CN102359959A - Method for determining sulfur dioxide oxidation rate of selective catalytic reduction denitration catalyst - Google Patents
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- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 title claims abstract description 34
- 239000003054 catalyst Substances 0.000 title claims abstract description 18
- 238000000034 method Methods 0.000 title claims abstract description 17
- 238000010531 catalytic reduction reaction Methods 0.000 title claims abstract description 10
- 238000007254 oxidation reaction Methods 0.000 title abstract description 4
- 230000003647 oxidation Effects 0.000 title abstract 3
- 239000007789 gas Substances 0.000 claims abstract description 81
- 238000010521 absorption reaction Methods 0.000 claims abstract description 39
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 28
- 239000003546 flue gas Substances 0.000 claims abstract description 28
- 239000007788 liquid Substances 0.000 claims abstract description 26
- 238000004448 titration Methods 0.000 claims abstract description 18
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims abstract description 14
- 238000011010 flushing procedure Methods 0.000 claims abstract description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 8
- 238000005070 sampling Methods 0.000 claims abstract description 7
- 229910021538 borax Inorganic materials 0.000 claims abstract description 6
- 238000001556 precipitation Methods 0.000 claims abstract description 6
- 235000010339 sodium tetraborate Nutrition 0.000 claims abstract description 6
- BSVBQGMMJUBVOD-UHFFFAOYSA-N trisodium borate Chemical compound [Na+].[Na+].[Na+].[O-]B([O-])[O-] BSVBQGMMJUBVOD-UHFFFAOYSA-N 0.000 claims abstract description 6
- KFZMGEQAYNKOFK-UHFFFAOYSA-N Isopropanol Chemical compound CC(C)O KFZMGEQAYNKOFK-UHFFFAOYSA-N 0.000 claims description 15
- ITHZDDVSAWDQPZ-UHFFFAOYSA-L barium acetate Chemical compound [Ba+2].CC([O-])=O.CC([O-])=O ITHZDDVSAWDQPZ-UHFFFAOYSA-L 0.000 claims description 14
- 238000006213 oxygenation reaction Methods 0.000 claims description 11
- 239000012530 fluid Substances 0.000 claims description 10
- 230000001590 oxidative effect Effects 0.000 claims description 10
- 238000005406 washing Methods 0.000 claims description 10
- QTBSBXVTEAMEQO-UHFFFAOYSA-M Acetate Chemical compound CC([O-])=O QTBSBXVTEAMEQO-UHFFFAOYSA-M 0.000 claims description 5
- 238000012545 processing Methods 0.000 claims description 5
- 230000001186 cumulative effect Effects 0.000 claims description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 2
- 239000001301 oxygen Substances 0.000 abstract description 2
- 229910052760 oxygen Inorganic materials 0.000 abstract description 2
- 230000002829 reductive effect Effects 0.000 description 4
- WWILHZQYNPQALT-UHFFFAOYSA-N 2-methyl-2-morpholin-4-ylpropanal Chemical compound O=CC(C)(C)N1CCOCC1 WWILHZQYNPQALT-UHFFFAOYSA-N 0.000 description 3
- 238000009833 condensation Methods 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- PVNIIMVLHYAWGP-UHFFFAOYSA-N Niacin Chemical compound OC(=O)C1=CC=CN=C1 PVNIIMVLHYAWGP-UHFFFAOYSA-N 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 230000005494 condensation Effects 0.000 description 2
- 239000003595 mist Substances 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 description 1
- GQPLMRYTRLFLPF-UHFFFAOYSA-N Nitrous Oxide Chemical class [O-][N+]#N GQPLMRYTRLFLPF-UHFFFAOYSA-N 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 1
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 1
- 235000011130 ammonium sulphate Nutrition 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 125000004435 hydrogen atom Chemical class [H]* 0.000 description 1
- 230000003189 isokinetic effect Effects 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- 229960003512 nicotinic acid Drugs 0.000 description 1
- 235000001968 nicotinic acid Nutrition 0.000 description 1
- 239000011664 nicotinic acid Substances 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 239000000779 smoke Substances 0.000 description 1
- AKEJUJNQAAGONA-UHFFFAOYSA-N sulfur trioxide Inorganic materials O=S(=O)=O AKEJUJNQAAGONA-UHFFFAOYSA-N 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- WKXHZKXPFJNBIY-UHFFFAOYSA-N titanium tungsten vanadium Chemical compound [Ti][W][V] WKXHZKXPFJNBIY-UHFFFAOYSA-N 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 229910052720 vanadium Inorganic materials 0.000 description 1
- LEONUFNNVUYDNQ-UHFFFAOYSA-N vanadium atom Chemical compound [V] LEONUFNNVUYDNQ-UHFFFAOYSA-N 0.000 description 1
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- Treating Waste Gases (AREA)
- Investigating Or Analyzing Non-Biological Materials By The Use Of Chemical Means (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
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):
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,
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,
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:
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,
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%,
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,
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,
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%,
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,
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,
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%,
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):
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,
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,
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Cited By (2)
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---|---|---|---|---|
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 |
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Cited By (2)
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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 |
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