ClO in water2Detection method of low detection limit of
阅读说明：本技术 一种水中ClO2-的低检出限的检测方法 (ClO in water2Detection method of low detection limit of ) 是由 郎爽 李曙光 贾丽 周阳 周欣燃 马立利 于 2021-08-27 设计创作，主要内容包括：本发明涉及一种水中ClO-(2)～(-)的低检出限的检测方法,使用光热电位分析仪,包括以下步骤：S100：使用蒸馏水配置ClO-(2)～(-)溶液,在ClO-(2)～(-)溶液中加入磷酸盐缓冲溶液,调节pH值为6-8；S200：在步骤S100所得的溶液中加入碘化钾,溶解后,得到待反应溶液；S300：调节所述待反应溶液的pH值为2-3,得到反应溶液,并立即将反应溶液放至暗处反应5-6min；S400：调节步骤S300所得溶液的pH值为3-5,同时加入淀粉指示剂和碘化钾,混合溶解,当光度电极开始反馈信号时,立即使用硫代硫酸钠标准溶液滴定；S500：记录滴定终点时所消耗的硫代硫酸钠标准溶液的体积并计算水中ClO-(2)～(-)的浓度。(The invention relates to a method for preparing ClO in water 2 ‑ The detection method of low detection limit, using a photothermal potential analyzer, comprising the steps of: s100: preparation of ClO Using distilled Water 2 ‑ Solution in ClO 2 ‑ Adding phosphate buffer solution into the solution, and adjusting the pH value to 6-8; s200: adding potassium iodide into the solution obtained in the step S100, and dissolving to obtain a solution to be reacted; s300: adjusting the pH value of the solution to be reacted to 2-3 to obtain a reaction solution, and immediately placing the reaction solution in a dark place for reaction for 5-6 min; s400: adjusting the pH value of the solution obtained in the step S300 to 3-5, simultaneously adding a starch indicator and potassium iodide, mixing and dissolving, and immediately titrating by using a sodium thiosulfate standard solution when a photometric electrode starts to feed back a signal; s500: record the volume of sodium thiosulfate standard solution consumed at the end of the titration and calculate the ClO in the water 2 ‑ The concentration of (c).)
1. ClO in water2 -The method for detecting a low detection limit of (2), wherein the method for detecting a low detection limit uses a photothermal potential analyzer, comprising the steps of:
s100: preparation of ClO Using distilled Water2 -Solution in ClO2 -Adding phosphate buffer solution into the solution, and adjusting the pH value to 6-8;
s200: adding potassium iodide into the solution obtained in the step S100, and dissolving to obtain a solution to be reacted;
s300: adjusting the pH value of the solution to be reacted to 2-3 to obtain a reaction solution, and immediately placing the reaction solution in a dark place for reaction for 5-6 min;
s400: adjusting the pH value of the solution obtained in the step S300 to 3-5, simultaneously adding a starch indicator, mixing and dissolving, and immediately titrating by using a sodium thiosulfate standard solution when a photometric electrode starts to feed back a signal;
s500: record the volume of sodium thiosulfate standard solution consumed at the end of the titration and calculate the ClO in the water2 -The concentration of (c).
2. ClO in water according to claim 12 -The method for detecting a low detection limit of (1), wherein in the method for detecting a low detection limit of (1), ClO in water2 -The concentration calculation formula is as follows:
in formula (1): c is the concentration of a sodium thiosulfate standard solution, mol/L; v is configuration ClO2 -Volume of solution, mL; vDVolume of sodium thiosulfate standard solution consumed, mL; 16.863:molar mass of (a), g/moL.
3. ClO in water according to claim 22 -The method for detecting a low detection limit of (1), wherein in step S100, a phosphate buffer solution is added to adjust the pH to 7.
4. ClO in water according to claim 22 -The method for detecting a low detection limit of (1), wherein in step S200, the amount of potassium iodide added is 1.0 to 1.5g by mass.
5. ClO in water according to claim 22 -The method for detecting a low detection limit of (1), wherein in step S300, the pH of the solution to be reacted is adjusted to 2 using concentrated hydrochloric acid.
6. ClO in water according to claim 22 -The method for detecting a low detection limit of (2), wherein in step S400, the pH of the solution obtained in step S300 is adjusted to 3 to 5 using the phosphate buffer solution; the mass fraction of the starch indicator is 4%.
7. ClO in water according to any of claims 6 or 42 -The detection method with the low detection limit is characterized in that in the step S400, potassium iodide and a starch indicator are added simultaneously, the mass-to-volume ratio of the potassium iodide to the starch indicator is 1g (15-18) mL, and the mass ratio of the potassium iodide added in the step S400 to the potassium iodide added in the step S200 is 1 (15-20).
8. ClO in water according to claim 62 -The method for detecting a low detection limit of (2), wherein in step S400, the same sample solution is simultaneously detected using two photometric electrodes, the light wavelengths of which are 640nm and 590nm, respectively.
9. ClO in water according to claim 82 -The detection method of (1) is characterized in that the ratio of the illuminance of light of 590nm to 640nm is 1 (5-7), and the illuminance of light of 640nm is 0.01-0.05 lux.
10. ClO in water according to claim 92 -The method for detecting a low detection limit of (1), wherein the volume of the final titration end point is 1/2+ r which is the sum of the volumes corresponding to the titration end points of the two titration curves of the two photometric electrodes;
the correction coefficient is r, and the calculation formula is as follows:
in the formula (2), L1The ratio of the illuminance of 590nm to 640nm is 1 (5-7), L2The ratio of the illuminance of 640nm to that of 590nm (5-7) is 1, and the lux is 640 nm.
Technical Field
The invention belongs to ClO in water2 -The technical field of content determination, in particular to ClO in water2 -The detection method of (4) is a low detection limit detection method.
Background
For detecting various chloride ions in drinking water, in particular to ClO in water2、Cl2、ClO2 -And ClO3 -The skilled person has studied continuous iodometric methods, and developed test methods for the above-mentioned interconversion or reaction between chloride ions in various valence states. However, for ClO alone in water2 -The detection has the problem that the detection limit concentration is higher. At present, ClO in Water2 -The concentration needs to reach 0.2mg/L, and the trace ClO in the water can be detected by an iodometry method2 -The detection limit is high, and the deep research and the wide popularization and application of the detection of various chloride ions in the domestic drinking water are not facilitated.
Disclosure of Invention
Aiming at the problems, the invention uses ClO alone in pure water2 -Research on ClO as an object of study2 -The titration method by the low detection limit iodometry. The invention provides a method for preparing ClO in water2 -The detection method of low detection limit, using a photothermal potential analyzer, comprises the steps of:
s100: preparation of ClO Using distilled Water2 -Solution in ClO2 -Adding phosphate buffer solution into the solution, and adjusting the pH value to 6-8;
s200: adding potassium iodide into the solution obtained in the step S100, and dissolving to obtain a solution to be reacted;
s300: adjusting the pH value of the solution to be reacted to 2-3 to obtain a reaction solution, and immediately placing the reaction solution in a dark place for reaction for 5-6 min;
s400: adjusting the pH value of the solution obtained in the step S300 to 3-5, simultaneously adding a starch indicator, mixing and dissolving, and immediately titrating by using a sodium thiosulfate standard solution when a photometric electrode starts to feed back a signal;
s500: record the volume of sodium thiosulfate standard solution consumed at the end of the titration and calculate the ClO in the water2 -The concentration of (c).
In the detection method, ClO in water2 -The concentration calculation formula is as follows:
in formula (1): c is the concentration of a sodium thiosulfate standard solution, mol/L; v is configuration ClO2 -Volume of solution, mL; vDVolume of sodium thiosulfate standard solution consumed, mL; 16.863:molar mass of (a), g/moL.
The detection method of the invention aims at the ClO in water2 -The problem of low detection limit when the iodometry is used for detection is explored for separately aiming at ClO2 -The high-sensitivity iodometry utilizes the principles of potentiometric titration and photometric titration, and promotes the ClO through the addition sequence of phosphate buffer solution, potassium iodide and starch indicator and the coordination of pH value changes of different steps2 -Fully dissolving and reacting with potassium iodide, and performing color reaction on the generated iodine simple substance and a starch indicator, thereby effectively reducing the ClO in water on the premise of not adding other reagents or substances2 -The detection limit of (2). Particularly, the invention achieves the purpose of controlling different reactions by controlling the pH values of different steps, so that the whole detection process is controllable in stages.
Optionally, in step S100, ClO with different concentrations is prepared using distilled water and chlorite standard2 -Standard solution of the ClO2 -The concentration of the standard solution is less than 0.2 mol/L.
Optionally, in step S100, the phosphate buffer solution is a sodium phosphate buffer solution or a potassium phosphate buffer solution, specifically NaH2PO4And Na2HPO4Solutions or K2HPO4And KH2PO4And (3) solution.
Preferably, in step S100, a phosphate buffer solution is added to adjust the pH to 7.
Optionally, in step S200, the amount of potassium iodide added is 1.0-1.5 g. So far, the solution to be reacted is fully dissolved with ClO2 -Potassium iodide is adjusted to pH value of 6-8 by phosphate buffer solution, and the research shows that in the solution environment of the pH value, the potassium iodide is most fully dissolved and is not dissolved with ClO2 -A reaction of potassium iodide with ClO in step S300 takes place2 -The reaction provides a good basis.
Optionally, in step S300, the pH of the solution to be reacted is adjusted to 2 to 3 using concentrated hydrochloric acid, and preferably, the pH of the solution to be reacted is adjusted to 2.
In step S300, when the pH value of the solution to be reacted is 2-3, the iodide ions and the ClO in the solution can be started2 -The reaction solution is immediately placed in the dark for reaction for 5-6min to avoid sublimation of the generated iodine, and the step S400 is also carried out in the dark in the whole process to prevent sublimation of the iodine. The dark place in the invention refers to an environment which is not light-tight.
The electrodes of the photothermal potential analyzer are a platinum ring electrode and a photometric electrode, the platinum ring electrode and the photometric electrode detect the same sample to obtain two titration curves, the detection results calculated by the corresponding curves of the two electrodes are convenient to compare, and the accuracy of the detection of the photometric electrode is verified.
Optionally, in step S400, the phosphate buffer solution is used to adjust the pH value of the solution obtained in step S300 to 3-5, preferably to 4, and the reaction between the iodine simple substance and starch is started; the mass fraction of the starch indicator is 4%.
Further optionally, in step S400, potassium iodide and a starch indicator are added simultaneously, the mass-to-volume ratio of potassium iodide to starch indicator is 1g (15-18) mL, and the mass ratio of potassium iodide added in step S400 to that added in step S200 is 1 (15-20).
The concentration of the sodium thiosulfate standard solution is 0.05 mol/L.
In step S400 of the detection method of the invention, the starch indicator reacts with the iodine simple substance generated in step S300, and the invention unexpectedly discovers that the concentration of iodine ions in the solution is increased by adding a small amount of potassium iodide together with the starch indicator, which is beneficial to ClO2 -In the case of a small content, that is, in the case of a small amount of iodine, the color development of iodine and starch is promoted.
Optionally, in step S400, two photometric electrodes are used to detect the same sample solution at the same time, and the light wavelengths of the two photometric electrodes are 640nm and 590nm, respectively.
Preferably, the ratio of the illuminance of the light of 590nm to that of 640nm is 1 (5-7), and the illuminance of the light of 640nm is 0.01-0.05 lux.
Two photometric electrodes are arranged closely to each other due to ClO in water2 -The concentration of the starch indicator is very low, so that compared with the blue color developed by the reaction of the starch indicator and the saturated iodine solution, the blue color developed by the solution after the reaction of the starch indicator and the iodine simple substance is relatively shallow and uniform, and the two photometric electrodes are closely arranged, so that the errors caused by the fact that light passes through and detects different positions of the solution due to the small difference of the positions of the two photometric electrodes can be basically ignored.
In the detection method, in the step S400 of the reaction of the starch and the iodine simple substance, the starch indicator and the potassium iodide which are added in a certain proportion during the matching of the proper pH value promote the reaction of the low-content iodine simple substance and the starch, and enhance the color development. In addition, the light source used by the photometric electrode is researched, and the change of the absorbance value of the reaction product reaching the titration end point under the two wavelengths is very obvious compared with the absorbance value at the beginning of titration, so that the titration result is judged more accurately. The photometric electrode is used for measuring the absorbance value of the solution in the titration process, the maximum absorbance value is not concerned by the spectrophotometry, but the change of the absorbance value at the beginning and the end of the titration, namely the difference between the absorbance value and the maximum absorbance value is concerned, and the larger the difference is, the higher the detection sensitivity and accuracy are. The light intensity of the photometric electrode provides a good light detection environment for the detected solution on the basis of ensuring the detection sensitivity and accuracy, and prevents iodine simple substance from sublimating to the maximum extent.
In addition, the invention uses the double-photometric electrode for detection, two photometric titration curves can be generated, the two photometric titration curves are verified mutually, and in order to avoid the influence of the system error of the two curves, the invention researches the calculation of the titration volume and reasonably corrects the titration volume.
Specifically, the volume of the final titration endpoint is 1/2+ r which is the sum of the volumes corresponding to the titration endpoints of the two titration curves of the two photometric electrodes.
The correction coefficient is r, and the calculation formula is as follows:
in the formula (2), L1The ratio of the illuminance of 590nm to 640nm is 1 (5-7), L2The ratio of the illuminance of 640nm to that of 590nm (5-7) is 1, and the lux is 640 nm.
Drawings
FIG. 1 is a schematic view of the connection of a fluid feed transmission unit and a burette of a photothermal potential analyzer.
Fig. 2 is a structural view of the fluid-feeding transmission unit.
Fig. 3 is a perspective view of the fluid-fed transmission unit.
In the attached drawings, 1-a fluid feed transmission unit; 2-burette; 11-a telescopic assembly; 12-a main motor; 13-a main lead screw; 14-a subdivision motor; 15-subdivision lead screw; 16-a drive gear; 17-big nut; 18-a proximity switch; 19-limit switch; 21-a pipe body; 22-pump head.
Detailed Description
The following examples and comparative examples used a conventional photothermal potential analyzer, and conducted ClO in water according to the present invention after replacing the conventional photothermal potential analyzer liquid feeding device and burette with the liquid feeding actuator unit and burette of the 202110808763.9 patent application2 -The detection method of (2) is a method of detecting a low detection limit, wherein electrodes used are a platinum ring electrode and a photometric electrode.
Example 1
ClO in Water as described in this example2 -The detection method of low detection limit using a photothermal potential analyzer, comprising the steps of:
s100: ClO formulated using distilled water and chlorite standards2 -Standard solution (0.15mol/L) in ClO2 -Adding NaH into the solution2PO4And Na2HPO4Buffering solution, regulating pH value to 6;
the chlorite standard sample is a water quality chlorite environment standard sample, meets the national standard GSB 07-2975-;
s200: adding 1g of potassium iodide into the solution obtained in the step S100, and fully dissolving to obtain a solution to be reacted;
s300: adjusting the pH value of the solution to be reacted to 3 by using concentrated hydrochloric acid to obtain a reaction solution, and immediately putting the reaction solution in a dark place for reaction for 5 min;
s400: using NaH2PO4And Na2HPO4Adjusting the pH value of the solution obtained in the step S300 to be 3 by using a buffer solution, adding 1ml of 4% starch indicator, mixing and dissolving, and immediately titrating by using a 0.05mol/L sodium thiosulfate standard solution when a photometric electrode starts to feed back a signal;
the wavelength of the optical signal used is 570 nm.
S500: record the volume of sodium thiosulfate standard solution consumed at the end of the titration and calculate the ClO in the water2 -The concentration of (c).
In the detection method, ClO in water2 -The concentration calculation formula is as follows:
in formula (1): c is the concentration of the sodium thiosulfate standard solution, and is 0.05 mol/L; v is configuration ClO2 -Volume of solution, mL; vDVolume of sodium thiosulfate standard solution consumed, mL; 16.863:molar mass of (a), g/moL; vDVolume corresponding to potential at 1/2 which is the sum of the maximum potential and the minimum potential on the end jump line of the E-V curve.
In this embodiment, a platinum ring electrode and a photometric electrode are used to detect the same sample, so as to obtain two titration curves, and the two calculation results are compared with each other, so that the relative deviation R is within 5%.
In the above formula, R represents relative deviation,%; c1Mg/g is the calculation result of the detection of the photometric electrode; c2The calculation result of the pH composite electrode detection is mg/g.
Comparative example 1
ClO in Water as described in this comparative example2 -The method for detecting a low detection limit of (2) is the same as in example 1, except that 1ml of 4% starch indicator is added to the reaction solution of step S300, mixed and dissolved, and then placed in the dark to react for 5 min; no starch indicator is added in step S400.
Example 2
ClO in Water as described in this example2 -The method for detecting a low detection limit of (2) is the same as in example 2, except that NaH is added in step S1002PO4And Na2HPO4Buffering the solution, and adjusting the pH value to 7.
Example 3
ClO in Water as described in this example2 -The method for detecting a low detection limit of (2) is the same as in example 2, except that NaH is added in step S1002PO4And Na2HPO4Buffering the solution, and adjusting the pH value to 8.
Example 4
ClO in Water as described in this example2 -The detection method of (4) is the same as in example 3 except that, in step S300, the pH of the solution to be reacted is adjusted to 2 using concentrated hydrochloric acid.
Example 5
ClO in Water as described in this example2 -The detection method of (4) is the same as in example 3 except that, in step S300, the pH of the solution to be reacted is adjusted to 1 using concentrated hydrochloric acid.
Example 6
ClO in Water as described in this example2 -The method for detecting a low detection limit of (2) is the same as in example 5, except that NaH is used in step S4002PO4And Na2HPO4The buffer solution adjusts the pH of the solution obtained in step S300 to 4.
Example 7
ClO in Water as described in this example2 -The method for detecting a low detection limit of (2) is the same as in example 5, except that NaH is used in step S4002PO4And Na2HPO4The buffer solution adjusts the pH of the solution obtained in step S300 to 5.
Example 8
ClO in Water as described in this example2 -The method for detecting a low detection limit of (2) is the same as in example 7, except that in step S400, potassium iodide and a starch indicator are added simultaneously, the mass-to-volume ratio of potassium iodide to the starch indicator is 1g:15mL, and the mass ratio of potassium iodide added in step S400 to that added in step S200 is 1:20, that is, the detection method isIn this step, 0.05g of potassium iodide was added.
Example 9
ClO in Water as described in this example2 -The method for detecting a low detection limit in (2) is the same as in example 9, except that the mass ratio of potassium iodide added in step S400 to that added in step S200 is 1:15, that is, 0.067g of potassium iodide is added in this step.
Example 10
ClO in Water as described in this example2 -The method for detecting a low detection limit in (2) is the same as in example 9, except that the mass ratio of potassium iodide added in step S400 to that added in step S200 is 1:14, that is, 0.071g of potassium iodide is added in this step.
Example 11
ClO in Water as described in this example2 -The method for detecting a low detection limit of (2) is the same as in example 10, except that the mass-to-volume ratio of potassium iodide to the starch indicator in step S400 is 1g:18 mL.
Example 12
ClO in Water as described in this example2 -The method for detecting a low detection limit of (2) is the same as in example 10, except that the mass-to-volume ratio of potassium iodide to the starch indicator in step S400 is 1g:19 mL.
Example 13
ClO in Water as described in this example2 -The method for detecting a low detection limit in (1) is the same as in example 12, except that in step S400, the same sample solution is simultaneously detected using two photometric electrodes, the two photometric electrodes are closely attached to each other, the wavelengths of light of the two photometric electrodes are 640nm and 590nm, respectively, the ratio of the illuminance of light of 590nm to 640nm is 1:5, and the illuminance of light of 640nm is 0.01 lux.
Example 14
ClO in Water as described in this example2 -The method for detecting a low detection limit in (2) is the same as in example 14, except that the ratio of the illuminance of the 590nm and 640nm light in step S400 is 1: 7.
Example 15
ClO in Water as described in this example2 -The method for detecting a low detection limit in (2) is the same as in example 14, except that the ratio of the illuminance of the 590nm and 640nm light in step S400 is 1: 8.
Example 16
ClO in Water as described in this example2 -The method for detecting a low detection limit in (2) is the same as in example 15, except that the illuminance of 640nm light in step S400 is 0.05 lux.
Example 17
ClO in Water as described in this example2 -The method for detecting a low detection limit in (2) is the same as in example 15, except that the illuminance of 640nm light in step S400 is 0.06 lux.
Example 18
ClO in Water as described in this example2 -The method for detecting a low detection limit of (2) is the same as in example 17, except that the volume V of the titration end point at the time of calculationD1/2+ r which is the sum of the volumes corresponding to the titration end points of the two titration curves for the two photometric electrodes,
the correction coefficient is r, and the calculation formula is as follows:
in the formula (2), L1The ratio of the illuminance of 590nm to 640nm is 1:7, L2The ratio of the illuminance of 640nm to that of 590nm was 7:1, and the illuminance of 640nm was 0.05 lux. Calculated r is 0.077.
Example 19
ClO in Water as described in this example2 -The detection method of (2) is the same as in example 19, except that ClO is disposed in step S1002 -The concentration of the standard solution was 0.1 mol/L.
Example 20
ClO in Water as described in this example2 -The method for detecting a low detection limit of (2) is the same as in example 19,except that step S100 configures the ClO2 -The concentration of the standard solution was 0.08 mol/L.
The calculation method of the accuracy in table 1 is:
TABLE 1 comparison of the effects of the examples and comparative examples
Accuracy (%)
Accuracy (%)
Example 1
8.0
Example 12
5.9
Example 2
7.8
Example 13
3.8
Example 3
8.3
Example 14
3.5
Example 4
7.4
Example 15
4.1
Example 5
7.8
Example 16
3.3
Example 6
7.0
Example 17
3.8
Example 7
7.7
Example 18
2.9
Example 8
5.7
Example 19
3.0
Example 9
5.5
Example 20
3.1
Example 10
6.0
Comparative example 1
13.6
Example 11
5.2
As can be seen from the above table, the ClO in water of the present invention2 -The detection method with low detection limit can well detect the ClO with low concentration2 -And ClO with2 -The standard concentration error of (2) is smaller, and the standard concentration error of the (2) is smaller for ClO in water of 0.08-0.15mol/L in the example2 -Can achieve better detection effect, and the lowest detection limit is 0.08 mol/L. In examples 1 to 12, the relative errors of the detection results obtained by the detection method using the platinum ring electrode and the photometric electrode are within 5%; in examples 13 to 17, 3 titration curves obtained by detecting the platinum ring electrode and the two photometric electrodes were calculated according to the calculation method of example 1 to obtain 3 detection results, wherein the relative error between the results of the photometric electrode of 590nm and the platinum ring electrode and the relative error between the results of the photometric electrode of 640nm and the platinum ring electrode are both within 5%; in examples 18 to 20, the results of the measurement of the photometric electrode were calculated from the two titration curves of the two photometric electrodes, and the results were compared with those of the platinum ring electrode, and the relative errors were within 3%.
To facilitate understanding of the photothermal potential analyzer used in the present invention, the structure of the fluid feeding transmission unit and the burette is supplemented as follows:
as shown in fig. 1, the burette 2 comprises a tube body 21 and a pump head 22 located in the tube body for pumping the titration liquid; the feeding transmission unit 1 pushes and pulls the pump head 22, so as to draw the titration liquid into the tube body 21 or inject the titration liquid in the tube body 21 into a beaker, and the beaker stores the liquid to be titrated.
A reversing mechanism is provided on the pump head 22 to draw the washing liquid and the titration liquid, respectively.
As shown in fig. 2 to 3, the fluid feed transmission unit 1 includes a telescopic assembly 11, a main motor 12, a main screw 13, a sub-divided motor 14, a sub-divided screw 15, a drive gear 16, and a large nut 17. The top end of the telescopic component 11 is connected with the pump head 22, and the bottom end of the telescopic component 11 is provided with a threaded hole which is sleeved on the subdivision screw rod 15;
one end of the subdivision screw rod 15 is fixedly connected with the top end of the large screw nut 17, the bottom end of the large screw nut is provided with a threaded hole, so that the large screw nut 17 can be sleeved on the main screw rod 13, and the circumferential side surface of the large screw nut 17 is provided with a gear corresponding to the driving gear 16, so that the driving gear 16 can drive or limit the rotation of the large screw nut 17; the driving gear 16 is connected with an output shaft of the subdivision motor 14; the main screw 13 is connected to an output shaft of the main motor 12.
Limit switches 19 are provided at upper and lower portions of the telescopic assembly 11 so that the telescopic assembly 11 can be only extended up and down and cannot be rotated.
The thread directions of the main lead screw 13 and the sub-lead screw 15 are the same, and the lead of the main lead screw 13 is larger than that of the sub-lead screw 15.
The axis of the driving gear 16 is parallel to the axis of the sub-divided screw 15, and the tooth width of the driving gear 16 is larger than that of the peripheral gear of the large screw 17, so that the large screw 17 and the driving gear 16 can slide relatively in the axial direction.
Main motor 12 rotates, drives main lead screw 13 rotatory, and the drive ratio of main lead screw 13 and main motor 12 is 1:5, the lead of the main lead screw is 5mm, and under the transmission effect, the subdivision of the main motor in step 1/4 can realize the subdivision of 20000/1 of the liquid feeding transmission unit. The large screw 17 is rotationally locked by the driving gear 16, the large screw 17 slides along the thread on the main screw 13 under the driving of the main screw 13, and then the subdivision motor 14 and the telescopic assembly 11 are driven to move up and down, and the pump head 22 is rapidly lifted.
When the dripping is performed at a slow speed, the main motor 12 is in a power-on locking state, and the main screw 13 does not rotate at the moment; the subdivision motor 14 rotates to drive the driving gear 16 to rotate, the large screw 17 rotates in the circumferential direction under the rotation of the driving gear 16, and the large screw 17 slides along the thread on the main screw 13 to ascend or descend; the subdivision screw rod 15 rotates along with the large screw nut 17, so that the telescopic assembly 11 slides relatively along the subdivision screw rod 15 and moves relatively in the direction opposite to the direction of the large screw nut 17; since the lead of the main screw 13 is greater than the lead of the subdividing motor 14, the lifting speed of the large nut 17 is different from the lifting speed of the telescopic assembly 11, and finally the actual lifting amount of the telescopic assembly 11 is the difference between the lifting amount of the large nut 17 and the lifting amount of the telescopic assembly 11 relative to the subdividing screw 15. A proximity switch 18 is provided at the lower end of the large nut 17, and the initial position of the large nut 17 is reset by the proximity switch 18. The main motor 12 operates to lower the large nut 17 until the large nut 17 contacts the proximity switch 18, at which time the position of the large nut 17 is the initial position.
The use of the above described fluid-fed transmission unit 1 is as follows:
s1, determining the single liquid feed amount to obtain the single pump head movement amount;
s2, dividing a fast titration stage and a slow titration stage according to the movement amount of the pump head to perform titration;
and S3, detecting by an electrode, confirming the next liquid feeding amount, and repeating the process until the titration is finished.