CN106841182A - Simultaneously and rapidly monitor the on-line computing model and method of silicate and phosphate radical in water - Google Patents

Simultaneously and rapidly monitor the on-line computing model and method of silicate and phosphate radical in water Download PDF

Info

Publication number
CN106841182A
CN106841182A CN201611246753.6A CN201611246753A CN106841182A CN 106841182 A CN106841182 A CN 106841182A CN 201611246753 A CN201611246753 A CN 201611246753A CN 106841182 A CN106841182 A CN 106841182A
Authority
CN
China
Prior art keywords
reagent
measuring cell
silicate
pipeline
phosphate radical
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201611246753.6A
Other languages
Chinese (zh)
Inventor
陈强
柳杰
苑海涛
朱亚利
赵波
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Beijing Research Institute of Chemical Engineering and Metallurgy of CNNC
Original Assignee
Beijing Research Institute of Chemical Engineering and Metallurgy of CNNC
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 Beijing Research Institute of Chemical Engineering and Metallurgy of CNNC filed Critical Beijing Research Institute of Chemical Engineering and Metallurgy of CNNC
Priority to CN201611246753.6A priority Critical patent/CN106841182A/en
Publication of CN106841182A publication Critical patent/CN106841182A/en
Pending legal-status Critical Current

Links

Classifications

    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/75Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated
    • G01N21/77Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated by observing the effect on a chemical indicator
    • G01N21/78Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated by observing the effect on a chemical indicator producing a change of colour

Abstract

A kind of on-line computing model for providing silicate and phosphate radical in simultaneously and rapidly monitoring water of the invention, the on-line computing model includes chemical stream, and the control system for controlling chemical stream;The on-line monitoring method, it is in acid condition, silicate and phosphate radical all generate the complex compound of molybdenum yellow and phosphorus the molybdenum Huang of yellow with ammonium molybdate reaction, silicate and phosphate concentration summation are obtained by detection and analysis, add citric acid, the yellow complex compound of phosphorus molybdenum will be decomposed, and the concentration for drawing independent silicate is tested and analyzed with this, and the concentration of silicate and phosphate radical in sample is respectively obtained successively.The present invention is once chemically reacted with a monitoring system, and the content of phosphate radical and silicate in solution is calculated by surveying the absorbance of different step.Because two kinds of elements of measurement have only used a set of reaction and detection part, the purchase cost for so reducing, maintenance cost reduces the usage amount of reagent, reduces the probability of error;And save installing space.

Description

Simultaneously and rapidly monitor the on-line computing model and method of silicate and phosphate radical in water
Technical field
The invention belongs to the device of silicate and phosphate radical in automatic on-line monitoring water, it is particularly suitable for Fast synchronization monitoring The on-line computing model and method of silicate and phosphate radical in water.
Background technology
In the prior art, there is the analyzer for monitoring silicate and phosphate radical simultaneously, Fig. 1 is its schematic diagram.This analysis Instrument has two sets of colorimetric pools and photometric detection device, and by silicate and phosphate radical, each chemical stream enters into ratio to water sample respectively Color pond is measured by adding respective chromogenic reaction reagent again, actually control simply two instruments and display part diversity It is combined, the stream and computational methods to the measurement of phosphate radical and silicate are not improved.Distinguish reagent adding to two In individual reaction detection device, measure twice, then shown on same display.It is substantially simple a silicate Analyzer and a phosphate analytical instrument simply merge what is got.Such analyzer is actually needed the sample difference to gathering Carry out a silicate monitoring and a phosphate radical monitoring is combined the result monitored twice and obtains a result, thus it is time-consuming Chemical reagent is wasted, error probability is high.
The content of the invention
It is an object of the invention to provide silicate and phosphate radical in a kind of simultaneously and rapidly monitoring water on-line computing model and Method, it can be able to obtain silicate and phosphate radical monitoring result by once chemically reacting.
Realize the technical scheme of the object of the invention:The on-line monitoring of silicate and phosphate radical in a kind of simultaneously and rapidly monitoring water Instrument, the on-line computing model includes chemical stream, and the control system for controlling chemical stream;Described chemical stream includes measurement Pond, the pipeline being connected with measuring cell, and the peristaltic pump set on pipeline;Wherein, water sample and several reagent by with The pipeline of measuring cell connection, peristaltic pump enter measuring cell, while several magnetic valves are additionally provided with the pipeline, by magnetic valve control Make different reagents and enter measuring cell when different;
Described control system includes computer system, the input block being connected with computer system, output unit, screen Display unit, photometric detection unit and power supply;Wherein, input block is contact action, and controlization is input into computer system Learn the work order of stream;Computer system will control the work order of chemical stream to deliver to chemical stream by output unit, Simultaneously in screen display unit display working condition;Photometric detection unit is after the work order for receiving computer system to surveying Amount pond carries out photometric detection, while testing result is delivered into computer system.
The on-line computing model of silicate and phosphate radical, connects with measuring cell in a kind of simultaneously and rapidly monitoring water as described above The magnetic valve for being passed through air is set on the pipeline for connecing, by air stirring so that water sample and reagent are thoroughly mixed;Go out in measuring cell Drain valve is set on mouth pipeline.
The on-line computing model of silicate and phosphate radical, described control system in a kind of simultaneously and rapidly monitoring water as described above System is provided with the relay of multichannel independence as output switch parameter, for the long-range connection upper limit, lower limit alarm lamp;When sample in measuring cell When concentration exceedes the upper limit or the lower limit less than setting of setting, the actuating of relay makes the closing of contact, sends alarm signal.
The on-line computing model of silicate and phosphate radical in a kind of simultaneously and rapidly monitoring water as described above, described water sample and Several reagent enters measuring cell by the pipeline that is connected with measuring cell, peristaltic pump, while being additionally provided with several on the pipeline Magnetic valve, measuring cell is entered by solenoid valve control difference reagent when different;Specifically, on the pipeline being connected with measuring cell also With the branch road for each leading into sulfuric acid or hydrochloric acid reagent, molybdic acid ammonium reagent, lemon acid reagent, sulfuric acid or hydrochloric acid reagent are being passed through The valve of reagent 1 is set on branch road, the setting valve of reagent 2 on the branch road of molybdic acid ammonium reagent is being passed through, the branch road of lemon acid reagent is being passed through The upper setting valve of reagent 3;The valve of reagent 1 is opened, sulfuric acid or hydrochloric acid reagent enter measuring cell by pipeline;Open the valve of reagent 2, ammonium molybdate Reagent enters measuring cell by pipeline;The valve of reagent 3 is opened, lemon acid reagent enters measuring cell by pipeline.
The on-line monitoring method of silicate and phosphate radical in a kind of simultaneously and rapidly monitoring water of the present invention, it is included such as Lower step:
The first step, the water sample containing silicate and phosphate radical enters measurement by the pipeline that is connected with measuring cell, peristaltic pump Pond, to realize the cleaning to chemical stream;
Second step, the quantitative water sample containing silicate and phosphate radical enters measuring cell, control system control by peristaltic pump The absorbance of solution, is designated as A0 in photometric detection unit detection measuring cell processed, used as the baseline that this water sample is measured;
3rd step, opens the valve of reagent 1 on pipeline, and sulfuric acid or hydrochloric acid reagent enter measuring cell by pipeline, and stirring waits 1 Chemically react within~5 minutes;
4th step, opens the valve of reagent 2 on pipeline, and molybdic acid ammonium reagent enters measuring cell by pipeline, and stirring waits 1~5 Minute chemical reaction;The absorbance of solution, is designated as A1 in control system control photometric detection unit detection measuring cell;
5th step, opens the valve of reagent 3 on pipeline, and lemon acid reagent enters measuring cell by pipeline, and stirring waits 1~5 Minute chemical reaction;The absorbance of solution, is designated as A2 in control system control photometric detection unit detection measuring cell;
6th step, sample in measuring cell is discharged by drain valve, and measurement terminates;
Calculate:The absorbance that A1-A2 is obtained is proportional to phosphate concentration in solution;
The absorbance that A2-A0 is obtained is proportional to silicate concentration in solution.
The on-line monitoring method of silicate and phosphate radical in a kind of simultaneously and rapidly monitoring water as described above, it passes through to shift to an earlier date On-line computing model is demarcated with phosphate radical and silicate with standard liquid, phosphate radical and silicate in solution can be calculated Content.
The on-line monitoring method of silicate and phosphate radical in a kind of simultaneously and rapidly monitoring water as described above, it is in acid bar Under part, silicate and phosphate radical all with the molybdenum yellow and the yellow complex compound of phosphorus molybdenum of ammonium molybdate reaction generation yellow, by detection point Analysis obtains silicate and phosphate concentration summation, adds citric acid, and the yellow complex compound of phosphorus molybdenum will be decomposed, tested and analyzed with this The concentration of independent silicate is drawn, the concentration of silicate and phosphate radical in sample is respectively obtained successively.
Effect of the invention is that:The present invention is provided and a kind of is suitable for silicate and phosphate radical in Fast synchronization monitoring water Monitor, only needs a set of light source detection system, and a small amount of sample, single is automatically brought into operation and can just complete monitoring.The present invention is with one Monitoring system, is once chemically reacted, and phosphate radical and silicate in solution are calculated by surveying the absorbance of different step Content.Because two kinds of elements of measurement have only used a set of reaction and detection part, the purchase cost for so reducing is safeguarded into This, reduces the usage amount of reagent, reduces the probability of error;And save installing space.Simultaneously can be by program setting only Determine one of which element.Analyzed by the actual monitoring to sample, completing once monitoring flow only needs sample 30mL, at 8 points Silicate and phosphate radical result can be respectively obtained in clock.Research and application result precision is high, favorable reproducibility can reach 2% with It is interior.
Brief description of the drawings
Fig. 1 is the existing analyzer schematic diagram for monitoring silicate and phosphate radical simultaneously;
Fig. 2 is on-line computing model composition schematic diagram of the present invention;
Fig. 3 is chemical stream schematic diagram of the present invention.
Specific embodiment
Below in conjunction with the accompanying drawings with specific embodiment to silicate and phosphorus in a kind of simultaneously and rapidly monitoring water of the present invention The on-line computing model and method of acid group are further described.
Embodiment 1
As depicted in figs. 1 and 2, a kind of online prison for simultaneously and rapidly monitoring silicate and phosphate radical in water of the present invention Instrument is surveyed, it includes chemical stream, and the control system for controlling chemical stream;
Described chemical stream includes measuring cell, the pipeline being connected with measuring cell, and in the pipeline being connected with measuring cell The peristaltic pump of upper setting;Wherein, pipeline, the peristaltic pump entrance measurement of water sample and several reagent by being connected with measuring cell Pond, while being additionally provided with several magnetic valves on the pipeline, measuring cell is entered by solenoid valve control difference reagent when different.Together When, the magnetic valve for being passed through air is also set up on the pipeline being connected with measuring cell, by air stirring so that water sample and reagent are complete Full mixing;Drain valve is set on measuring cell export pipeline.
Described control system includes computer system, the input block being connected with computer system, output unit, screen Display unit, photometric detection unit and power supply;Wherein,
Input block is contact action, to the work order of the computer system chemical stream of input control;
Computer system will control the work order of chemical stream to deliver to chemical stream by output unit, while in screen Display unit display working condition;
Photometric detection unit carries out photometric detection after the work order for receiving computer system to measuring cell, while will Testing result is delivered to computer system.
Described control system is additionally provided with the relay of multichannel independence as output switch parameter, for the long-range connection upper limit, under Limit alarm lamp.When sample concentration exceedes the upper limit or the lower limit less than setting of setting in measuring cell, the actuating of relay makes contact Closure, sends alarm signal.The capacity of relay normally open contact is 1A AC 250V.
Embodiment 2
As depicted in figs. 1 and 2, a kind of online prison for simultaneously and rapidly monitoring silicate and phosphate radical in water of the present invention Instrument is surveyed, it includes chemical stream, and the control system for controlling chemical stream;
Described chemical stream includes measuring cell, the pipeline being connected with measuring cell, and in the pipeline being connected with measuring cell The peristaltic pump of upper setting.Wherein, water sample, sulfuric acid (or hydrochloric acid) reagent, molybdic acid ammonium reagent, lemon acid reagent by with measuring cell The pipeline of connection, peristaltic pump enter measuring cell;Specially:Also carried on the pipeline being connected with measuring cell and each lead into sulfuric acid or salt Acid reagent, molybdic acid ammonium reagent, the branch road of lemon acid reagent, set the valve of reagent 1 on the branch road for being passed through sulfuric acid or hydrochloric acid reagent, The setting valve of reagent 2 on the branch road of molybdic acid ammonium reagent is passed through, the setting valve of reagent 3 on the branch road of lemon acid reagent is being passed through;Open examination The valve of agent 1, sulfuric acid or hydrochloric acid reagent enter measuring cell by pipeline;The valve of reagent 2 is opened, molybdic acid ammonium reagent enters measurement by pipeline Pond;The valve of reagent 3 is opened, lemon acid reagent enters measuring cell by pipeline.
Meanwhile, the magnetic valve for being passed through air is also set up on the pipeline being connected with measuring cell, by air stirring so that water Sample and reagent are thoroughly mixed;Drain valve is set on measuring cell export pipeline.
Described control system includes computer system, the input block being connected with computer system, output unit, screen Display unit, photometric detection unit and power supply;Wherein,
Input block is contact action, to the work order of the computer system chemical stream of input control;
Computer system will control the work order of chemical stream to deliver to chemical stream by output unit, while in screen Display unit display working condition;
Photometric detection unit carries out photometric detection after the work order for receiving computer system to measuring cell, while will Testing result is delivered to computer system.
Described control system is additionally provided with the relay of multichannel independence as output switch parameter, for the long-range connection upper limit, under Limit alarm lamp.When sample concentration exceedes the upper limit or the lower limit less than setting of setting in measuring cell, the actuating of relay makes contact Closure, sends alarm signal.The capacity of relay normally open contact is 1A AC 250V.
The on-line monitoring method of silicate and phosphate radical in water is simultaneously and rapidly monitored using above-mentioned on-line computing model, it includes Following steps:
The first step, the water sample containing silicate and phosphate radical enters measuring cell by pipeline, peristaltic pump, to realize to chemistry The cleaning of stream;
Second step, quantitative water sample enters measuring cell by peristaltic pump, and control system control photometric detection unit detection is surveyed The absorbance of solution, is designated as A0 in amount pond, used as the baseline that this water sample is measured;
3rd step, opens the valve of reagent 1 on pipeline, and the sulfuric acid of reagent one (or hydrochloric acid) enters measuring cell by pipeline, stirs Wait chemically react within 1~5 minute;
4th step, opens the valve of reagent 2 on pipeline, and reagent ammonium dimolybdate enters measuring cell by pipeline, and stirring waits 1~ Chemically react within 5 minutes;The absorbance of solution, is designated as A1 in control system control photometric detection unit detection measuring cell;
5th step, opens the valve of reagent 3 on pipeline, and the citric acid of reagent three enters measuring cell by pipeline, and stirring waits 1~ Chemically react within 5 minutes;The absorbance of solution, is designated as A2 in control system control photometric detection unit detection measuring cell;
6th step, sample in measuring cell is discharged by drain valve, and measurement terminates.
Calculate:The absorbance that A1-A2 is obtained is proportional to phosphate concentration in solution;
The absorbance that A2-A0 is obtained is proportional to silicate concentration in solution.
By being demarcated with phosphate radical and silicate to on-line computing model with standard liquid in advance, solution can be calculated The content of middle phosphate radical and silicate.
Embodiment 3
It is synchronous using the on-line computing model of silicate and phosphate radical in a kind of simultaneously and rapidly monitoring water described in embodiment 2 The on-line monitoring method of silicate and phosphate radical in fast monitored water, it comprises the following steps:
The first step, the water sample containing silicate and phosphate radical enters measuring cell by pipeline, peristaltic pump, to realize to chemistry The cleaning of stream;
Second step, quantitative water sample enters measuring cell by peristaltic pump, and control system control photometric detection unit detection is surveyed The absorbance of solution, is designated as A0=0.005 in amount pond, used as the baseline that this water sample is measured;
3rd step, opens the valve of reagent 1 on pipeline, and the sulfuric acid of reagent one (or hydrochloric acid) enters measuring cell by pipeline, stirs Wait chemically react within 1~5 minute;
4th step, opens the valve of reagent 2 on pipeline, and reagent ammonium dimolybdate enters measuring cell by pipeline, and stirring waits 1~ Chemically react within 5 minutes;The absorbance of solution, is designated as A1=0.142 in control system control photometric detection unit detection measuring cell;
5th step, opens the valve of reagent 3 on pipeline, and the citric acid of reagent three enters measuring cell by pipeline, and stirring waits 1~ Chemically react within 5 minutes;The absorbance of solution, is designated as A2=0.089 in control system control photometric detection unit detection measuring cell;
6th step, sample in measuring cell is discharged by drain valve, and measurement terminates.
A1-A0 is absorbance when silicate and phosphate radical develop the color together
A2-A0 is absorbance when only silicate develops the color
(A1-A0) absorbance that-(A2-A0)=A1-A2=0.053 is obtained is proportional to phosphate concentration in solution;
The absorbance that A2-A0=0.084 is obtained is proportional to silicate concentration in solution.
A0 is equivalent to be water sample color in itself, it is believed that be reference;
A1 is that silicate and phosphate radical show together after adding the sulfuric acid of reagent one (hydrochloric acid or other acid) and reagent ammonium dimolybdate The value of color;
A2 is to add reagent three (citric acid) (phosphate radical can fade with the color of ammonium molybdate reaction after adding citric acid) phosphorus Absorbance after only remaining silicate develops the color after acid group colour fading.
The on-line monitoring method of silicate and phosphate radical in simultaneously and rapidly monitoring water of the invention, its principle is in acid bar Under part, silicate and phosphate radical all with the molybdenum yellow and the yellow complex compound of phosphorus molybdenum of ammonium molybdate reaction generation yellow, by detection point Analysis obtains silicate and phosphate concentration summation, adds citric acid, and the yellow complex compound of phosphorus molybdenum will be decomposed, tested and analyzed with this The concentration of independent silicate is drawn, the concentration of silicate and phosphate radical in sample is respectively obtained successively.Therefore it is different by detecting The color of solution calculates the concentration of silicate and phosphate radical during step.

Claims (7)

1. it is a kind of simultaneously and rapidly monitoring water in silicate and phosphate radical on-line computing model, it is characterised in that:The on-line computing model Including chemical stream, and the control system for controlling chemical stream;
Described chemical stream includes measuring cell, the pipeline being connected with measuring cell, and the peristaltic pump set on pipeline;Its In, water sample and several reagent enter measuring cell by the pipeline that is connected with measuring cell, peristaltic pump, while also being set on the pipeline There are several magnetic valves, measuring cell is entered when different by solenoid valve control difference reagent;
Described control system includes computer system, the input block being connected with computer system, output unit, screen display Unit, photometric detection unit and power supply;Wherein,
Input block is contact action, to the work order of the computer system chemical stream of input control;
Computer system will control the work order of chemical stream to deliver to chemical stream by output unit, while in screen display Unit display working condition;
Photometric detection unit carries out photometric detection after the work order for receiving computer system to measuring cell, while will detection Result is delivered to computer system.
2. in a kind of simultaneously and rapidly monitoring water according to claim 1 silicate and phosphate radical on-line computing model, it is special Levy and be:The magnetic valve for being passed through air is set on the pipeline being connected with measuring cell, by air stirring so that water sample and reagent It is thoroughly mixed;Drain valve is set on measuring cell export pipeline.
3. in a kind of simultaneously and rapidly monitoring water according to claim 1 silicate and phosphate radical on-line computing model, it is special Levy and be:Described control system is provided with the relay of multichannel independence as output switch parameter, for the long-range connection upper limit, lower limit report Warning lamp;When sample concentration exceedes the upper limit or the lower limit less than setting of setting in measuring cell, the actuating of relay closes contact Close, send alarm signal.
4. in a kind of simultaneously and rapidly monitoring water according to claim 1 silicate and phosphate radical on-line computing model, it is special Levy and be:Described water sample and several reagent enter measuring cell by the pipeline that is connected with measuring cell, peristaltic pump, while should Several magnetic valves are additionally provided with pipeline, measuring cell is entered when different by solenoid valve control difference reagent;Specifically,
Also with each leading into sulfuric acid or hydrochloric acid reagent, molybdic acid ammonium reagent, lemon acid reagent on the pipeline being connected with measuring cell Branch road, sets the valve of reagent 1 on the branch road for being passed through sulfuric acid or hydrochloric acid reagent, and reagent is set being passed through on the branch road of molybdic acid ammonium reagent 2 valves, are being passed through the setting valve of reagent 3 on the branch road of lemon acid reagent;The valve of reagent 1 is opened, sulfuric acid or hydrochloric acid reagent are entered by pipeline Enter measuring cell;The valve of reagent 2 is opened, molybdic acid ammonium reagent enters measuring cell by pipeline;The valve of reagent 3 is opened, lemon acid reagent passes through Pipeline enters measuring cell.
5. silicate and phosphate radical in the simultaneously and rapidly monitoring water of any on-line computing model described in a kind of use Claims 1-4 On-line monitoring method, it is characterised in that:The method comprises the following steps:
The first step, the water sample containing silicate and phosphate radical enters measuring cell by the pipeline that is connected with measuring cell, peristaltic pump, with Realize the cleaning to chemical stream;
Second step, the quantitative water sample containing silicate and phosphate radical enters measuring cell, control system control light by peristaltic pump The absorbance of solution, is designated as A0, as the baseline that this water sample is measured in degree detection unit detection measuring cell;
3rd step, opens the valve of reagent 1 on pipeline, and sulfuric acid or hydrochloric acid reagent enter measuring cell by pipeline, and stirring waits 1~5 Minute chemical reaction;
4th step, opens the valve of reagent 2 on pipeline, and molybdic acid ammonium reagent enters measuring cell by pipeline, and stirring is waited 1~5 minute Chemical reaction;The absorbance of solution, is designated as A1 in control system control photometric detection unit detection measuring cell;
5th step, opens the valve of reagent 3 on pipeline, and lemon acid reagent enters measuring cell by pipeline, and stirring is waited 1~5 minute Chemical reaction;The absorbance of solution, is designated as A2 in control system control photometric detection unit detection measuring cell;
6th step, sample in measuring cell is discharged by drain valve, and measurement terminates;
Calculate:The absorbance that A1-A2 is obtained is proportional to phosphate concentration in solution;
The absorbance that A2-A0 is obtained is proportional to silicate concentration in solution.
6. it is according to claim 5 it is a kind of simultaneously and rapidly monitoring water in silicate and phosphate radical on-line monitoring method, its It is characterised by:By being demarcated with phosphate radical and silicate to on-line computing model with standard liquid in advance, can calculate molten The content of phosphate radical and silicate in liquid.
7. it is according to claim 5 it is a kind of simultaneously and rapidly monitoring water in silicate and phosphate radical on-line monitoring method, its It is characterised by:In acid condition, silicate and phosphate radical all generate molybdenum yellow and phosphorus the molybdenum Huang of yellow with ammonium molybdate reaction Complex compound, silicate and phosphate concentration summation are obtained by detection and analysis, add citric acid, and the yellow complex compound of phosphorus molybdenum will Decompose, the concentration for drawing independent silicate is tested and analyzed with this, the concentration of silicate and phosphate radical in sample is respectively obtained successively.
CN201611246753.6A 2016-12-29 2016-12-29 Simultaneously and rapidly monitor the on-line computing model and method of silicate and phosphate radical in water Pending CN106841182A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201611246753.6A CN106841182A (en) 2016-12-29 2016-12-29 Simultaneously and rapidly monitor the on-line computing model and method of silicate and phosphate radical in water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201611246753.6A CN106841182A (en) 2016-12-29 2016-12-29 Simultaneously and rapidly monitor the on-line computing model and method of silicate and phosphate radical in water

Publications (1)

Publication Number Publication Date
CN106841182A true CN106841182A (en) 2017-06-13

Family

ID=59114553

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201611246753.6A Pending CN106841182A (en) 2016-12-29 2016-12-29 Simultaneously and rapidly monitor the on-line computing model and method of silicate and phosphate radical in water

Country Status (1)

Country Link
CN (1) CN106841182A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110095433A (en) * 2019-06-17 2019-08-06 广西师范大学 A method of silicate is measured with Resonance Rayleigh Scattering Spectra
CN110514610A (en) * 2019-09-30 2019-11-29 南京润驰工程技术有限公司 A kind of silicate measurement device and measurement method
US11480526B2 (en) * 2020-01-21 2022-10-25 Mettler-Toledo Thornton, Inc. Instrument for sequential analysis for silica and phosphate in aqueous solution

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1116303A (en) * 1994-08-31 1996-02-07 陈义新 Automatic measurer for content of silicic acid group
CN2486967Y (en) * 2000-09-30 2002-04-17 边东福 Water sample analyser for monitoring silicon phosphate radical
CN102226755A (en) * 2011-04-15 2011-10-26 河海大学常州校区 On-line analyzer for monitoring silicate concentration or phosphate concentration in water
CN102262068A (en) * 2011-04-28 2011-11-30 河海大学常州校区 Wireless network-based intelligent on-line analysis recorder for concentration of phosphate radical

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1116303A (en) * 1994-08-31 1996-02-07 陈义新 Automatic measurer for content of silicic acid group
CN2486967Y (en) * 2000-09-30 2002-04-17 边东福 Water sample analyser for monitoring silicon phosphate radical
CN102226755A (en) * 2011-04-15 2011-10-26 河海大学常州校区 On-line analyzer for monitoring silicate concentration or phosphate concentration in water
CN102262068A (en) * 2011-04-28 2011-11-30 河海大学常州校区 Wireless network-based intelligent on-line analysis recorder for concentration of phosphate radical

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110095433A (en) * 2019-06-17 2019-08-06 广西师范大学 A method of silicate is measured with Resonance Rayleigh Scattering Spectra
CN110514610A (en) * 2019-09-30 2019-11-29 南京润驰工程技术有限公司 A kind of silicate measurement device and measurement method
US11480526B2 (en) * 2020-01-21 2022-10-25 Mettler-Toledo Thornton, Inc. Instrument for sequential analysis for silica and phosphate in aqueous solution

Similar Documents

Publication Publication Date Title
US4224033A (en) Programmable, continuous flow analyzer
US4314824A (en) Programmable, continuous flow analyzer
CN101793902A (en) Device for fluidly injecting and rapidly analyzing residual chlorine of water quality and analysis method thereof
CN104849422A (en) Ammonia nitrogen on-line monitoring system and method thereof
CN103439258B (en) A kind of water nutrition in situ detection instrument based on integrated valve terminal device and detection method
CN107367475A (en) Water sample total cyanogen analytical equipment and analysis method
CN106841182A (en) Simultaneously and rapidly monitor the on-line computing model and method of silicate and phosphate radical in water
CN111323531A (en) Titration device and titration method for combining speed and speed in automatic titration process
CN100478678C (en) Method for analyzing phosphate in sea water and estuary water
CN209247625U (en) A kind of micro-fluidic NH 3 flow path system
CN208366698U (en) A kind of sample dilution device for core sampling system
KR101581230B1 (en) Total nitrogen and total phosphorus measuring device
CN205080143U (en) Automatic quick detecting system of trace iron ion in power plant's steam
CN106645501A (en) Continuous automatic sampling and analyzing method and continuous automatic sampling and analyzing device for measuring atmospheric carbonate
CN103399163B (en) Online phosphorus and fluorine content measuring analyzer
CN110006893B (en) Online automatic determination method for zirconium silane concentration
CN103399164A (en) System for rapidly measuring sulfate radical concentration on line
Mozzhukhin et al. Stepwise injection analysis as a new method of flow analysis
CN214528145U (en) On-line analysis equipment for alkalinity of working solution in preparation of hydrogen peroxide by anthraquinone process
US7306765B2 (en) Apparatus and method for chemical analysis
CN204989129U (en) Online electrometric titration system of totally -enclosed formula
CN208537538U (en) A kind of micro-fluidic chip
EP3635369B1 (en) Colorimetric analyzer with improved error detection
van Staden Solving the problems of sequential injection systems as process analyzers
Taylor et al. Co-determination of sodium metabisulfite and starch in corn syrup by flow injection coulometry

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20170613