CN101915743A - Method for calibrating online ozone analyzer - Google Patents
Method for calibrating online ozone analyzer Download PDFInfo
- Publication number
- CN101915743A CN101915743A CN 201010221398 CN201010221398A CN101915743A CN 101915743 A CN101915743 A CN 101915743A CN 201010221398 CN201010221398 CN 201010221398 CN 201010221398 A CN201010221398 A CN 201010221398A CN 101915743 A CN101915743 A CN 101915743A
- Authority
- CN
- China
- Prior art keywords
- ozone
- online
- gas
- nitrogen
- analyzer
- 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.)
- Granted
Links
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 title claims abstract description 148
- 238000000034 method Methods 0.000 title claims abstract description 19
- MWUXSHHQAYIFBG-UHFFFAOYSA-N Nitric oxide Chemical compound O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 claims abstract description 241
- MGWGWNFMUOTEHG-UHFFFAOYSA-N 4-(3,5-dimethylphenyl)-1,3-thiazol-2-amine Chemical compound CC1=CC(C)=CC(C=2N=C(N)SC=2)=C1 MGWGWNFMUOTEHG-UHFFFAOYSA-N 0.000 claims abstract description 18
- JCXJVPUVTGWSNB-UHFFFAOYSA-N nitrogen dioxide Inorganic materials O=[N]=O JCXJVPUVTGWSNB-UHFFFAOYSA-N 0.000 claims abstract description 18
- 238000005259 measurement Methods 0.000 claims abstract description 11
- 238000006243 chemical reaction Methods 0.000 claims abstract description 9
- 239000007789 gas Substances 0.000 claims description 147
- 229960003753 nitric oxide Drugs 0.000 claims description 92
- 235000019391 nitrogen oxide Nutrition 0.000 claims description 42
- 229910000831 Steel Inorganic materials 0.000 claims description 21
- 239000010959 steel Substances 0.000 claims description 21
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 20
- 229910052757 nitrogen Inorganic materials 0.000 claims description 10
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 8
- 239000001301 oxygen Substances 0.000 claims description 8
- 229910052760 oxygen Inorganic materials 0.000 claims description 8
- 230000009466 transformation Effects 0.000 claims description 8
- 230000000717 retained effect Effects 0.000 claims description 3
- 241000273930 Brevoortia tyrannus Species 0.000 description 14
- 230000007613 environmental effect Effects 0.000 description 4
- 238000007689 inspection Methods 0.000 description 4
- 238000013461 design Methods 0.000 description 3
- 238000002798 spectrophotometry method Methods 0.000 description 3
- 239000003570 air Substances 0.000 description 2
- ADCOVFLJGNWWNZ-UHFFFAOYSA-N antimony trioxide Chemical group O=[Sb]O[Sb]=O ADCOVFLJGNWWNZ-UHFFFAOYSA-N 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000005436 troposphere Substances 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- 238000002835 absorbance Methods 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 230000032683 aging Effects 0.000 description 1
- 239000012080 ambient air Substances 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 238000003556 assay Methods 0.000 description 1
- 238000004364 calculation method Methods 0.000 description 1
- 229910002091 carbon monoxide Inorganic materials 0.000 description 1
- 239000012159 carrier gas Substances 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000002795 fluorescence method Methods 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- KHLVKKOJDHCJMG-QDBORUFSSA-L indigo carmine Chemical compound [Na+].[Na+].N/1C2=CC=C(S([O-])(=O)=O)C=C2C(=O)C\1=C1/NC2=CC=C(S(=O)(=O)[O-])C=C2C1=O KHLVKKOJDHCJMG-QDBORUFSSA-L 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
Images
Landscapes
- Sampling And Sample Adjustment (AREA)
- Investigating Or Analyzing Non-Biological Materials By The Use Of Chemical Means (AREA)
Abstract
The invention relates to a method for calibrating an online ozone analyzer, which comprises the following steps of: 1) setting an air distribution system for calibrating the online ozone analyzer; 2) determining the nitrogen oxide conversion rate of the online nitrogen oxide analyzer; 3) calibrating the measurement accuracy of the online nitrogen oxide analyzer; 4) roughly determining the concentration of ozone generated by an ozone generating device with certain ozone generation capability in an air calibrator through the online ozone analyzer; 5) obtaining an accurate concentration value of nitrogen dioxide through the online nitrogen oxide analyzer and by combining the measurement accuracy of the online nitrogen oxide analyzer, namely obtaining an accurate concentration value of the ozone generated by the ozone generating device in the step 4); 6) comparing the accurate ozone concentration value obtained by the step 5) with the ozone concentration value roughly determined by the online ozone analyzer in the step 4), and calibrating the online ozone analyzer; and 7) returning to the step 4), resetting the ozone generation capability of the ozone generating device, and performing multipoint calibration on the online ozone analyzer.
Description
Technical field
The present invention relates to a kind of scaling method, particularly about a kind of scaling method of online ozone analyzer.
Background technology
The troposphere atmospheric ozone is one of important secondary light chemical pollutant that influences atmosphere quality, visibility, aerial oxygen voltinism and health, because its regional influence obviously, cause the concern of environmental administration and environment R﹠D institution gradually, therefore, the observation of troposphere atmospheric ozone also is included in the middle of the daily air quality monitoring system of environmental administration gradually.At present, assay method for ozone concentration has a lot, wherein, sodium indigotindisulfonate spectrophotometric method, ultraviolet spectrophotometry and chemiluminescence fluorescence method are three kinds of ozone analysis determining methods recommending in (GB3095-1996) of China's " ambient air quality " in 1996.And ultraviolet spectrophotometry be most widely used at present, method that technology is the most ripe, its principle is the ultraviolet light that utilizes under the ozone molecule absorption 254nm, according to Lambert-Beer's law, can be directly per sample gas to the ozone concentration in the absorbance log calculation sample gas of ultraviolet light.These class methods need be used online ozone analyzer in implementation procedure, the simple structure of online ozone analyzer, and ruuning situation is stable.But because instrument the excessive situation of drift value can occur after under situations such as carrying, installation, part aging and reaction tank pollution, using certain hour, but drift value is less in time owing to this instrument, often is difficult in the field inspection finding.
In order to guarantee the accurate operation of online ozone analyzer, need regularly it to be demarcated.Traditional scaling method of online ozone analyzer device is to use the standard ozone generator, produce a certain amount of, decide concentration of ozone as standard substance, after squeezing into online ozone analyzer, investigate the difference between input standard value and the instrument readout, investigate the accuracy of online ozone analyzer with this.The principle of ozone generator commonly used is made high-concentrated ozone for using high-voltage arc at present, is made into the output ozone of normal concentration through gas distributing system.Because standard ozone generator cost is higher and carry inconvenience, therefore most environmental administrations and scientific research institution, have restricted the observation effect of online ozone analyzer to a certain extent not to the independent outfit standard ozone generator of online ozone analyzer.
Summary of the invention
At the problems referred to above, the purpose of this invention is to provide a kind of strong operability, low, the accurate real-time height of device therefor cost, be applicable to the scaling method of the online ozone analyzer of field environment observation.
For achieving the above object, the present invention takes following technical scheme: a kind of scaling method of online ozone analyzer, it may further comprise the steps: 1) be provided with one and be used for gas distributing system that online ozone analyzer is demarcated, described gas distributing system comprises Zero gas generator, gas marking apparatus, online nitrogen-oxide analyzer,, online ozone analyzer, NPN calibrating gas steel cylinder and nitrogen monoxide calibrating gas steel cylinder; Be provided with three flow controllers, a mixing bunker and an ozone generating-device in the described gas marking apparatus; Be provided with the thermocatalysis reburner in the described online nitrogen-oxide analyzer; 2) NPN calibrating gas steel cylinder is connected to the gas marking apparatus after, NPN calibrating gas steel cylinder and Zero gas generator are squeezed into gas simultaneously in the gas marking apparatus, in mixing bunker, produce the NPN calibrating gas of deciding the concentration constant flow by the flow controller in the gas marking apparatus, the NPN calibrating gas of deciding the concentration constant flow that produces is driven in the online nitrogen-oxide analyzer,, utilize thermocatalysis reburner in the online nitrogen-oxide analyzer, will decide the oxides of nitrogen that contains in the NPN calibrating gas of concentration constant flow, be converted into nitrogen monoxide; Observe the difference between the nitrogen monoxide value that concentration constant flow NPN calibrating gas value and online nitrogen-oxide analyzer, read of deciding of input, determine that the thermocatalysis reburner is to the transformation efficiency A of the oxides of nitrogen in the NPN calibrating gas in the online nitrogen-oxide analyzer; 3) nitrogen monoxide calibrating gas steel cylinder is connected to the gas marking apparatus after, nitrogen monoxide calibrating gas steel cylinder and Zero gas generator are squeezed into gas simultaneously in the gas marking apparatus, in mixing bunker, produce the nitrogen monoxide calibrating gas of deciding the concentration constant flow by the flow controller in the gas marking apparatus, the nitrogen monoxide calibrating gas of deciding the concentration constant flow that produces is driven in the online nitrogen-oxide analyzer,, the constant flow of observing input decide the difference between the nitrogen monoxide value that concentration nitrogen monoxide calibrating gas value and online nitrogen-oxide analyzer, read, and cooperation transformation efficiency A determines the accuracy of measurement B of online nitrogen-oxide analyzer; 4) ozone generating-device in the unlatching gas marking apparatus, the ability that the ozone that ozone generating-device produces at this moment is set is a%, the span of a is 0～100, produce a certain amount of unknown concentration ozone, this part ozone is squeezed in the online ozone analyzer by flow controller, roughly determined the ozone concentration value C that squeezes into by online ozone analyzer; 5) open nitrogen monoxide calibrating gas steel cylinder, in the gas marking apparatus, squeeze into the nitrogen monoxide calibrating gas, keep ozone generating-device to open simultaneously, enter the ozone concentration that nitrogen monoxide calibrating gas concentration in the mixing bunker and ozone generating-device produce by the flow controller in gas marking apparatus control, wherein, enter nitrogen monoxide calibrating gas concentration in the mixing bunker and need surpass 1～2 times of ozone concentration C that online ozone analyzer roughly determines; Excessive nitrogen monoxide calibrating gas and ozone reaction generate nitrogen dioxide and oxygen, nitrogen dioxide that generates and oxygen and remaining nitrogen monoxide calibrating gas are retained in the mixing bunker in the gas marking apparatus, then the gas in the mixing bunker is directly squeezed in the online nitrogen-oxide analyzer,, write down the content of nitrogen dioxide value that online nitrogen-oxide analyzer, is read, accuracy of measurement B in conjunction with online nitrogen-oxide analyzer,, obtain the accurate concentration value D of nitrogen dioxide, promptly obtaining in the step 4) ozone generating-device is under the situation of a% producing the ozone ability, the exact value D of the ozone concentration of generation; 6) demarcation of online ozone analyzer: the ozone concentration value C that online ozone analyzer in the exact value D of the ozone concentration that obtains in the step 5) and the step 4) is roughly determined compares, and online ozone analyzer is demarcated; 7) return step 4), reset the value of a%, online ozone analyzer is carried out multi-point calibration.
The present invention is owing to take above technical scheme, it has the following advantages: 1, the present invention adopts the common equipment in the field inspections such as environmental administration and R﹠D institution atmospheric contaminant analyzer device commonly used at present, calibrating instrument to form gas distributing system, and adopt common agents to be used for online ozone analyzer is demarcated, and need not the independent outfit standard ozone generator of online ozone analyzer, therefore, not only saved cost, and have strong operability, convenient and swift, accuracy is high, be applicable to characteristics such as field environment observation.2, the present invention is by Zero gas generator and gas marking apparatus and NPN calibrating gas and nitrogen monoxide calibrating gas, can determine the conversion ratio of online nitrogen-oxide analyzer, to the oxides of nitrogen in the NPN calibrating gas, can determine the accuracy of measurement of online nitrogen-oxide analyzer, according to conversion ratio, lay the foundation for accurately demarcating online ozone analyzer.3, the present invention produces a certain amount of unknown concentration ozone by the ozoniferous ability of ozone generating-device in the gas marking apparatus is set, and roughly determines the ozone concentration value by online ozone analyzer; Reaction by nitrogen monoxide calibrating gas in the gas marking apparatus and ozone then, generate nitrogen dioxide and oxygen, accuracy of measurement according to online nitrogen-oxide analyzer,, can accurately measure the accurate concentration value of nitrogen dioxide, promptly obtain the exact value of ozone concentration, the exact value of this ozone concentration compares with the ozone concentration value of roughly determining, can demarcate online ozone analyzer.4, the present invention can be by being provided with in the gas marking apparatus, the ozoniferous different ability values of ozone generating-device, and then can carry out multi-point calibration to online ozone analyzer.The present invention is skillfully constructed, and is easy to operate, and the degree of accuracy height can be widely used in the calibration process of online ozone analyzer.
Description of drawings
Fig. 1 is the gas distributing system synoptic diagram that the present invention is used to demarcate
Embodiment
Below in conjunction with drawings and Examples the present invention is described in detail.
The present invention includes following steps:
1) be provided with one and be used for gas distributing system that online ozone analyzer is demarcated: as shown in Figure 1, this gas distributing system comprises conventional Zero gas generator 1, gas marking apparatus 2, online nitrogen-oxide analyzer, 3, online ozone analyzer 4, NPN calibrating gas steel cylinder 5 and nitrogen monoxide calibrating gas steel cylinder 6.Wherein, Zero gas generator 1 is used for gases such as airborne ozone, carbon monoxide, sulphuric dioxide, oxides of nitrogen are removed, thereby produce the gas of cleaning, and the clean air that produces squeezed in the gas marking apparatus 2, as the balance carrier gas, dilution enters the high concentration calibrating gas in the gas marking apparatus 2, thereby obtains deciding the calibrating gas of concentration, constant flow.Be provided with three flow controllers 21,22 and 23, one mixing bunkers 24 and an ozone generating-device 25 in the gas marking apparatus 2.Be provided with thermocatalysis reburner (not shown) in the online nitrogen-oxide analyzer, 3, effect is that the oxynitrides that will enter in the online nitrogen-oxide analyzer, 3 is converted to nitrogen monoxide.The NPN calibrating gas is one of gas commonly used in the atmosphere environment supervision, and English name is N-propylnitrate, and composition is: n-propyl nitrate, the NPN calibrating gas can directly be bought for demarcating transformation efficiency of the oxides of nitrogen usefulness.
2) measure the transformation efficiency of the oxides of nitrogen of online nitrogen-oxide analyzer, 3: after NPN calibrating gas steel cylinder 5 is connected to gas marking apparatus 2, NPN calibrating gas steel cylinder 5 and Zero gas generator 1 are squeezed into gas simultaneously in gas marking apparatus 2, by the flow controller in the gas marking apparatus 2 21,23 produce the NPN calibrating gas of deciding the concentration constant flow in mixing bunker 24, the NPN calibrating gas of deciding the concentration constant flow that produces is driven in the online nitrogen-oxide analyzer, 3, utilize thermocatalysis reburner in the online nitrogen-oxide analyzer, 3 will decide the oxides of nitrogen that contains in the NPN calibrating gas of concentration constant flow, be converted into nitrogen monoxide; Observe the difference between the nitrogen monoxide value that concentration constant flow NPN calibrating gas value and online nitrogen-oxide analyzer, 3 read of deciding of input, determine the transformation efficiency A of the oxides of nitrogen in 31 pairs of NPN calibrating gas of thermocatalysis reburner in the online nitrogen-oxide analyzer, 3.
3) measurement accuracy of online nitrogen-oxide analyzer, 3 is demarcated: after nitrogen monoxide calibrating gas steel cylinder 6 is connected to gas marking apparatus 2, nitrogen monoxide calibrating gas steel cylinder 6 and Zero gas generator 1 are squeezed into gas simultaneously in gas marking apparatus 2, by the flow controller in the gas marking apparatus 2 21,23 produce the nitrogen monoxide calibrating gas of deciding the concentration constant flow in mixing bunker 24, the nitrogen monoxide calibrating gas of deciding the concentration constant flow that produces is driven in the online nitrogen-oxide analyzer, 3, the constant flow of observing input decide the difference between the nitrogen monoxide value that concentration nitrogen monoxide calibrating gas value and online nitrogen-oxide analyzer, 3 read, and cooperation transformation efficiency A determines the accuracy of measurement B of online nitrogen-oxide analyzer.
4) ozone generating-device 25 in the unlatching gas marking apparatus 2, produce a certain amount of unknown concentration ozone, because design concept, the generation concentration of ozone generating-device 25 does not have the normal concentration design in the gas marking apparatus 2, the number percent design is only arranged, ozone generating-device 25 can ozoniferous maximum capacity be 100%, thousands of approximately ppb concentration, it is a%=30% that this step is provided with ozone generating-device 25 ozoniferous abilities, be that ozone generating-device 25 produces 30% of ozone maximum capacity, but be not limited thereto, the span of a is 0～100, this part ozone is squeezed in the online ozone analyzer 4 by flow controller 22, roughly determined the ozone concentration C that squeezes into by online ozone analyzer 4.
5) open nitrogen monoxide calibrating gas steel cylinder 6, in gas marking apparatus 2, squeeze into the nitrogen monoxide calibrating gas, keep ozone generating-device 25 to open simultaneously, enter the ozone concentration that nitrogen monoxide calibrating gas concentration in the mixing bunker 24 and ozone generating-device 25 produce by the flow controller in the gas marking apparatus 2 23,22 control, wherein, enter nitrogen monoxide calibrating gas concentration in the mixing bunker 24 and need surpass 1～2 times of ozone concentration C that online ozone analyzer 3 roughly determines.Excessive nitrogen monoxide calibrating gas and ozone reaction, generate nitrogen dioxide and oxygen, nitrogen dioxide and oxygen and remaining nitrogen monoxide calibrating gas are retained in the mixing bunker 24 in the gas marking apparatus 2, then the gas in the mixing bunker 24 is directly squeezed in the online nitrogen-oxide analyzer, 3, write down the content of nitrogen dioxide value that online nitrogen-oxide analyzer, 3 is read, in conjunction with the accuracy of measurement B of online nitrogen-oxide analyzer, 3, can obtain the accurate concentration value D of nitrogen dioxide.Because the mol ratio of nitrogen monoxide and ozone reaction is 1: 1, and the amount of generation nitrogen dioxide and the mol ratio of required nitric oxide production amount also are 1: 1, therefore, accurate concentration value D according to content of nitrogen dioxide, can obtain ozone generating-device 25 in the gas marking apparatus 2 is under 30% the situation producing the ozone ability, the accurate concentration value of the ozone that produces, promptly the accurate concentration value D with nitrogen dioxide is identical.
6) demarcation of online ozone analyzer: the ozone concentration value C that online ozone analyzer 4 in the accurate concentration value D of the ozone that obtains in the step 5) and the step 4) is roughly determined compares, and online ozone analyzer 4 is demarcated.
7) owing to the ozone generating-device 25 that has accurately obtained in the gas marking apparatus 2, it in ozoniferous ability the ozone concentration under 30% the situation, therefore, can return step 4), reset ozone generating-device 25 ozoniferous ability a%, for example a%=10%, a%=50% etc., determine the exact value of the ozone concentration of generation under the different ability conditions, therefore can very easily carry out multi-point calibration, thereby determine the degree of accuracy of online ozone analyzer 4 accurately online ozone analyzer 4.
The contrast of the inventive method and traditional scaling method is compared:
In order to verify the accuracy of the inventive method, by using this method and standard ozone generator (49PS) to contrast in the field inspection at the scene, comparing result shows, this method calibrated error can satisfy in the field inspection calibration request to online ozone analyzer fully between 1%～3%.
The various embodiments described above only are used to illustrate the present invention, and wherein the structure of each parts, connected mode etc. all can change to some extent, and every equivalents of carrying out on the basis of technical solution of the present invention and improvement all should not got rid of outside protection scope of the present invention.
Claims (1)
1. the scaling method of an online ozone analyzer, it may further comprise the steps:
1) be provided with one and be used for gas distributing system that online ozone analyzer is demarcated, described gas distributing system comprises Zero gas generator, gas marking apparatus, online nitrogen-oxide analyzer,, online ozone analyzer, NPN calibrating gas steel cylinder and nitrogen monoxide calibrating gas steel cylinder; Be provided with three flow controllers, a mixing bunker and an ozone generating-device in the described gas marking apparatus; Be provided with the thermocatalysis reburner in the described online nitrogen-oxide analyzer;
2) NPN calibrating gas steel cylinder is connected to the gas marking apparatus after, NPN calibrating gas steel cylinder and Zero gas generator are squeezed into gas simultaneously in the gas marking apparatus, in mixing bunker, produce the NPN calibrating gas of deciding the concentration constant flow by the flow controller in the gas marking apparatus, the NPN calibrating gas of deciding the concentration constant flow that produces is driven in the online nitrogen-oxide analyzer,, utilize thermocatalysis reburner in the online nitrogen-oxide analyzer, will decide the oxides of nitrogen that contains in the NPN calibrating gas of concentration constant flow, be converted into nitrogen monoxide; Observe the difference between the nitrogen monoxide value that concentration constant flow NPN calibrating gas value and online nitrogen-oxide analyzer, read of deciding of input, determine that the thermocatalysis reburner is to the transformation efficiency A of the oxides of nitrogen in the NPN calibrating gas in the online nitrogen-oxide analyzer;
3) nitrogen monoxide calibrating gas steel cylinder is connected to the gas marking apparatus after, nitrogen monoxide calibrating gas steel cylinder and Zero gas generator are squeezed into gas simultaneously in the gas marking apparatus, in mixing bunker, produce the nitrogen monoxide calibrating gas of deciding the concentration constant flow by the flow controller in the gas marking apparatus, the nitrogen monoxide calibrating gas of deciding the concentration constant flow that produces is driven in the online nitrogen-oxide analyzer,, the constant flow of observing input decide the difference between the nitrogen monoxide value that concentration nitrogen monoxide calibrating gas value and online nitrogen-oxide analyzer, read, and cooperation transformation efficiency A determines the accuracy of measurement B of online nitrogen-oxide analyzer;
4) ozone generating-device in the unlatching gas marking apparatus, the ability that the ozone that ozone generating-device produces at this moment is set is a%, the span of a is 0～100, produce a certain amount of unknown concentration ozone, this part ozone is squeezed in the online ozone analyzer by flow controller, roughly determined the ozone concentration value C that squeezes into by online ozone analyzer;
5) open nitrogen monoxide calibrating gas steel cylinder, in the gas marking apparatus, squeeze into the nitrogen monoxide calibrating gas, keep ozone generating-device to open simultaneously, enter the ozone concentration that nitrogen monoxide calibrating gas concentration in the mixing bunker and ozone generating-device produce by the flow controller in gas marking apparatus control, wherein, enter nitrogen monoxide calibrating gas concentration in the mixing bunker and need surpass 1～2 times of ozone concentration C that online ozone analyzer roughly determines; Excessive nitrogen monoxide calibrating gas and ozone reaction generate nitrogen dioxide and oxygen, nitrogen dioxide that generates and oxygen and remaining nitrogen monoxide calibrating gas are retained in the mixing bunker in the gas marking apparatus, then the gas in the mixing bunker is directly squeezed in the online nitrogen-oxide analyzer,, write down the content of nitrogen dioxide value that online nitrogen-oxide analyzer, is read, accuracy of measurement B in conjunction with online nitrogen-oxide analyzer,, obtain the accurate concentration value D of nitrogen dioxide, promptly obtaining in the step 4) ozone generating-device is under the situation of a% producing the ozone ability, the exact value D of the ozone concentration of generation;
6) demarcation of online ozone analyzer: the ozone concentration value C that online ozone analyzer in the exact value D of the ozone concentration that obtains in the step 5) and the step 4) is roughly determined compares, and online ozone analyzer is demarcated;
7) return step 4), reset the value of a%, online ozone analyzer is carried out multi-point calibration.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN2010102213983A CN101915743B (en) | 2010-06-29 | 2010-06-29 | Method for calibrating online ozone analyzer |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN2010102213983A CN101915743B (en) | 2010-06-29 | 2010-06-29 | Method for calibrating online ozone analyzer |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN101915743A true CN101915743A (en) | 2010-12-15 |
| CN101915743B CN101915743B (en) | 2012-05-30 |
Family
ID=43323304
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN2010102213983A Expired - Fee Related CN101915743B (en) | 2010-06-29 | 2010-06-29 | Method for calibrating online ozone analyzer |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN101915743B (en) |
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103399127A (en) * | 2013-08-16 | 2013-11-20 | 中国环境科学研究院 | Gas analyzer calibration measurement apparatus and calibration measurement method thereof |
| CN105314601A (en) * | 2014-07-29 | 2016-02-10 | 潘本锋 | Novel standard ozone generator |
| CN105911222A (en) * | 2016-04-18 | 2016-08-31 | 中国石油化工股份有限公司 | Metrological verification device for ammonia gas detector and metrological verification method thereof |
| CN107219324A (en) * | 2017-07-13 | 2017-09-29 | 中国科学院城市环境研究所 | The adjustable ozone purification evaluation system of a kind of humidity, content and evaluation method |
| CN109187456A (en) * | 2018-08-17 | 2019-01-11 | 南京科略环境科技有限责任公司 | A kind of atmosphere total oxidant photochemistry generating rate monitoring system |
| CN110763639A (en) * | 2019-11-13 | 2020-02-07 | 上海市计量测试技术研究院 | Calibration method of ozone analyzer in water |
| CN110987911A (en) * | 2020-01-06 | 2020-04-10 | 北京雪迪龙科技股份有限公司 | Ozone analysis method and ozone analyzer based on chemiluminescence method |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH07229833A (en) * | 1994-02-18 | 1995-08-29 | Ebara Jitsugyo Kk | Correction method of measurement for in-line insertion type concentration meter |
| JP2000162125A (en) * | 1998-11-26 | 2000-06-16 | Dkk Corp | Calibrating method and calibrating system of oxidant analyzer, and ozone generator |
| CN1920533A (en) * | 2005-08-24 | 2007-02-28 | 南引明 | Ozone concentration measurer |
-
2010
- 2010-06-29 CN CN2010102213983A patent/CN101915743B/en not_active Expired - Fee Related
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH07229833A (en) * | 1994-02-18 | 1995-08-29 | Ebara Jitsugyo Kk | Correction method of measurement for in-line insertion type concentration meter |
| JP2000162125A (en) * | 1998-11-26 | 2000-06-16 | Dkk Corp | Calibrating method and calibrating system of oxidant analyzer, and ozone generator |
| CN1920533A (en) * | 2005-08-24 | 2007-02-28 | 南引明 | Ozone concentration measurer |
Non-Patent Citations (4)
| Title |
|---|
| 《上海计量测试》 20091031 丁臻敏等 一种水中臭氧分析仪校准系统 12-13，17 1 , 第5期 2 * |
| 《中国空间科学学会第七次学术年会》 20090830 王英鉴等 紫外臭氧总量探测仪的涉及和定标 125 1 , 2 * |
| 《天津理工学院学报》 20020331 陈向辉等 动态气体校准仪的研究和应用 54-56 1 第18卷, 第1期 2 * |
| 《现代科学仪器》 20090630 黄一祥等 多元气体配气仪设计及精度分析 44-47 1 , 第3期 2 * |
Cited By (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103399127A (en) * | 2013-08-16 | 2013-11-20 | 中国环境科学研究院 | Gas analyzer calibration measurement apparatus and calibration measurement method thereof |
| CN105314601A (en) * | 2014-07-29 | 2016-02-10 | 潘本锋 | Novel standard ozone generator |
| CN105911222A (en) * | 2016-04-18 | 2016-08-31 | 中国石油化工股份有限公司 | Metrological verification device for ammonia gas detector and metrological verification method thereof |
| CN107219324A (en) * | 2017-07-13 | 2017-09-29 | 中国科学院城市环境研究所 | The adjustable ozone purification evaluation system of a kind of humidity, content and evaluation method |
| CN107219324B (en) * | 2017-07-13 | 2023-06-06 | 中国科学院城市环境研究所 | Ozone purification evaluation system and method with adjustable humidity and content |
| CN109187456A (en) * | 2018-08-17 | 2019-01-11 | 南京科略环境科技有限责任公司 | A kind of atmosphere total oxidant photochemistry generating rate monitoring system |
| CN109187456B (en) * | 2018-08-17 | 2020-10-20 | 南京科略环境科技有限责任公司 | System for monitoring photochemical generation rate of total atmospheric oxidant |
| CN110763639A (en) * | 2019-11-13 | 2020-02-07 | 上海市计量测试技术研究院 | Calibration method of ozone analyzer in water |
| CN110987911A (en) * | 2020-01-06 | 2020-04-10 | 北京雪迪龙科技股份有限公司 | Ozone analysis method and ozone analyzer based on chemiluminescence method |
Also Published As
| Publication number | Publication date |
|---|---|
| CN101915743B (en) | 2012-05-30 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN101915743B (en) | Method for calibrating online ozone analyzer | |
| CN103399127B (en) | A kind of gas analyzer calibration measurements device and calibration measuring method thereof | |
| CN203324220U (en) | Multi-component gas monitoring device | |
| US8654334B1 (en) | Incoherent cavity ringdown spectroscopy gas analyzer coupled with periodic chemical scrubbing | |
| CN107044958B (en) | A kind of measured oxygen concentration method of the measured oxygen concentration system based on ultraviolet broadband second level absorption spectrum | |
| CN211627359U (en) | Detecting system for sulfur trioxide content in flue gas | |
| EP2430440A1 (en) | Environmental control of fluid samples, calibration, and detection of concentration levels | |
| CN111982611A (en) | Online detection device and detection method for ammonia in flue gas | |
| CN104267019A (en) | Gas concentration calibrating and detecting method for laser Raman gas analyzer | |
| US9719891B2 (en) | Simultaneous multi-point testing systems and methods | |
| CN104020089A (en) | Method for calibrating PM2.5 (Particulate Matter2.5) monitor | |
| CN102175817A (en) | Device for simulating vapour hydrogen and oxygen stable isotope fluxes and application thereof | |
| CN103977739B (en) | A kind of atmospheric environment concentration peroxide gas generating system and method thereof | |
| CN202421062U (en) | Ultraviolet analyzer for measuring sulfur dioxide and nitrogen oxides | |
| CN203816579U (en) | Atmospheric environment concentration peroxide gas generation system | |
| CN208636206U (en) | A kind of pollutant testing apparatus | |
| CN202041462U (en) | Portable flue gas analyzer | |
| Baer et al. | Environmental and atmospheric monitoring using off-axis integrated cavity output spectroscopy (OA-ICOS) | |
| CN112945887B (en) | Flue gas in-situ monitoring system and method | |
| CN105314601A (en) | Novel standard ozone generator | |
| CN109358005A (en) | Content of nitrogen dioxide detection device and method | |
| RU71165U1 (en) | WIDE-BAND OZONE CONCENTRATION METER | |
| CN108956513A (en) | Portable ultraviolet spectrum flue gas analyzer and analysis method | |
| CN209589904U (en) | A kind of high-precision gas sensor array detection device | |
| CN202903672U (en) | Small-scale analytical system for sequential injection of nitrite |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| CF01 | Termination of patent right due to non-payment of annual fee | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20120530 |