CN104677900B - A kind of method of chlorine dioxide content in quick detection water for eliminating reagent blank influence - Google Patents

A kind of method of chlorine dioxide content in quick detection water for eliminating reagent blank influence Download PDF

Info

Publication number
CN104677900B
CN104677900B CN201510090771.9A CN201510090771A CN104677900B CN 104677900 B CN104677900 B CN 104677900B CN 201510090771 A CN201510090771 A CN 201510090771A CN 104677900 B CN104677900 B CN 104677900B
Authority
CN
China
Prior art keywords
chlorine dioxide
water
color
blank
reagent
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.)
Active
Application number
CN201510090771.9A
Other languages
Chinese (zh)
Other versions
CN104677900A (en
Inventor
林林
连国军
黄陈平
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.)
Wenzhou Medical University
Original Assignee
Wenzhou Medical University
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 Wenzhou Medical University filed Critical Wenzhou Medical University
Priority to CN201510090771.9A priority Critical patent/CN104677900B/en
Publication of CN104677900A publication Critical patent/CN104677900A/en
Application granted granted Critical
Publication of CN104677900B publication Critical patent/CN104677900B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Investigating Or Analyzing Non-Biological Materials By The Use Of Chemical Means (AREA)

Abstract

The invention discloses a kind of method of chlorine dioxide content in quick detection water for eliminating reagent blank influence, this method prepares liquid-type chlorine dioxide detection reagent first, the chlorine dioxide standard color card for deducting reagent blank is made of water white transparency PVC plastic flitch again, chlorine dioxide standard color card is placed in blank bottom of the tube during test, the chlorine dioxide concentration corresponding to standard color card during with sample cell solid colour is read, chlorine dioxide concentration in water sample is obtained.Chlorine dioxide concentration detection is carried out by the method, influence of the reagent blank to testing result can be eliminated, be particularly suitable for chlorine dioxide field quick detection in water.

Description

Chlorine dioxide content in a kind of quick detection water for eliminating reagent blank influence Method
Technical field
The present invention relates to the present invention relates to field of water quality detection, more particularly to a kind of eliminate the quick of reagent blank influence The method for detecting chlorine dioxide content in water.
Background technology
Chlorine dioxide(ClO2)Be at present in the world generally acknowledged the efficient of latest generation, wide spectrum, safety it is sterilized, fresh-keeping Agent, is the optimal substitute of chlorinated product, has been widely used in World Developed Countries.Use the life of chlorine dioxide treatment Drinking water living will not produce generally the teratogenesis being also easy to produce during with chlorine-containing disinfectants such as sodium hypochlorite, mutagens, carcinogenic chloroform, But skin is contacted or solution of the intake containing high concentration of chlorine dioxide, may still cause intense stimulus and corrosiveness.
In water more than the detection of chlorine dioxide using directly develop the color AAS, Fading spectrophotometry, fluorimetry, Chemical titration, chromatography, electrochemical method, plasma resonance scattering method, these methods are both needed to take back water sample special Laboratory, is chemically examined by the operating technology personnel of specialty and completed, most of method also needs to the high large-scale instrumentation of price, no Quick, easy Site Detection requirement can be met, some special when and wheres also exist sampling not in time, can not be objective anti- Reflect the situation of sampling location Water quality.
Existing chlorine dioxide Site Detection reagent is the dry-type detection reagent based on colorimetric method in the market, The detection reagent takes a certain amount of water sample mix, dissolve with dry-type detection reagent when measuring, react a period of time after Specific color is produced, the concentration for drawing water sample test substance is directly compareed with standard color card.Such method is quick, conveniently, it is public Many participations are high, but can not eliminate influence of the change to measurement result of reagent blank during measurement, only constant in reagent blank Just there is higher accuracy when constant.But, actually detected to find, the either detection reagent of liquid-type or dry-type, All inevitably there is a situation where that reagent blank becomes larger or diminished in storing process.In addition, using the inspection of dry-type Test agent when carrying out water sample detection, it is necessary to first detection reagent is fully dissolved with water sample to be measured, then with the specific pollution in water sample Thing carries out reaction and produces particular color.Because the TWS that Various Seasonal, different zones are gathered is not quite similar, dry-type is dissolved Also it is not quite similar the time required to during detection reagent, effectively control is difficult to the time required to whole detection process, also to testing result Accuracy is adversely affected.
Therefore, demand one kind uses liquid-type detection reagent, can eliminate reagent blank on testing result influence, using standard The detection method of chlorine dioxide in the quantitative water of the direct visual colorimetric determination of colour atla, for realizing chlorine dioxide field quick detection in water It is particularly important.
The content of the invention
It is an object of the invention to:In view of the shortcomings of the prior art, reagent blank shadow can be eliminated the invention provides one kind The method of chlorine dioxide content in loud quick detection water.
For achieving the above object, the present invention uses following scheme:A kind of quick inspection for eliminating reagent blank influence The method for surveying chlorine dioxide content in water, it is characterised in that methods described comprises the following steps:
(1)The preparation of liquid-type chlorine dioxide detection reagent, the liquid-type chlorine dioxide detection reagent presses the amount of material Following components and deionized water are configured to solution by concentration,
(N, N- diethyl -1,4- phenylenediamines)Sulfate 0.19-0.38 mmol/L
Glycine 0.267-0.675 mol/L
Disodium ethylene diamine tetraacetate 2.69-5.38 mmol/L
Ethylene glycol 0.36-0.90 mol/L
PH6.50 phosphate buffer 30-80 mmol/L;
(2)The preparation of the chlorine dioxide standard color card after reagent blank is deducted, at least 4 colorimetric cylinders, optional 1 colorimetric are taken Manage as blank tube, remaining colorimetric cylinder is first to add in standard pipe, blank tube first to add concentration in deionized water, each standard pipe in ladder The chlorine dioxide standard spent the deionized water added in the chlorine dioxide standard liquid of change, blank tube and added in standard pipe is molten Liquid product is identical, the step of adding same volume in all colorimetric cylinders(1)Obtained liquid-type chlorine dioxide detection reagent, reaction No longer change to color, it is in color to be shot by colorimetric cylinder bottom up in each colorimetric cylinder, with mapping software by each standard pipe face Color deducts blank tube color, then the concentration of the color of gained and corresponding chlorine dioxide standard liquid is printed upon into water white transparency plate On;
(3)The detection of water sample to be measured, while taking at least 2 colorimetric cylinders, optional 1 colorimetric cylinder is blank tube, remaining colorimetric Manage as sample cell, the deionization for first adding and being added in water sample to be measured, blank tube in deionized water, sample cell is first added in blank tube Water is identical with the volume of water sample to be measured added in sample cell, the step of adding same volume in all colorimetric cylinders(1)Obtained liquid Build chlorine dioxide detection reagent, reaction no longer changes to color, then by step(2)Made standard color card is placed in blank tube The overlay color of bottom, observation blank tube and chlorine dioxide standard color card, reads and sample cell color most close overlay color Corresponding chlorine dioxide concentration.
It is used as the preferred scheme of the present invention, step(1)In liquid-type chlorine dioxide detection reagent press substance withdrawl syndrome Following components and deionized water are configured to solution,
(N, N- diethyl -1,4- phenylenediamines)Sulfate 0.26-0.31 mmol/L
Glycine 0.37-0.57 mol/L
Disodium ethylene diamine tetraacetate 3.74-4.34 mmol/L
Ethylene glycol 0.53-0.73 mol/L
PH6.50 phosphate buffer 40-65 mmol/L.
It is used as present invention further optimization, step(1)In liquid-type chlorine dioxide detection reagent by material amount it is dense Following components and deionized water are configured to solution by degree,
(N, N- diethyl -1,4- phenylenediamines)The mmol/L of sulfate 0.28
The mol/L of glycine 0.471
The mmol/L of disodium ethylene diamine tetraacetate 4.04
The mol/L of ethylene glycol 0.63
The mmol/L of pH6.50 phosphate buffers 50.
It is used as the preferred scheme of the present invention, step(2)In take 7 colorimetric cylinders, an optional colorimetric cylinder is blank tube, remaining Sequentially added in the six roots of sensation colorimetric cylinder concentration for 0.05mg/L, 0.10mg/L, 0.20mg/L, 0.30mg/L, 0.50mg/L, 0.80mg/L chlorine dioxide standard liquid.
As the preferred scheme of the present invention, water white transparency plate is the water white transparency PVC plastic flitch that thickness is 1-2mm.
The positive effect of the present invention is as follows:
The method of chlorine dioxide content has method letter in the quick detection water for eliminating reagent blank influence of the present invention High, the easily operated advantage of single, accuracy;Detected, can effectively be controlled whole using liquid-type chlorine dioxide detection reagent The time required to detection process;By the side that blank tube color addition is carried out to colorimetric control with sample cell again on standard color card Method, can effectively eliminate influence of the reagent blank to testing result, be particularly suitable for chlorine dioxide field quick detection in water.
Embodiment
Embodiment 1
(1)The preparation of liquid-type chlorine dioxide detection reagent, the liquid-type chlorine dioxide detection reagent presses the amount of material Following components and deionized water are configured to solution by concentration,
(N, N- diethyl -1,4- phenylenediamines)The mmol/L of sulfate 0.19
The mol/L of glycine 0.267
The mmol/L of disodium ethylene diamine tetraacetate 2.69
The mol/L of ethylene glycol 0.36
The mmol/L of pH6.50 phosphate buffers 30;
(2)The preparation of the chlorine dioxide standard color card after reagent blank is deducted, 7 10ml glass colorimetric cylinders are taken, the 1st is set Root colorimetric cylinder is that blank tube, 2-7 root colorimetric cylinders are standard pipe, adds 10ml deionized waters in blank tube and standard pipe respectively With the chlorine dioxide mark that 10ml concentration is 0.05mg/L, 0.10mg/L, 0.20mg/L, 0.30mg/L, 0.50mg/L, 0.80mg/L Quasi- solution, adds step(1)Described liquid-type chlorine dioxide detection reagent 0.2ml, reacts to color and no longer becomes at room temperature Change, as the color produced by colorimetric cylinder bottom up shoots each tube reaction, with mapping software photoshop7.0 by each standard pipe Color is deducted after blank tube color, and the concentration of the color of gained and corresponding chlorine dioxide standard liquid is printed upon into thickness is On 1mm water white transparency PVC plastic flitch;
(3)Take 2 10ml glass colorimetric cylinders, it is that blank tube, the 2nd colorimetric cylinder are sample cell to set the 1st colorimetric cylinder, point 10ml deionized waters and 10ml water samples to be measured are not added in blank tube and sample cell, step is added(1)Described in liquid Type chlorine dioxide detection reagent, reacts to color and no longer changes at room temperature, by step(2)Described standard color card is placed in this step In blank bottom of the tube, by blank tube bottom up observe blank tube be superimposed with standard color card after color, and with sample cell face Color is compareed, when both solid colours, is read and the chlorine dioxide concentration corresponding to sample cell color most close overlay color.
Embodiment 2
(1)The preparation of liquid-type chlorine dioxide detection reagent, the liquid-type chlorine dioxide detection reagent presses the amount of material Following components and deionized water are configured to solution by concentration,
(N, N- diethyl -1,4- phenylenediamines)The mmol/L of sulfate 0.28
The mol/L of glycine 0.471
The mmol/L of disodium ethylene diamine tetraacetate 4.04
The mol/L of ethylene glycol 0.63
The mmol/L of pH6.50 phosphate buffers 50;
(2)The preparation of the chlorine dioxide standard color card after reagent blank is deducted, 7 10ml glass colorimetric cylinders are taken, the 1st is set Root colorimetric cylinder is that blank tube, 2-7 root colorimetric cylinders are standard pipe, adds 10ml deionized waters in blank tube and standard pipe respectively With the chlorine dioxide mark that 10ml concentration is 0.05mg/L, 0.10mg/L, 0.20mg/L, 0.30mg/L, 0.50mg/L, 0.80mg/L Quasi- solution, adds step(1)Described liquid-type chlorine dioxide detection reagent 0.2ml, reacts to color and no longer becomes at room temperature Change, as the color produced by colorimetric cylinder bottom up shoots each tube reaction, with mapping software photoshop7.0 by each standard pipe Color is deducted after blank tube color, and the concentration of the color of gained and corresponding chlorine dioxide standard liquid is printed upon into thickness is On 1mm water white transparency PVC plastic flitch;
(3)Take 2 10ml glass colorimetric cylinders, it is that blank tube, the 2nd colorimetric cylinder are sample cell to set the 1st colorimetric cylinder, point 10ml deionized waters and 10ml water samples to be measured are not added in blank tube and sample cell, step is added(1)Described in liquid Type chlorine dioxide detection reagent, reacts to color and no longer changes at room temperature, by step(2)Described standard color card is placed in this step In blank bottom of the tube, by blank tube bottom up observe blank tube be superimposed with standard color card after color, and with sample cell face Color is compareed, when both solid colours, is read and the chlorine dioxide concentration corresponding to sample cell color most close overlay color.
Embodiment 3
(1)The preparation of liquid-type chlorine dioxide detection reagent, the liquid-type chlorine dioxide detection reagent presses the amount of material Following components and deionized water are configured to solution by concentration,
(N, N- diethyl -1,4- phenylenediamines)The mmol/L of sulfate 0.38
The mol/L of glycine 0.675
The mmol/L of disodium ethylene diamine tetraacetate 4.04
The mol/L of ethylene glycol 0.90
The mmol/L of pH6.50 phosphate buffers 80;
(2)The preparation of the chlorine dioxide standard color card after reagent blank is deducted, 7 10ml glass colorimetric cylinders are taken, the 1st is set Root colorimetric cylinder is that blank tube, 2-7 root colorimetric cylinders are standard pipe, adds 10ml deionized waters in blank tube and standard pipe respectively With the chlorine dioxide mark that 10ml concentration is 0.05mg/L, 0.10mg/L, 0.20mg/L, 0.30mg/L, 0.50mg/L, 0.80mg/L Quasi- solution, adds step(1)React to color and no longer become under described liquid-type chlorine dioxide detection reagent 0.2ml, normal temperature Change, as the color produced by colorimetric cylinder bottom up shoots each tube reaction, with mapping software photoshop7.0 by each standard pipe Color is deducted after blank tube color, and the concentration of the color of gained and corresponding chlorine dioxide standard liquid is printed upon into thickness is On 1mm water white transparency PVC plastic flitch;
(3)Take 2 10ml glass colorimetric cylinders, it is that blank tube, the 2nd colorimetric cylinder are sample cell to set the 1st colorimetric cylinder, point 10ml deionized waters and 10ml water samples to be measured are not added in blank tube and sample cell, step is added(1)Described in liquid React to color and no longer change under type chlorine dioxide detection reagent, normal temperature, by step(2)Described standard color card is placed in this step In blank bottom of the tube, by blank tube bottom up observe blank tube be superimposed with standard color card after color, and with sample cell face Color is compareed, when both solid colours, is read and the chlorine dioxide concentration corresponding to sample cell color most close overlay color.
Embodiment 4
In order to which the effect further to the present invention is verified, the change of reagent blank is investigated to measurement result accuracy Influence, the present invention has done following contrast test:By the step of this law embodiment 1(1)Described method prepares liquid-type chlorine dioxide Detection reagent is test group, not deduct reagent blank, the detection reagent of standard color card direct color comparison be used as control group, by two Group reagent puts 4 DEG C of refrigerators respectively and 37 water-baths are stored 7 days, and to a dense with national standard method measure chlorine dioxide Spend and be measured for 0.05mg/L water sample, while replacing water sample to carry out reagent blank test with deionized water, with 721 light splitting light Degree meter record reagent blank value, the results are shown in Table 2.
Table 2
From table 2 it can be seen that under identical experiment condition, with the gradually increase of reagent blank, the measure of test group As a result keep constant, but the measurement result of control group substantially becomes big, shows that method of the present invention can effectively remove reagent empty Influence of the white change to chlorine dioxide test result.
The present invention is not limited to above-mentioned embodiment, and persons skilled in the art are according to disclosed by the invention interior Hold, the present invention, or every thinking using the present invention implemented using other a variety of embodiments, do simple change or Change, both fall within protection scope of the present invention.

Claims (6)

1. a kind of method of chlorine dioxide content in quick detection water for eliminating reagent blank influence, it is characterised in that the side Method comprises the following steps:
(1)The preparation of liquid-type chlorine dioxide detection reagent, the liquid-type chlorine dioxide detection reagent presses substance withdrawl syndrome Following components and deionized water are configured to solution,
(N, N- diethyl -1,4- phenylenediamines)Sulfate 0.19-0.38 mmol/L
Glycine 0.267-0.675 mol/L
Disodium ethylene diamine tetraacetate 2.69-5.38 mmol/L
Ethylene glycol 0.36-0.90 mol/L
PH6.50 phosphate buffer 30-80 mmol/L;
(2)The preparation of the chlorine dioxide standard color card after reagent blank is deducted, at least 4 colorimetric cylinders are taken, optional 1 colorimetric cylinder is Blank tube, remaining colorimetric cylinder is standard pipe, under the conditions of 5-40 DEG C, is first added in blank tube in deionized water, each standard pipe first Add the deionized water added in the chlorine dioxide standard liquid of concentration in gradient change, blank tube and added in standard pipe two Chlorine monoxid standard liquid volume is identical, the step of adding same volume in all colorimetric cylinders(1)Obtained liquid-type chlorine dioxide Detection reagent, reaction no longer changes to color, and it is in color to be shot by colorimetric cylinder bottom up in each colorimetric cylinder, uses mapping software Each standard pipe color is deducted into blank tube color, then the color of gained and the concentration of corresponding chlorine dioxide standard liquid are printed On water white transparency plate;
(3)The detection of water sample to be measured, while taking at least 2 colorimetric cylinders, optional 1 colorimetric cylinder is blank tube, and remaining colorimetric cylinder is Sample cell, under the conditions of 5-40 DEG C, first adds in deionized water, sample cell in blank tube and first adds in water sample to be measured, blank tube The deionized water of addition is identical with the volume of water sample to be measured added in sample cell, the step of adding same volume in all colorimetric cylinders (1)Obtained liquid-type chlorine dioxide detection reagent, reaction no longer changes to color, then by step(2)Made reference colour The overlay color of blank bottom of the tube, observation blank tube and chlorine dioxide standard color card is placed in, is read and sample cell color most phase Chlorine dioxide concentration corresponding near overlay color.
2. the side of chlorine dioxide content in a kind of quick detection water for eliminating reagent blank influence according to claim 1 Method, it is characterised in that:Step(1)In liquid-type chlorine dioxide detection reagent by substance withdrawl syndrome by following components and go from Sub- water is configured to solution,
(N, N- diethyl -1,4- phenylenediamines)Sulfate 0.26-0.31 mmol/L
Glycine 0.37-0.57 mol/L
Disodium ethylene diamine tetraacetate 3.74-4.34 mmol/L
Ethylene glycol 0.53-0.73 mol/L
PH6.50 phosphate buffer 40-65 mmol/L.
3. the side of chlorine dioxide content in a kind of quick detection water for eliminating reagent blank influence according to claim 1 Method, it is characterised in that:Step(1)In liquid-type chlorine dioxide detection reagent by substance withdrawl syndrome by following components and go from Sub- water is configured to solution,
(N, N- diethyl -1,4- phenylenediamines)The mmol/L of sulfate 0.28
The mol/L of glycine 0.471
The mmol/L of disodium ethylene diamine tetraacetate 4.04
The mol/L of ethylene glycol 0.63
The mmol/L of pH6.50 phosphate buffers 50.
4. chlorine dioxide contains in a kind of quick detection water for eliminating reagent blank influence according to claim 1 or 2 or 3 The method of amount, it is characterised in that:Step(2)In take 7 colorimetric cylinders, an optional colorimetric cylinder is blank tube, remaining six roots of sensation colorimetric The dioxy that concentration is 0.05mg/L, 0.10mg/L, 0.20mg/L, 0.30mg/L, 0.50mg/L, 0.80mg/L is sequentially added in pipe Change chlorine standard liquid.
5. chlorine dioxide contains in a kind of quick detection water for eliminating reagent blank influence according to claim 1 or 2 or 3 The method of amount, it is characterised in that:Water white transparency plate is the water white transparency PVC plastic flitch that thickness is 1-2mm.
6. the side of chlorine dioxide content in a kind of quick detection water for eliminating reagent blank influence according to claim 4 Method, it is characterised in that:Water white transparency plate is the water white transparency PVC plastic flitch that thickness is 1-2mm.
CN201510090771.9A 2015-02-28 2015-02-28 A kind of method of chlorine dioxide content in quick detection water for eliminating reagent blank influence Active CN104677900B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510090771.9A CN104677900B (en) 2015-02-28 2015-02-28 A kind of method of chlorine dioxide content in quick detection water for eliminating reagent blank influence

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510090771.9A CN104677900B (en) 2015-02-28 2015-02-28 A kind of method of chlorine dioxide content in quick detection water for eliminating reagent blank influence

Publications (2)

Publication Number Publication Date
CN104677900A CN104677900A (en) 2015-06-03
CN104677900B true CN104677900B (en) 2017-07-11

Family

ID=53313248

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510090771.9A Active CN104677900B (en) 2015-02-28 2015-02-28 A kind of method of chlorine dioxide content in quick detection water for eliminating reagent blank influence

Country Status (1)

Country Link
CN (1) CN104677900B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109406425A (en) * 2018-11-13 2019-03-01 上海仪电科学仪器股份有限公司 For detecting detection agent of chlorine dioxide and preparation method thereof and detection method in water
CN111504992A (en) * 2020-05-06 2020-08-07 中国检验检疫科学研究院 Rapid detection kit for chlorine dioxide after ballast water disinfection
CN114002212B (en) * 2021-12-24 2022-04-26 广东环凯生物技术有限公司 Chlorine dioxide detection reagent, kit and rapid detection method

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN2482081Y (en) * 2001-03-23 2002-03-13 广东省微生物研究所 Total chlorine, residual chlorine and ozone quick measuring reagent box for water
CN1796985A (en) * 2004-12-21 2006-07-05 上海三爱思试剂有限公司 Test paper for detecting disinfector of chlorine dioxide, and preparation method
CN101231245A (en) * 2008-02-26 2008-07-30 内蒙古蒙牛乳业(集团)股份有限公司 Method and kit for quick qualitative testing chlorine dioxide in milk
CN101241080A (en) * 2008-01-25 2008-08-13 黄晓平 Convenient colorimetric technique for detecting subaqueous polymorphic chlorine and its color comparator
CN103207158A (en) * 2013-04-17 2013-07-17 上海绿帝环保科技有限公司 Water quality detecting agent for residual chlorine

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN2482081Y (en) * 2001-03-23 2002-03-13 广东省微生物研究所 Total chlorine, residual chlorine and ozone quick measuring reagent box for water
CN1796985A (en) * 2004-12-21 2006-07-05 上海三爱思试剂有限公司 Test paper for detecting disinfector of chlorine dioxide, and preparation method
CN101241080A (en) * 2008-01-25 2008-08-13 黄晓平 Convenient colorimetric technique for detecting subaqueous polymorphic chlorine and its color comparator
CN101231245A (en) * 2008-02-26 2008-07-30 内蒙古蒙牛乳业(集团)股份有限公司 Method and kit for quick qualitative testing chlorine dioxide in milk
CN103207158A (en) * 2013-04-17 2013-07-17 上海绿帝环保科技有限公司 Water quality detecting agent for residual chlorine

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
Comparison of Spectrophotometric Methods for Measuring Chlorine Dioxide in Drinking Water;R.HOFMANN et al.;《Environmental Technology》;19981231;第19卷;761-773 *
N,N-二乙基对苯二胺(DPD)-硫酸亚铁铵滴定法测定水中二氧化氯问题的探讨;刘渊芳;《广东化工》;20110325;第38卷(第3期);269-270 *

Also Published As

Publication number Publication date
CN104677900A (en) 2015-06-03

Similar Documents

Publication Publication Date Title
CN104677900B (en) A kind of method of chlorine dioxide content in quick detection water for eliminating reagent blank influence
CN104792852B (en) A kind of Algae toxins molecular engram chemoreceptor sensor and its preparation method and application
CN101226154A (en) Indicating substance for on-line testing formaldehyde oxide gas concentration
CN105277535B (en) Ammonia nitrogen field fast detection method in a kind of water for eliminating reagent blank influence
CN105300970B (en) Total residual chlorine field fast detection method in a kind of water for eliminating reagent blank influence
CN101825579A (en) Method for measuring concentration of polyacrylamide solution
CN104359901A (en) Rapid detecting method for hydroxymethyl furfural in honey
CN105987903A (en) On-site quick detection kit of ammonia nitrogen in water and preparation method
CN102721786A (en) Method for determining ammonia nitrogen content in water
CN102435560B (en) Method for testing nitrification inhibition rate of stabilized fertilizer
CN106680062B (en) Utilize the method for resonance rayleigh light scattering method measurement anionic surfactant concentration
CN108267485A (en) The assay method of salinity in a kind of water
CN111024687B (en) Glutaraldehyde determination test paper and rapid determination method
CN108387573A (en) Hydroxymethylfurfural quick detection reagent, kit and detection method in a kind of honey
CN105319209B (en) Iron ion field fast detection method in a kind of water for eliminating reagent blank influence
CN105277542B (en) A kind of water nitrite field fast detection method for eliminating reagent blank influence
CN105987911A (en) Detection kit for on-site quick detection of fluorine ions in water and preparing method
CN106092935B (en) Method For Nitrate Content and its application in edaphon toxicity test
CN111504992A (en) Rapid detection kit for chlorine dioxide after ballast water disinfection
CN105300969B (en) Chromium ion field fast detection method in a kind of water for eliminating reagent blank influence
Tkáčová et al. Determination of chlorine dioxide and chlorite in water supply systems by verified methods
Breland et al. Determination of sea water alkalinity by direct equilibration with carbon dioxide
Fontela et al. Carbonate system species and pH
JP2009150836A (en) Analysis method of boron
CN105158307B (en) A kind of microcomponent's sample fluorine ion purification and alkaline collection device and its application

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant