detection cell body rear surface and perpendicular to described rear surface.
Described also liquid outlet tube be can be used as to electrode (6), be connected with the outflow fluid path of described test chamber (7) is vertical.
Described contrast electrode (10) is connected in the horizontal direction with the outflow fluid path of described test chamber (7).
Compared with prior art, according to the beneficial effect of electrochemical investigating pond of the present utility model be:
Very thin at the liquid fluid layer of the miniature test chamber of working electrode surface formation, be conducive to improving the sensitivity detected, reduce detectability;
Contrast electrode and the mounting means of electrode (liquid outlet tube) is conducive to the discharge of bubble in fluid path, thus be conducive to detecting continuous, smooth, carry out reliably.
Accompanying drawing explanation
Fig. 1 is the structure front elevation (looking over from front surface) of the utility model three electrode flow injection electrochemical investigating pond.
Fig. 2 is the structure vertical view (going down viewed from upper surface) of the utility model detection cell.
Reference numeral
1 detection cell body; 2 sealing gaskets; 3 working electrodes; 4 electrode fixed heads; 5 screws; 6 pairs of electrodes (liquid outlet tube); 7 test chamber; 8 working electrode lead-in wires; 9 liquid inlet ducts; 10 contrast electrodes.
Embodiment
See Fig. 1 and Fig. 2, according to a kind of embodiment of the present utility model, provide a kind of electrochemical investigating pond, comprise detection cell body 1, sealing gasket 2, working electrode 3, to electrode 6 and contrast electrode 10.Wherein, the one side of sealing gasket 2 is close to the front surface of detection cell body 1, and another side is had vacant position at middle part; Working electrode 3 is pressed in the one side that sealing gasket 2 has vacant position by electrode fixing device 4, thus forms test chamber 7 by detection cell body 1, working electrode 3 with sealing gasket 2.This test chamber 7 is sealings, and preferably oval.
Above-mentioned sealing gasket 2 has the thickness of 10 μm ~ 1000 μm, the thickness of preferably 10 μm ~ 100 μm.
Electrode fixing device 4 can be electrode fixed head; And utilize screw 5, through electrode fixed head, working electrode 3 and sealing gasket 2 are fastened on the front surface of detection cell body 1.
Also comprise liquid inlet duct 9 according to electrochemical investigating pond of the present utility model, its be positioned at detection cell body 1 upper surface and perpendicular to this upper surface.
Above-mentioned contrast electrode 10 is positioned at the rear surface of detection cell body and perpendicular to this rear surface, and is connected in the horizontal direction with the outflow fluid path of test chamber 7.Meanwhile, above-mentioned to electrode 6 be also used as liquid outlet tube, be connected with the outflow fluid path of test chamber 7 is vertical.
Particularly, see Fig. 2, in above-mentioned electrochemical investigating pond, preferred detection pond body 1 is that one has certain thickness strip and block resistant material, has a path run through as liquid inlet passage in the direction that its middle part is vertical with forward and backward surface.Have the sealing gasket 2 that one deck is very thin on the front surface, its middle part has one piece of oval vacancy to be used for forming test chamber, and liquid inlet passage is arranged in this test chamber.In addition, at the opposite side of test chamber, a liquid outflow pathway is had.It is the working electrode 3 of sheet on sealing gasket 2, it is electrode fixed head 4 on working electrode 3, electrode fixed head 4 two gib screws 5 are fastened on detection cell body 1, thus make working electrode 3 can be pressed in the miniature test chamber 7 sealing gasket 2 being formed sealing tightly, working electrode lead-in wire 8 is derived simultaneously.Liquid inlet duct 9 be positioned at detection cell body rear surface and perpendicular to rear surface, to electrode (liquid outlet tube) 6 be positioned at detection cell body 1 upper surface and perpendicular to this upper surface, contrast electrode 10 be positioned at detection cell body rear surface and perpendicular to rear surface.
Above-mentioned contrast electrode 10 is non-screen printing electrode, and potential stability is good, can reuse.Are a kind of hollow edged electrodes to electrode 6, are made up of metal platinum or other metals, when being used as liquid outlet tube, liquid flows into from the inlet tube of detection cell, flows through test chamber, finally flows out to electrode from bottom to top.
In electrochemical investigating pond as above, the miniature test chamber of a sealing is formed by detection cell body, working electrode and sealing gasket, in so miniature test chamber, a very thin liquid fluid layer can be formed on the surface of working electrode, therefore being conducive to organism, to be diffused into electrode surface oxidized, and then be conducive to increasing response current, improve detection sensitivity and reduce detectability (as being low to moderate 1mg/L).
Above-mentioned contrast electrode and be conducive to the bubble that may exist in fluid path to be discharged in time to the specific mounting means of electrode (liquid outlet tube), avoids the accumulation of bubble in fluid path.Thus be conducive to detect continuous, smooth, carry out reliably.
Test novel electrochemical investigating pond according to this to assemble by the conventional method of this area.Such as, first sealing gasket is placed on the suitable position of detection cell front surface, liquid-inlet and outlet is exposed to the middle vacancy position of sealing gasket to form miniature test chamber.Then sheet working electrode (as Characterization of Boron-Doped Diamond Thin Film Electrode) is placed on sealing gasket, working electrode surface is made to be exposed in test chamber, face adds working electrode fixed head on the working electrode (s again, working electrode lead-in wire will be derived from the hole of fixed head central authorities simultaneously.Subsequently two gib screws added and tighten gradually simultaneously, working electrode is fastened on detection cell, and forming the miniature test chamber of a sealing at working electrode surface.Liquid inlet duct be arranged on the rear surface of detection cell body and perpendicular to rear surface, be connected with the liquid inlet channel in detection cell body.Liquid outlet tube of holding concurrently to electrode be arranged on the upper surface of detection cell body and perpendicular to upper surface, be connected with liquid outflow channel and perpendicular to the outflow fluid path of test chamber.Contrast electrode be arranged on the rear surface of detection cell body and perpendicular to rear surface, be connected in the horizontal direction with the outflow fluid path of test chamber.To ensure after all parts installs that the sealing of whole detection cell does not well have seepage.
Particularly, Characterization of Boron-Doped Diamond Thin Film Electrode can be used as working electrode, Ag/AgCl electrode is used as contrast electrode, and platinum electrode is used as electrode, Na
2sO
4solution is the COD value test that carrier fluid carries out sample.The detection cell assembled is connected with flow injection injector, simultaneously by three of detection cell Electrode connection on electrochemical workstation or analyser.With flow injection injector by carrier fluid Na
2sO
4solution is transported to three-electrode electro Chemical detection cell constantly, and carrier fluid enters from detection cell liquid inlet duct, flows out to electrode (liquid outlet tube).Flow through miniature test chamber in the process and with the surface contact of working electrode.By electrochemical workstation or analyser, a suitable voltage is applied to working electrode, as 2.8V, then detect the electric current obtained and be background current.By the time, after background current reaches stable state, just sample analysis can be carried out.
The water body example flow injection injector of certain volume (as 10 μ L) containing certain organic contaminant is injected carrier fluid, and sample will be brought into miniature test chamber by carrier fluid and contact with working electrode surface.Under the voltage that working electrode applies, the organism in sample, by oxidized and produce certain electric current, shows as a current peak.By the current peak recorded (or under peak area) with contrast with the calibration curve that standard model draws, just can draw the COD value in sample.Organic concentration is higher, and current peak higher (or under peak, area is larger), the COD value therefore recorded is also higher.
Embodiment 1
Bioassay standard sample.Take Characterization of Boron-Doped Diamond Thin Film Electrode as working electrode, Ag/AgCl electrode is contrast electrode, and platinum electrode is to electrode, 0.1MNa
2sO
4solution (pH=1.0) is carrier fluid, and the detection voltage that working electrode applies is 2.8V, and carrier fluid flow velocity is that 0.2mL/min is as experiment condition.When carrier fluid is by after during working electrode, reasons for its use electric current reaches stable state, inject the various standard model solution of the different COD value of 10 μ L respectively, comprise glucose, Potassium Hydrogen Phthalate, phenol, benzoic acid, salicylic acid, maleic acid and ethane diacid.Record current peak that each sample produces on the working electrode (s (or under peak area), then with the COD value of each sample for horizontal ordinate, corresponding current peak (or under peak area) is that ordinate draws calibration curve.The calibration curve obtained is have good linear relationship (linearly dependent coefficient R within the scope of 2.5 – 120mg/L in COD value
2>0.99).
Embodiment 2
Measure the COD value of real wastewater samples.Take Characterization of Boron-Doped Diamond Thin Film Electrode as working electrode, Ag/AgCl electrode is contrast electrode, and platinum electrode is to electrode, 0.1MNa
2sO
4solution (pH=1.0) is carrier fluid, and the detection voltage that working electrode applies is 2.8V, and carrier fluid flow velocity is that 0.2mL/min is as experiment condition.When carrier fluid is by after reasons for its use electric current reaches stable state during working electrode, inject the 5 kind different wastewater samples of 10 μ L from chemical plant and food factory respectively.The current peak of different wastewater samples recorded and the calibration curve of acquisition are contrasted, draws the COD value in wastewater sample.Adopt traditional COD bioassay standard method (potassium dichromate method) to measure above-mentioned wastewater sample simultaneously, draw COD value.Two groups of COD value that contrast obtains can calculate and measure the recovery of real wastewater samples is 96% ~ 106%, relative standard deviation RSD be less than 5.5% (n=7).
Claims (8)
1. an electrochemical investigating pond, comprise detection cell body (1), sealing gasket (2), working electrode (3), to electrode (6) and contrast electrode (10), it is characterized in that, the one side of described sealing gasket (2) is close to the front surface of detection cell body (1), and another side is had vacant position at middle part; Described working electrode (3) is pressed in the one side that described sealing gasket (2) has vacant position by electrode fixing device (4), thus forms test chamber (7) by described detection cell body (1), described working electrode (3) with described sealing gasket (2).
2. electrochemical investigating pond as claimed in claim 1, it is characterized in that, described sealing gasket (2) has the thickness of 10 μm ~ 1000 μm.
3. electrochemical investigating pond as claimed in claim 1, it is characterized in that, described electrode fixing device (4) is electrode fixed head.
4. electrochemical investigating pond as claimed in claim 1, it is characterized in that, described electrode fixing device (4) utilizes screw (5) described working electrode (3) and described sealing gasket (2) to be fastened on the front surface of described detection cell body (1).
5. electrochemical investigating pond as claimed in claim 1, it is characterized in that, described electrochemical investigating pond also comprises liquid inlet duct (9), described liquid inlet duct (9) be positioned at described detection cell body upper surface and perpendicular to described upper surface.
6. electrochemical investigating pond as claimed in claim 1, is characterized in that, described contrast electrode (10) be positioned at detection cell body rear surface and perpendicular to described rear surface.
7. electrochemical investigating pond as claimed in claim 1, is characterized in that, is describedly connected with the outflow fluid path of described test chamber (7) is vertical electrode (6).
8. electrochemical investigating pond as claimed in claim 1, it is characterized in that, described contrast electrode (10) is connected in the horizontal direction with the outflow fluid path of described test chamber (7).
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201520698992.XU CN204925023U (en) | 2015-09-10 | 2015-09-10 | Electrochemical detection pond |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201520698992.XU CN204925023U (en) | 2015-09-10 | 2015-09-10 | Electrochemical detection pond |
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| Publication Number | Publication Date |
|---|---|
| CN204925023U true CN204925023U (en) | 2015-12-30 |
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ID=54974137
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201520698992.XU Expired - Fee Related CN204925023U (en) | 2015-09-10 | 2015-09-10 | Electrochemical detection pond |
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Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105092676A (en) * | 2015-09-10 | 2015-11-25 | 鞠文军 | Electrochemical detection cell |
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2015
- 2015-09-10 CN CN201520698992.XU patent/CN204925023U/en not_active Expired - Fee Related
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105092676A (en) * | 2015-09-10 | 2015-11-25 | 鞠文军 | Electrochemical detection cell |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20151230 Termination date: 20160910 |
|
| CF01 | Termination of patent right due to non-payment of annual fee |