CN102359959A - Method for determining sulfur dioxide oxidation rate of selective catalytic reduction denitration catalyst - Google Patents

Method for determining sulfur dioxide oxidation rate of selective catalytic reduction denitration catalyst Download PDF

Info

Publication number
CN102359959A
CN102359959A CN2011101747263A CN201110174726A CN102359959A CN 102359959 A CN102359959 A CN 102359959A CN 2011101747263 A CN2011101747263 A CN 2011101747263A CN 201110174726 A CN201110174726 A CN 201110174726A CN 102359959 A CN102359959 A CN 102359959A
Authority
CN
China
Prior art keywords
gas
unit
solution
ppm
concentration
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
CN2011101747263A
Other languages
Chinese (zh)
Inventor
肖雨亭
徐莉
王仁虎
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.)
Jiangsu Longyuan Catalyst Co Ltd
Original Assignee
Jiangsu Longyuan Catalyst Co Ltd
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 Jiangsu Longyuan Catalyst Co Ltd filed Critical Jiangsu Longyuan Catalyst Co Ltd
Priority to CN2011101747263A priority Critical patent/CN102359959A/en
Publication of CN102359959A publication Critical patent/CN102359959A/en
Pending legal-status Critical Current

Links

Landscapes

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

Abstract

The invention relates to a method for determining a sulfur dioxide oxidation rate of a selective catalytic reduction denitration catalyst. The method is characterized by comprising the following steps of 1, controlling a temperature of a gas trap in a range of 85 to 95 DEG C, and connecting the gas trap to a boiler for flue gas trapping, wherein a gas absorption bottle is connected to the gas trap and a H2O2 solution for absorption of SO2 gas is placed in the gas absorption bottle, 2, starting a suction pump and sucking out flue gas in the boiler, 3, after sampling, flushing the flue gas trapped by the gas trap by a sulfuric acid solution having a pH value of 5 to 6, and collecting the solution obtained by flushing, wherein the H2O2 solution absorbs SO2 gas to form absorption liquid, 4, through a sodium borate solution, titrating the solution obtained by flushing until a pH value of the solution obtained by flushing reaches 5.5, and calculating the concentration SO3(ppm) of SO3, 5, analyzing the concentration of SO2 in the absorption liquid by a precipitation titration method, and 6, calculating an oxidation rate of SO2. The method can guarantee that water vapor in flue gas does not condense; SO2 does not react with oxygen and water vapor; and a measuring result is accurate.

Description

Measure the method for denitrifying catalyst with selective catalytic reduction oxidizing sulfur dioxide rate
Technical field
The present invention relates to a kind of method of measuring the oxidizing sulfur dioxide rate, especially a kind of method of measuring denitrifying catalyst with selective catalytic reduction oxidizing sulfur dioxide rate.
Background technology
Along with country during " 12 " is more and more stricter to the control of discharged nitrous oxides; Simple low nitrogen burning technology can't satisfy the requirement of existing emission standard, and the coal-burning power plant uses SCR (SCR) technology because of its high-efficiency reliable denitration performance has begun at home.The cardinal principle of SCR is with NH 3Be reductive agent, under the effect of catalyzer, optionally with NO xBe reduced into N 2At present most widely used is honeycomb fashion vanadium tungsten titanium catalyst.
Owing to also have SO in the boiler smoke 2Deng gas, and the active component vanadium in the catalyzer also can be with the SO in the flue gas in the process of catalytic degradation NOx 2Oxidation generates SO 3, SO 3Generate ammonium hydrogen sulfate with unreacted reductive agent ammonia react in the SCR denitrification process.Ammonium hydrogen sulfate has viscosity, can work the mischief to air preheater and beds.Ammonium hydrogen sulfate has hydroscopicity at low temperatures, after suction from flue gas, can cause corrosion on Equipment to stop up.Behind flue gas process SCR reactor and the air preheater hot arc; Exhaust gas temperature reduces; The gaseous sulfuric acid hydrogen ammonium that when temperature is reduced to below 185 ℃, has generated in the flue gas can solidify on the heat transfer element of cold section of air preheater down, causes cold section salification of air preheater and fouling, and then influences the normal operation of air preheater.If stick to catalyst surface, can cause catalyst member to stop up, increase catalyst pressure drop or cause catalyst failure.
Therefore, SO in monitoring and the analysis flue gas 3And H 2SO 4Concentration, become regulation and control boiler operatiopn condition, check and accept and estimate the indispensable means of SCR catalyzer.SO 2Oxygenation efficiency becomes an important indicator estimating SCR catalyst performance and SCR system acceptance.
Summary of the invention
The objective of the invention is to overcome the deficiency that exists in the prior art; A kind of method of measuring denitrifying catalyst with selective catalytic reduction oxidizing sulfur dioxide rate is provided; Realized testing, the data support of control decision is provided for the content of sulfuric anhydride and ammonium sulfate in the performance of estimating denitrating catalyst, the control flue gas and the normal operation that ensures the coal-burning power plant denitrating catalyst oxidizing sulfur dioxide rate.
According to technical scheme provided by the invention, the method for said mensuration denitrifying catalyst with selective catalytic reduction oxidizing sulfur dioxide rate, characteristic is to comprise following processing step:
(1) temperature constant of pilot-gas drip catcher is at 85~95 ℃, and gas trap is connected on the boiler to capture flue gas, on gas trap, is connected with the gas absorption bottle, is contained with in the gas absorption bottle to be used to absorb SO 2The H of gas 2O 2Solution, said H 2O 2The mass percentage concentration of solution is 1%~3%;
(2) open aspiration pump, extract the flue gas in the boiler, the control speed of exhaust is 3~5L/min, and the gas sample volume is V, and the pressure of gas meter is Pm, and the temperature of gas meter is t;
(3) after sampling finished, using pH value was the flue gas on 5~6 the sulfuric acid solution flushing gas drip catcher, collection washing fluid, SO 2Gas is by H 2O 2The solution absorption liquid that is absorbed;
(4) using the dobell's solution titration washing fluid of 0.02mol/L is 5.5 up to pH, calculates SO through following formula 3Concentration SO 3(ppm):
SO 3 ( ppm ) = 0.224 × a × f V × 273 273 + t × Pa + Pm - Pv 760 × 1000 ( ppm ) ,
Wherein, the volume of the 0.02mol/L dobell's solution that a=consumes, unit is ml;
F=2, promptly concentration is the factor of the sodium borate of 0.02mol/L;
V=gas sample volume, unit are L;
T=gas meter temperature, unit is ℃;
Pa=atmospheric pressure, unit are mmHg;
Pm=gas meter pressure, unit are mmHg;
Water saturation vapour pressure under the Pv=gas meter temperature, unit is mmHg;
(5) adopt precipitation titration to analyze the SO in the absorption liquid 2Concentration, draw SO 2Concentration SO 2(ppm): the absorption liquid of getting 5~25ml is put into conical flask; Add 35~50ml isopropyl alcohol, 0.5~2ml acetate adds 3~5 indicator arsenazo III solution; Present blueness with the barium acetate solution titration absorption liquid of 0.05mol/L again and do not decorporate, calculate SO through following formula again 2Concentration,
SO 2 ( ppm ) = afV l / V s V g 273 273 + t Pa + Pm - Pv 760 · 1000 ,
Wherein, the volume of the 0.05mol/L barium acetate that a=consumes, unit is ml;
F=1.12 is the factor of 0.05mol/L barium acetate;
V 1The cumulative volume of=absorption liquid, unit are ml;
V sThe absorption liquid volume that=titration is used, unit is ml;
V g=gas sample volume, unit are 1;
T=gas meter temperature, unit is ℃;
Pa=atmospheric pressure, unit are mmHg;
Pm=gas meter pressure, unit are mmHg;
Water saturation vapour pressure under the Pv=gas meter temperature, unit is mmHg;
(6) SO 2The mensuration of oxygenation efficiency: adopt following formula to calculate SO 2Oxygenation efficiency η SO 2,
η SO 2 ( % ) = SO 3 ( ppm ) SO 2 ( ppm ) + SO 3 ( ppm ) × 100 .
The present invention has the following advantages:
(1) SO in the flue gas 3/ H 2SO 4All exist, guarantee that nicotinic acid steam all gets in the spiral condensation and collection pipe in downstream with gaseous form;
(2) get into the SO of spiral pipe with gaseous form 3And H 2SO 4Condensation immediately forms the acid mist droplet, and when utilizing the isokinetic sampling, the centrifugal force that in spiral pipe, produces in the flue gas aspiration procedure is with the H of droplet shape 2SO 4Be thrown to the wall of spiral pipe, and utilize the strong adsorbability of acid mist droplet, stick on the collection tube wall, be convenient to collect fully;
(3) collection tube places the water-bath more than 85~95 ℃, and this temperature is higher than the dewpoint temperature of water, and the water vapour in the flue gas can condensation, SO 2Can not react in this temperature, can not produce interference, measure accurately with oxygen, steam.
Embodiment
Below in conjunction with specific embodiment the present invention is described further.
Embodiment one: a kind of method of measuring denitrifying catalyst with selective catalytic reduction oxidizing sulfur dioxide rate comprises following processing step:
(1) temperature constant of pilot-gas drip catcher is at 93 ℃, and gas trap is connected on the boiler to capture flue gas, on gas trap, is connected with the gas absorption bottle, is contained with in the gas absorption bottle to be used to absorb SO 2The H of gas 2O 2Solution, said H 2O 2The mass percentage concentration of solution is 2.1%;
(2) open aspiration pump, extract the flue gas in the boiler, the control speed of exhaust is 4L/min, and the gas sample volume is V=120L, and the pressure of gas meter is Pm=43mmHg, and the temperature of gas meter is t=35 ℃;
(3) after sampling finished, using pH value was the flue gas on 5.5 the sulfuric acid solution flushing gas drip catcher, collection washing fluid, SO 2Gas is by H 2O 2The solution absorption liquid that is absorbed;
(4) using the dobell's solution titration washing fluid of 0.02mol/L is 5.5 up to pH, calculates SO through following formula 3Concentration SO 3(ppm)=5.0ppm:
SO 3 ( ppm ) = 0.224 × a × f V × 273 273 + t × Pa + Pm - Pv 760 × 1000 ( ppm ) ,
Wherein, a=1.20ml, the volume of the 0.02mol/L dobell's solution of consumption;
F=2, promptly concentration is the factor of the sodium borate of 0.02mol/L;
V=120L;
t=35;
Pa=760mmHg;
Pm=43mmHg;
Pv=42.1mmHg;
(5) adopt precipitation titration to analyze the SO in the absorption liquid 2Concentration, draw SO 2Concentration SO 2(ppm): the absorption liquid of getting 20ml is put into conical flask; Add the 40ml isopropyl alcohol, 1ml acetate adds 4 indicator arsenazo III solution; Present blueness with the barium acetate solution titration absorption liquid of 0.05mol/L again and do not decorporate, calculate SO through following formula again 2Concentration SO 2(ppm)=489.6ppm,
SO 2 ( ppm ) = afV l / V s V g 273 273 + t Pa + Pm - Pv 760 · 1000 ,
Wherein, a=9.31ml;
F=1.12 is the factor of 0.05mol/L barium acetate;
V 1=100ml;
V s=20ml;
V g=1201;
t=35℃;
Pa=760mmHg;
Pm=43mmHg;
Pv=42.1mmHg;
(6) SO 2The mensuration of oxygenation efficiency: adopt following formula to calculate SO 2Oxygenation efficiency η SO 2=1.01%,
η SO 2 ( % ) = SO 3 ( ppm ) SO 2 ( ppm ) + SO 3 ( ppm ) × 100 .
Embodiment two: a kind of method of measuring denitrifying catalyst with selective catalytic reduction oxidizing sulfur dioxide rate comprises following processing step:
(1) temperature constant of pilot-gas drip catcher is at 95 ℃, and gas trap is connected on the boiler to capture flue gas, on gas trap, is connected with the gas absorption bottle, is contained with in the gas absorption bottle to be used to absorb SO 2The H of gas 2O 2Solution, said H 2O 2The mass percentage concentration of solution is 2.5%;
(2) open aspiration pump, extract the flue gas in the boiler, the control speed of exhaust is 4.2L/min, and the gas sample volume is V=126L, and the pressure of gas meter is Pm=46mmHg, and the temperature of gas meter is t=36 ℃;
(3) after sampling finished, using pH value was the flue gas on 5.5 the sulfuric acid solution flushing gas drip catcher, collection washing fluid, SO 2Gas is by H 2O 2The solution absorption liquid that is absorbed;
(4) using the dobell's solution titration washing fluid of 0.02mol/L is 5.5 up to pH, calculates SO through following formula 3Concentration SO 3(ppm)=4.0ppm,
SO 3 ( ppm ) = 0.224 × a × f V × 273 273 + t × Pa + Pm - Pv 760 × 1000 ( ppm ) ,
Wherein, a=1.00ml, the volume of the 0.02mol/L dobell's solution of consumption;
F=2, promptly concentration is the factor of the sodium borate of 0.02mol/L;
V=126L;
t=36℃;
Pa=760mmHg;
Pm=46mmHg;
Pv=44.6mmHg;
(5) adopt precipitation titration to analyze the SO in the absorption liquid 2Concentration, draw SO 2Concentration SO 2(ppm): the absorption liquid of getting 15ml is put into conical flask; Add the 35ml isopropyl alcohol, 1ml acetate adds 4 indicator arsenazo III solution; Present blueness with the barium acetate solution titration absorption liquid of 0.05mol/L again and do not decorporate, calculate SO through following formula again 2Concentration SO 2(ppm)=508.8ppm,
SO 2 ( ppm ) = afV l / V s V g 273 273 + t Pa + Pm - Pv 760 · 1000 ,
Wherein, a=7.60ml, the volume of the 0.05mol/L barium acetate of consumption;
F=1.12 is the factor of 0.05mol/L barium acetate;
V 1=100ml;
V s=15ml;
V=126L;
t=36℃;
Pa=760mmHg;
Pm=46mmHg;
Pv=44.6mmHg;
(6) SO 2The mensuration of oxygenation efficiency: adopt following formula to calculate SO 2Oxygenation efficiency η SO 2=0.78%,
η SO 2 ( % ) = SO 3 ( ppm ) SO 2 ( ppm ) + SO 3 ( ppm ) × 100 .
Embodiment three: a kind of method of measuring denitrifying catalyst with selective catalytic reduction oxidizing sulfur dioxide rate comprises following processing step:
(1) temperature constant of pilot-gas drip catcher is at 90 ℃, and gas trap is connected on the boiler to capture flue gas, on gas trap, is connected with the gas absorption bottle, is contained with in the gas absorption bottle to be used to absorb SO 2The H of gas 2O 2Solution, said H 2O 2The mass percentage concentration of solution is 2.2%;
(2) open aspiration pump, extract the flue gas in the boiler, the control speed of exhaust is 3.9L/min, and the gas sample volume is V=118L, and the pressure of gas meter is Pm=32mmHg, and the temperature of gas meter is t=30 ℃;
(3) after sampling finished, using pH value was the flue gas on 5.5 the sulfuric acid solution flushing gas drip catcher, collection washing fluid, SO 2Gas is by H 2O 2The solution absorption liquid that is absorbed;
(4) using the dobell's solution titration washing fluid of 0.02mol/L is 5.5 up to pH, calculates SO through following formula 3Concentration SO 3(ppm)=3.5ppm,
SO 3 ( ppm ) = 0.224 × a × f V × 273 273 + t × Pa + Pm - Pv 760 × 1000 ( ppm ) ,
Wherein, a=0.83ml, the volume of the 0.02mol/L dobell's solution of consumption;
F=2, promptly concentration is the factor of the sodium borate of 0.02mol/L;
V=118L;
t=30℃;
Pa=760mmHg;
Pm=32mmHg;
Pv=31.8mmHg;
(5) adopt precipitation titration to analyze the SO in the absorption liquid 2Concentration, draw SO 2Concentration SO 2(ppm): the absorption liquid of getting 15ml is put into conical flask; Add the 35ml isopropyl alcohol, 1ml acetate adds 4 indicator arsenazo III solution; Present blueness with the barium acetate solution titration absorption liquid of 0.05mol/L again and do not decorporate, calculate SO through following formula again 2Concentration SO 2(ppm)=502.7ppm,
SO 2 ( ppm ) = afV l / V s V g 273 273 + t Pa + Pm - Pv 760 · 1000 ,
Wherein, a=7.16ml, the volume of the 0.05mol/L barium acetate of consumption;
F=1.12 is the factor of 0.05mol/L barium acetate;
V 1=100ml;
V s=15ml;
V=118L;
t=30℃;
Pa=760mmHg;
Pm=32mmHg;
Pv=31.8mmHg;
(6) SO 2The mensuration of oxygenation efficiency: adopt following formula to calculate SO 2Oxygenation efficiency η SO 2=0.69%,
η SO 2 ( % ) = SO 3 ( ppm ) SO 2 ( ppm ) + SO 3 ( ppm ) × 100 .

Claims (1)

1. a method of measuring denitrifying catalyst with selective catalytic reduction oxidizing sulfur dioxide rate is characterized in that, comprises following processing step:
(1) temperature constant of pilot-gas drip catcher is at 85~95 ℃, and gas trap is connected on the boiler to capture flue gas, on gas trap, is connected with the gas absorption bottle, is contained with in the gas absorption bottle to be used to absorb SO 2The H of gas 2O 2Solution, said H 2O 2The mass percentage concentration of solution is 1%~3%;
(2) open aspiration pump, extract the flue gas in the boiler, the control speed of exhaust is 3~5L/min, and the gas sample volume is V, and the pressure of gas meter is Pm, and the temperature of gas meter is t;
(3) after sampling finished, using pH value was the flue gas on 5~6 the sulfuric acid solution flushing gas drip catcher, collection washing fluid, SO 2Gas is by H 2O 2The solution absorption liquid that is absorbed;
(4) using the dobell's solution titration washing fluid of 0.02mol/L is 5.5 up to pH, calculates SO through following formula 3Concentration SO 3(ppm):
SO 3 ( ppm ) = 0.224 × a × f V × 273 273 + t × Pa + Pm - Pv 760 × 1000 ( ppm ) ,
Wherein, the volume of the 0.02mol/L dobell's solution that a=consumes, unit is ml;
F=2, promptly concentration is the factor of the sodium borate of 0.02mol/L;
V=gas sample volume, unit are L;
T=gas meter temperature, unit is ℃;
Pa=atmospheric pressure, unit are mmHg;
Pm=gas meter pressure, unit are mmHg;
Water saturation vapour pressure under the Pv=gas meter temperature, unit is mmHg;
(5) adopt precipitation titration to analyze the SO in the absorption liquid 2Concentration, draw SO 2Concentration SO 2(ppm): the absorption liquid of getting 5~25ml is put into conical flask; Add 35~50ml isopropyl alcohol, 0.5~2ml acetate adds 3~5 indicator arsenazo III solution; Present blueness with the barium acetate solution titration absorption liquid of 0.05mol/L again and do not decorporate, calculate SO through following formula again 2Concentration,
SO 2 ( ppm ) = afV l / V s V g 273 273 + t Pa + Pm - Pv 760 · 1000 ,
Wherein, the volume of the 0.05mol/L barium acetate that a=consumes, unit is ml;
F=1.12 is the factor of 0.05mol/L barium acetate;
V 1The cumulative volume of=absorption liquid, unit are ml;
V sThe absorption liquid volume that=titration is used, unit is ml;
V g=gas sample volume, unit are 1;
T=gas meter temperature, unit is ℃;
Pa=atmospheric pressure, unit are mmHg;
Pm=gas meter pressure, unit are mmHg;
Water saturation vapour pressure under the Pv=gas meter temperature, unit is mmHg;
(6) SO 2The mensuration of oxygenation efficiency: adopt following formula to calculate SO 2Oxygenation efficiency η SO 2,
η SO 2 ( % ) = SO 3 ( ppm ) SO 2 ( ppm ) + SO 3 ( ppm ) × 100 .
CN2011101747263A 2011-06-24 2011-06-24 Method for determining sulfur dioxide oxidation rate of selective catalytic reduction denitration catalyst Pending CN102359959A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2011101747263A CN102359959A (en) 2011-06-24 2011-06-24 Method for determining sulfur dioxide oxidation rate of selective catalytic reduction denitration catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2011101747263A CN102359959A (en) 2011-06-24 2011-06-24 Method for determining sulfur dioxide oxidation rate of selective catalytic reduction denitration catalyst

Publications (1)

Publication Number Publication Date
CN102359959A true CN102359959A (en) 2012-02-22

Family

ID=45585320

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2011101747263A Pending CN102359959A (en) 2011-06-24 2011-06-24 Method for determining sulfur dioxide oxidation rate of selective catalytic reduction denitration catalyst

Country Status (1)

Country Link
CN (1) CN102359959A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102778518A (en) * 2012-07-17 2012-11-14 东南大学 Method and device for measuring SOx in fire coal fume
CN108414516A (en) * 2018-06-12 2018-08-17 大唐环境产业集团股份有限公司 It is a kind of to measure device and method of power plant's denitrating catalyst to oxidation rate of sulfur dioxide

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4026665A (en) * 1976-06-11 1977-05-31 Fisher Scientific Company Method and apparatus for sulfur analysis
US4409336A (en) * 1981-02-17 1983-10-11 Standard Oil Company (Indiana) Method of analysis for determining very low sulfur levels in volatilizable samples
CN1865993A (en) * 2006-06-19 2006-11-22 上海吴泾化工有限公司 Combined detection method for high-purity SO3 gas and impurity SO2 gas therein
CN101109742A (en) * 2007-08-24 2008-01-23 中电投远达环保工程有限公司 Method for testing and analyzing warehouse separated type denitrated catalyzer
CN101509909A (en) * 2009-03-05 2009-08-19 河北省电力研究院 Sulphates content testing method in flue gas desulfurization system

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4026665A (en) * 1976-06-11 1977-05-31 Fisher Scientific Company Method and apparatus for sulfur analysis
US4409336A (en) * 1981-02-17 1983-10-11 Standard Oil Company (Indiana) Method of analysis for determining very low sulfur levels in volatilizable samples
CN1865993A (en) * 2006-06-19 2006-11-22 上海吴泾化工有限公司 Combined detection method for high-purity SO3 gas and impurity SO2 gas therein
CN101109742A (en) * 2007-08-24 2008-01-23 中电投远达环保工程有限公司 Method for testing and analyzing warehouse separated type denitrated catalyzer
CN101509909A (en) * 2009-03-05 2009-08-19 河北省电力研究院 Sulphates content testing method in flue gas desulfurization system

Non-Patent Citations (5)

* Cited by examiner, † Cited by third party
Title
NCASI SOUTHERN REGIONAL CENTER: "《EPA METHOD 8A-Determination of Sulfuric Acid Vapor or Mist and Sulfur Dioxide. Emissions from Kraft Recovery Furnaces》", 31 December 1996 *
无: "《JIS K0103-2005 Methods for determination of sulfur oxides in flue gas》", 31 December 2005 *
王方群等: "火电厂烟气中SO3的检测技术及应用", 《环境工程》 *
石志圣等: "沸腾炉气中二氧化硫和三氧化硫的快速分析", 《冶金分析》 *
黄梅芬等: "烟气中二氧化硫及三氧化硫测定方法的研究", 《理化检验一化学分册》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102778518A (en) * 2012-07-17 2012-11-14 东南大学 Method and device for measuring SOx in fire coal fume
CN108414516A (en) * 2018-06-12 2018-08-17 大唐环境产业集团股份有限公司 It is a kind of to measure device and method of power plant's denitrating catalyst to oxidation rate of sulfur dioxide

Similar Documents

Publication Publication Date Title
Liu et al. Absorption of carbon dioxide in aqueous ammonia
CN207730510U (en) A kind of harvester for sulfur trioxide in flue gas
CN102879239A (en) Flue gas pre-treatment type sampling and analysis device and method for escaping ammonia of denitration system of power plant
CN106353457B (en) A kind of detection flue gas SO absorbed based on salt3Method and system
CN105181614B (en) Sulfur trioxide analytical instrument and method
CN106248442B (en) SO in a kind of detection flue gas3Method
CN108303293A (en) System and method for sampling and detecting sulfur trioxide in coal-fired boiler flue gas
EP2380652A1 (en) System and method for controlling and reducing nox emissions
WO2005100947A1 (en) Method for sampling flue gas for analysis containing gas component having high susceptibility to adsorption
CN104458869A (en) Online ammonia escape monitoring and analyzing method and online ammonia escape monitoring and analyzing instrument
CN204116274U (en) The escaping of ammonia on-line monitoring analytical instrument
CN105352784A (en) Sampling method and device for testing concentration of SO3 acid mist in wet desulfuration flue gas
CN110806339A (en) SO in flue gas of thermal power plant3Sampling method
CN104931303A (en) Sampling device and sampling method for detecting ammonia escaping concentration of smoke denitration
JP2000009603A (en) Ammonia analyzer
CN106289884B (en) A kind of SO3The method of on-line checking
CN102359959A (en) Method for determining sulfur dioxide oxidation rate of selective catalytic reduction denitration catalyst
CN207248580U (en) One kind is based on flue-gas temperature and thermostat water bath coolant controlled SO3Sampling system
CN207866584U (en) Sulfur trioxide's sampling system in coal fired boiler flue gas
CN102818783B (en) Method and device for measuring ammonia escape amount in sintering flue gas ammonia-process desulfurization technique
CN202814766U (en) Escape ammonia sampling analyzing device of smoke pretreatment type power plant denitrating system
CN115792079A (en) Method for measuring ammonium sulfate and ammonium bisulfate in coal-fired flue gas
CN208206808U (en) A kind of measurement power plant's denitrating catalyst is to the device of oxidation rate of sulfur dioxide
CN215492692U (en) High-temperature extraction method ammonia escape on-line monitoring system
JPS59188553A (en) Method for pretreating sampling gas for measuring nitrogen oxide

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C12 Rejection of a patent application after its publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20120222