CN203663847U - Composite device for testing regeneration of SCR denitration catalyst and activity before and after regeneration - Google Patents

Composite device for testing regeneration of SCR denitration catalyst and activity before and after regeneration Download PDF

Info

Publication number
CN203663847U
CN203663847U CN201320733299.2U CN201320733299U CN203663847U CN 203663847 U CN203663847 U CN 203663847U CN 201320733299 U CN201320733299 U CN 201320733299U CN 203663847 U CN203663847 U CN 203663847U
Authority
CN
China
Prior art keywords
regeneration
active testing
reacting furnace
catalyst
furnace
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.)
Withdrawn - After Issue
Application number
CN201320733299.2U
Other languages
Chinese (zh)
Inventor
赵宁
李丽
汤龙华
盘思伟
韦正乐
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.)
Electric Power Research Institute of Guangdong Power Grid Co Ltd
Original Assignee
Electric Power Research Institute of Guangdong Power Grid 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 Electric Power Research Institute of Guangdong Power Grid Co Ltd filed Critical Electric Power Research Institute of Guangdong Power Grid Co Ltd
Priority to CN201320733299.2U priority Critical patent/CN203663847U/en
Application granted granted Critical
Publication of CN203663847U publication Critical patent/CN203663847U/en
Anticipated expiration legal-status Critical
Withdrawn - After Issue legal-status Critical Current

Links

Images

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Abstract

The utility model relates to a composite device for testing the regeneration of an SCR denitration catalyst and the activity before and after the regeneration. The device comprises an activity testing system and a regenerating system, wherein a vertical reacting furnace 1 is shared by the activity testing system and the regenerating system, and a gas analyzer is respectively arranged at an inlet and an outlet of the vertical reacting furnace 1; compressed air in a compressed air storage tank 12 of the regenerating system and regenerated liquid pumped out of a circulating pool 14 by a circulating pump 13 are respectively conveyed to a cleaning nozzle 17 arranged above an inner cavity of the reacting furnace 1 of the activity testing system, a dust separating plate 19 is arranged below the inner cavity of the reacting furnace, dust collecting grooves 20 are formed on both sides of the dust separating plate, and the outlets of the dust collecting grooves 20 are communicated to the circulating pool 14. Through the adoption of the device, the regeneration process of the catalyst is simplified, and the verification and the evaluation of an actual regeneration effect are convenient.

Description

The set composite of active testing before and after the regeneration of SCR denitrating catalyst and regeneration
Technical field
The utility model relates to a kind of set composite for active testing before and after the regeneration of SCR denitrating catalyst and regeneration.
Background technology
In order to tackle increasingly serious environment situation, country had strengthened the control dynamics to coal-burning power plant's Air Pollutant Emission in recent years, and denitrating flue gas becomes another emission control emphasis after dedusting, desulfurization.According to the requirement of up-to-date standard GB/T 13223-2011 " fossil-fuel power plant atmospheric pollutant emission standard ", from 1 day July in 2014, the discharged nitrous oxides concentration of most of existing thermal power generation boiler will be carried out 100mg/Nm 3limit value.In order to meet discharged nitrous oxides requirement under the new situation, a large amount of coal-fired units had started the transformation of Flue Gas Denitrification Engineering over the past two years, what wherein great majority were selected is the SCR that denitration efficiency is high, technique is more ripe (Selective Catalytic Reduction, SCR) gas denitrifying technology.
The core of SCR denitration technology is SCR denitrating catalyst, and in SCR denitrating system actual moving process, the activity of catalyst can decline, and along with the activity of catalyst declines, the performance of whole denitrating system also declines gradually.In the time that catalyst activity reduction arrives certain threshold value, must change processing.For the catalyst of inactivation, best processing mode is the processing of regenerating, and the activity of regeneration rear catalyst can be recovered to a certain extent, thereby has realized the recycling of decaying catalyst, and the secondary pollution of having avoided catalyst to bring, there is good economic benefit and environmental benefit.
The general process of catalyst regeneration is: first, and the activity of sampling and testing catalyst, and determine the main cause of catalysqt deactivation and the feasibility of regeneration by chemical analysis characterization method; Secondly,, according to catalysqt deactivation reason, select renovation process and prepare catalyst regeneration liquid it is carried out to actual reproduction; Finally, regeneration rear catalyst is carried out to active testing, whether checking regeneration produces a desired effect.At present, the renovation process of SCR catalyst mainly contains: washing regeneration, pickling regeneration, thermal process regeneration etc.According to the deactivation cause difference of catalyst, selected renovation process is also different.Generally, because the deactivation cause of catalyst is comparatively complicated, often need that multiple renovation process is compound to be selected, so that realize the at utmost recovery of catalyst activity.
Publication number is device and the technique that the utility model patent of CN102114422A has proposed a kind of SCR catalyst and can realize denitration reaction and regeneration, this utility model, by a SCR catalyst regeneration reaction unit and SCR catalyst denitration reaction device reaction unit that permeates, has realized the denitration simultaneously of SCR catalyst and regeneration.Regenerative process comprises that air purge, pickling the step such as supplement except alkali, drying and roasting, host, and regeneration rear catalyst can continue on for denitration reaction, but this utility model patent does not relate to the active testing of regeneration rear catalyst.
Publication number is that the utility model patent of CN102103047A has proposed a kind of method and apparatus detecting for fume denitration catalyst activity, the Main Components of the accurate control simulation flue gas of the method, simulated flue gas completes denitration reaction process after entering the reactor that catalyst to be measured is housed, by flue gas NO change in concentration situation before and after flue gas analyzer detection reaction device, thereby obtain the activity of catalyst.This apparatus system is simple, and parameter control is accurate, but this scheme institute detecting catalyst module requires to be less than 500cm 3, be difficult to meet the testing requirement to SCR catalyst monomer module.
In prior art, not yet find that there is the set composite that can simultaneously carry out the regeneration of SCR denitrating catalyst and regeneration front and back active testing.
Utility model content
Technical problem to be solved in the utility model, is just to provide a kind of set composite for active testing before and after the regeneration of SCR denitrating catalyst and regeneration, and this device has been simplified the regenerative process of catalyst effectively, is convenient to checking and evaluation to actual reproduction effect.
Solve the problems of the technologies described above, the utility model adopts following technical scheme:
Before and after the regeneration of SCR denitrating catalyst and regeneration, a set composite for active testing, comprises active testing system and regenerative system, it is characterized in that: described active testing system and regenerative system share a vertical response stove 1;
Described active testing system comprises vertical response stove 1, and the import/export of vertical response stove 1 is respectively provided with a set of gas analyzer;
Described regenerative system comprises compressed air reservoir 12, circulatory pool 14, circulating pump 13, threeway changeover valve 11, washer jet 17, every hawk 19, ash collection slot 20, the compressed air of described compressed air reservoir 12 and being delivered to respectively after threeway changeover valve 11 by the regenerated liquid that circulating pump 13 pumps circulatory pool 14, then the washer jet 17 of top of reacting furnace 1 inner chamber through being arranged in active testing system to reacting furnace in decaying catalyst purge and spray cleaning; Be arranged in the below of reacting furnace inner chamber every hawk 19, the partition for purge to bottom pipeline, prevents and treats pipeline blockage, and ash collection slot 20 is arranged in the both sides every hawk, the dust stratification producing for collecting purge, and circulatory pool 14 is led in the outlet of ash collection slot 20.
Described active testing system comprises NH 3, N 2, O 2, SO 2, NO gas cylinder group 3, water evaporation device 9, mix preheating furnace 8, reacting furnace 1 and condensation absorption plant 18; Described NH 3gas cylinder is connected directly to reacting furnace entrance by pipeline, described N 2, O 2, SO 2, NO gas cylinder with mix preheating furnace 8 and pass through pipeline connection, each gas passes to mix in preheating furnace and mixes and preheat, described water evaporation device 9 is connected to and is mixed preheating furnace entrance by pipeline, the steam producing passes into and mixes in preheating furnace, described mixing preheating furnace 8, reacting furnace 1 and condensation absorption plant 18 use pipelines are connected successively, each gas, after mixing, preheating, reaction, is discharged through the post processing of condensation absorption plant;
On the basis of the above, the utility model can also have following various improvement:
1, in described reacting furnace stove, be provided with heater 6 and temperature controller 7, regulate temperature in corresponding stove according to different step;
2, described active testing system to reacting furnace, regenerative system is provided with switch valve to the connecting line of reacting furnace, for the mutual isolation of regenerative system and active testing system;
3, described mixing preheating furnace is also provided with heater and temperature controller, and the temperature of mixing preheating furnace while controlling active testing is 300 DEG C;
4, described NH 3, N 2, O 2, SO 2, NO gas cylinder connecting line on be provided with pressure-reducing valve 4 and mass flowmenter 5, described water evaporation device and mix on the connecting line of preheating furnace and be also provided with mass flowmenter, for the accurate control to each composition flow rate;
5, on the pipeline that described compressed air reservoir is connected with threeway changeover valve, be also provided with pressure-reducing valve and mass flowmenter, for controlling the purging pressure of purge;
6, in described circulatory pool, can add deionized water or regenerated liquid, circulating-pump outlet is also provided with mass flowmenter, for controlling to adjust the cleaning flow of cleaning process;
7, the outer wall of described reacting furnace is also coated with one deck insulating 21;
8, described circulatory pool is also provided with dosing mouth 15 and floss hole 16, for interpolation and the replacing of solution in pond.
The course of work of the present utility model:
(1) active testing before regeneration: the SCR catalyst of inactivation is packed in reacting furnace, decaying catalyst is carried out to active testing, active testing process adopts gas cylinder group to simulate actual flue gas condition, by mixing after preheating, each component gas enters and in reacting furnace, completes denitration reaction, by the nitrous oxides concentration of gas analyzer test reaction stove entrance and exit, and then calculate the activity constant K value before decaying catalyst regeneration;
The activity constant K of SCR catalyst 1value is calculated according to following formula:
K(α)=-AVln(1-η);
In formula, the activity constant value that K is catalyst, m/h; AV is air velocity, m 3/ H stp, wet/ m 2; η is transformation efficiency of the oxides of nitrogen, %, η=(C 0-C 1)/C 0, C 0, C 1be respectively nitrogen oxide entrance and exit concentration, mg/Nm 3;
(2) actual reproduction of catalyst: regenerative process mainly comprises the steps:
1. purge deashing: adopt oil-free compressed air to carry out purge to decaying catalyst, remove the dust stratification on catalyst duct and surface;
2. solution cleans: catalyst regeneration liquid is packed in circulatory pool, by circulating pump, regenerated liquid is inputted in reacting furnace, decaying catalyst is sprayed to cleaning;
3. rinsing recovers: deionized water is packed in circulatory pool, by circulating pump, deionized water is inputted in reacting furnace, decaying catalyst is carried out to rinsing Recovery processing;
4. drying and roasting: adopt oil-free compressed air, under certain temperature conditions, the decaying catalyst in reacting furnace is carried out to drying and roasting processing;
Above-mentioned steps also can be carried out repetition or increase according to the actual inactivation situation of catalyst;
(3) active testing after regeneration: the catalyst after treatment of regenerating is carried out to active testing, and the same step of process (1), calculates the catalyst activity constant K after regeneration 2value, (being to introduce first this concept for the first time) introduces the regeneration recovery coefficient K of catalyst again h, evaluate regeneration recovery coefficient K for the regeneration effect to catalyst hcomputing formula is as follows:
K h=K 2/K 1
In the utility model, the gas cylinder group of described step (1) includes N 2, O 2, NO, NH 3, SO 2be used for simulating actual flue gas condition, also include water evaporation device, be used for passing into steam in reacting furnace, described mixing preheating furnace and reacting furnace all dispose heater and temperature controller, for accurately controlling the temperature of mixing preheating furnace and reacting furnace, mix preheat temperature and are set as 300 DEG C, the Temperature Setting of reaction system is 350~420 DEG C, specifically according to the optimum activity Temperature Setting of catalyst; The purging deashing process of described step (2), purges pressure and can be set as 0.4~0.6MPa, and the regenerated liquid pH value control range that described solution cleaning process adds is 4~6, and scavenging period is 2~3h; Described rinsing recovery process, rinsing time is 1~2h; Described drying and roasting process is carried out under compressed air atmosphere, and pressure setting is 0.1MPa, and baking temperature is 300~360 DEG C,, be 2~3h drying time.
Compared with prior art, the utlity model has following remarkable result:
(1) SCR catalyst activity test of the present utility model shares a set of reacting furnace with regeneration, realize the compound of regeneration and regeneration front and back active testing function, after catalyst regeneration, can directly carry out active testing, this systematic economy is efficient, the dismounting of catalyst and the workload of again loading, remarkable in economical benefits are greatly reduced;
(2) circulatory pool of the present utility model can add deionized water, acid solution, composite regenerated liquid etc., can be according to user's request, realize the functions such as washing, pickling and the composite cleaning of SCR catalyst, and simple in structure, regenerative process is convenient, easy operating;
(3) the utility model can be realized purging, washing, rinsing, the drying and other steps to decaying catalyst by threeway changeover valve, needn't dismounting catalyst in regenerative process, simplify regeneration step, and avoid the wearing and tearing of being dismounted for multiple times process to catalyst;
(4) NH in active testing system of the present utility model 3gas circuit directly passes into reacting furnace top, has reduced NH 3with SO 2side reaction occur, avoided the sulfate and the obstruction of ammonium sulfate salt material to system that generate;
(5) reacting furnace of the present utility model can be loaded the small-sized test module of catalyst or catalyst monomer test module, meets catalyst activity test and the regeneration effect evaluation requirements of different user, has a good application prospect.
Brief description of the drawings
Below in conjunction with the drawings and specific embodiments, the utility model is described in further detail.
Accompanying drawing is the overall structure schematic diagram of the evaluating combined device of the utility model SCR denitrating catalyst regeneration effect.
Description of reference numerals
1, reacting furnace; 2, switch valve; 3, gas cylinder group; 4, pressure-reducing valve; 5, mass flowmenter; 6, heater; 7, temperature controller; 8, mix preheating furnace; 9, water evaporation device; 10, gas analyzer; 11, threeway changeover valve; 12, compressed air reservoir; 13, circulating pump; 14, circulatory pool; 15, dosing mouth; 16, floss hole; 17, washer jet; 18, condensation absorption plant; 19, every hawk; 20, ash collection slot; 21, insulating.
Detailed description of the invention
As shown in drawings, before and after SCR denitrating catalyst regeneration of the present utility model and regeneration, the set composite of active testing, comprises the active testing system and the regenerative system that share a vertical response stove 1, and the import/export of vertical response stove 1 is respectively provided with a set of gas analyzer.
Active testing system comprises NH 3, N 2, O 2, SO 2, NO gas cylinder 3, water evaporation device 9, mix preheating furnace 8, reacting furnace 1 and condensation absorption plant 18; NH 3gas cylinder 3 is connected to reacting furnace 1 entrance, N by pipeline 2, O 2, SO 2, NO gas cylinder 3 with mix preheating furnace 8 and pass through pipeline connection, each gas passes to mix in preheating furnace 8 and mixes and preheat, water evaporation device 9 is connected to and is mixed preheating furnace 8 entrances by pipeline, the steam producing passes into and mixes in preheating furnace 8, mixing preheating furnace 8, reacting furnace 1 are connected successively with condensation absorption plant 18, each gas, after mixing, preheating, reaction, is discharged through 18 post processings of condensation absorption plant.
Regenerative system comprises compressed air reservoir 12, circulatory pool 14, circulating pump 13, threeway changeover valve 11, washer jet 17, every hawk 19, ash collection slot 20; Compressed air reservoir 12 is connected to threeway changeover valve 11 by pipeline, circulatory pool 14 is connected by pipeline with circulating pump 13, circulating pump 13 exports by pipeline and is connected to threeway changeover valve 11, threeway changeover valve 11 is connected to washer jet 17 by pipeline, washer jet 17 is arranged in the top of reacting furnace 1, cleans for the purging to reacting furnace 1 interior decaying catalyst and spray.Be arranged in the below of reacting furnace every hawk 19, the partition for purge to bottom pipeline, prevents and treats pipeline blockage, and described ash collection slot 20 is arranged in every the both sides of hawk 19, the dust stratification producing for collecting purge, and circulatory pool 14 is led in the outlet of ash collection slot 20.
Vertical response stove 1 can be realized the regeneration processing of denitration reaction process and catalyst, is provided with heater 6 and temperature controller 7 in stove, regulates temperature in corresponding stove according to different step.
Active testing system to reacting furnace 1, regenerative system is provided with switch valve 2 to the connecting line of reacting furnace 1, for the mutual isolation of regenerative system and active testing system; Mix preheating furnace 8 and be also provided with heater 6 and temperature controller 7, the temperature of mixing preheating furnace while controlling active testing is 300 DEG C; NH 3, N 2, O 2, SO 2, NO gas cylinder 3 connecting line on be provided with pressure-reducing valve 4 and mass flowmenter 5, water evaporation device 9 and mix on the connecting line of preheating furnace 8 and be also provided with mass flowmenter 5, for the accurate control to each composition flow rate; On the pipeline that compressed air reservoir 12 is connected with threeway changeover valve 11, be also provided with pressure-reducing valve 4 and mass flowmenter 5, for controlling the purging pressure of purge; In circulatory pool 14, can add deionized water or regenerated liquid, circulating pump 13 exports and is also provided with mass flowmenter 5, for controlling to adjust the cleaning flow of cleaning process; The outer wall of reacting furnace 1 is also coated with one deck insulating 21; Circulatory pool 14 is also provided with dosing mouth 15 and floss hole 16, for interpolation and the replacing of solution in pond.
The course of work
Embodiment 1
Honeycomb fashion SCR denitrating catalyst monomer to an inactivation is regenerated and regeneration effect evaluation.The honeycomb type denitrification catalyst monomer that the catalyst A of getting is 150mm × 150mm × 870mm, key component is V 2o 5-WO 3/ TiO 2.
Implementation process comprises the steps:
(1) active testing before regeneration: the SCR catalyst of inactivation is packed in reacting furnace 1, closing switch valve 2C, 2D, by regenerative system isolation, opening switch valve 2A, 2B, carry out active testing to catalyst A, and active testing process is as follows:
First open N 2gas cylinder 3 and pressure-reducing valve 4, quality of regulation flowmeter 5, controls N 2flow is 10L/min; Heater 6, regulates temperature controller 7, and the temperature of setting respectively mixing preheating furnace 8 and reacting furnace 1 is 300 DEG C and 350 DEG C; Until temperature rise arrive design temperature and stable after, open other gas cylinders 3 and water evaporation device 9, set by the true empty-running speed of catalyst A and Gas Parameters, regulate inlet flue gas parameter as following table by mass flowmenter 4:
Project Unit
O 2 3.9(Vol%)
SO 2 0.06(Vol%)
H 2O 9.6(Vol%)
NO 450(mg/Nm 3
NH 3 450(mg/Nm 3
N 2 Other
Opening switch valve 2E, 2F, open gas analyzer 10 respectively, measures importing and exporting NO concentration, when measuring after concentration stabilize 30min, starts to record NO concentration, and calculate the catalyst A activity constant K before regeneration 1value, for 14.71m/h, completes active testing process.
(2) actual reproduction of catalyst: the regenerative process of the present embodiment comprises the steps:
1. purge deashing: closing switch valve 2A, opening switch valve 2C, regulates threeway changeover valve 11 to compressed air communication pipeline, opens compressed air reservoir 12, adopts oil-free compressed air to carry out purge, removes the dust stratification on catalyst duct and surface; Keeping purging pressure is 0.5MPa, continues to purge 30min;
2. solution cleans: closing switch valve 2B, opening switch valve 2D, regulate threeway changeover valve 11 to circulating pump 13 connecting pipelines, by dosing mouth 15, regenerated liquid (the present embodiment is selected sulfuric acid solution and deionized water preparation) is packed in circulatory pool 14, regulating pH is 5.0, by circulating pump 13, interior circulatory pool 14 solution is inputted in reacting furnace 1 by washer jet 17, and catalyst A is sprayed to cleaning, continue wash cycles 3h, by floss hole 16, solution is discharged;
3. rinsing recovers: deionized water is packed in circulatory pool 14, by circulating pump 13, deionized water is inputted in reacting furnace 1, catalyst A is carried out to rinsing Recovery processing, rinsing time control is 1.5h;
4. drying and roasting: closing switch valve 2D, opening switch valve 2B, regulate threeway changeover valve 11 to compressed air communication pipeline, open reacting furnace heater 6, regulating reacting furnace temperature is 320 DEG C, adopt oil-free compressed air to carry out drying and roasting processing to the catalyst A in reacting furnace 1, drying time, 1h, completed regenerative process.
(3) active testing after regeneration: the catalyst after treatment of regenerating is carried out to active testing, and the same step of process (1), calculates the catalyst A activity constant K after regeneration 2value is 30.11m/h, and then calculates the regeneration recovery coefficient K of catalyst hbe 2.05, regeneration effect is obvious.
Embodiment 2
Honeycomb fashion SCR denitrating catalyst monomer to an inactivation is regenerated and regeneration effect evaluation.The honeycomb type denitrification catalyst monomer that the catalyst B of getting is 150mm × 150mm × 900mm, key component is V 2o 5-WO 3/ TiO 2.
Implementation process comprises the steps:
(1) active testing before regeneration: the SCR catalyst of inactivation is packed in reacting furnace 1, closing switch valve 2C, 2D, by regenerative system isolation, opening switch valve 2A, 2B, carry out active testing to catalyst B, and active testing process is as follows:
First open N 2gas cylinder 3 and pressure-reducing valve 4, quality of regulation flowmeter 5, controls N 2flow is 10L/min; Heater 6, regulates temperature controller 7, and the temperature of setting respectively mixing preheating furnace 8 and reacting furnace 1 is 300 DEG C and 350 DEG C; Until temperature rise arrive design temperature and stable after, open other gas cylinders 3 and water evaporation device 9, set by the true empty-running speed of catalyst A and Gas Parameters, regulate inlet flue gas parameter as following table by mass flowmenter 4:
Project Unit
O 2 4.1(Vol%)
SO 2 0.06(Vol%)
H 2O 9.6(Vol%)
NO 408(mg/Nm 3
NH 3 408(mg/Nm 3
N 2 Other
Opening switch valve 2E, 2F, open gas analyzer 10 respectively, measures importing and exporting NO concentration, when measuring after concentration stabilize 30min, starts to record NO concentration, and calculate the catalyst B activity constant K before regeneration 1value, for 18.63m/h, completes active testing process.
(2) actual reproduction of catalyst: the regenerative process of the present embodiment comprises the steps:
1. purge deashing: closing switch valve 2A, opening switch valve 2C, regulates threeway changeover valve 11 to compressed air communication pipeline, opens compressed air reservoir 12, adopts oil-free compressed air to carry out purge, removes the dust stratification on catalyst duct and surface; Keeping purging pressure is 0.6MPa, continues to purge 45min;
2. solution cleans: closing switch valve 2B, opening switch valve 2D, regulate threeway changeover valve 11 to circulating pump 13 connecting pipelines, by dosing mouth 15, regenerated liquid (the present embodiment is selected acetum and deionized water preparation) is packed in circulatory pool 14, regulating pH is 5.0, by circulating pump 13, interior circulatory pool 14 solution is inputted in reacting furnace 1 by washer jet 17, and catalyst A is sprayed to cleaning, continue wash cycles 2h, by floss hole 16, solution is discharged;
3. rinsing recovers: deionized water is packed in circulatory pool 14, by circulating pump 13, deionized water is inputted in reacting furnace 1, catalyst A is carried out to rinsing Recovery processing, rinsing time control is 1h;
4. drying and roasting: closing switch valve 2D, opening switch valve 2B, regulate threeway changeover valve 11 to compressed air communication pipeline, open reacting furnace heater 6, regulating reacting furnace temperature is 320 DEG C, adopt oil-free compressed air to carry out drying and roasting processing to the catalyst B in reacting furnace 1, drying time, 1h, completed regenerative process.
(3) active testing after regeneration: the catalyst after treatment of regenerating is carried out to active testing, and the same step of process (1), calculates the catalyst B activity constant K after regeneration 2value is 33.87m/h, and then calculates the regeneration recovery coefficient K of catalyst hbe 1.82, regeneration effect is obvious.

Claims (10)

1. the set composite of active testing before and after SCR denitrating catalyst regeneration and regeneration, comprise active testing system and regenerative system, it is characterized in that: described active testing system comprises vertical response stove (1), and the import/export of vertical response stove is respectively provided with a set of gas analyzer; Described regenerative system comprises compressed air reservoir (12), circulatory pool (14), circulating pump (13), threeway changeover valve (11), washer jet (17), every hawk (19), ash collection slot (20), the compressed air of described compressed air reservoir (12) and being delivered to respectively after threeway changeover valve (11) by the regenerated liquid that circulating pump (13) pumps circulatory pool (14), then the washer jet (17) of top of reacting furnace (1) inner chamber through being arranged in active testing system to reacting furnace in decaying catalyst purge and spray cleaning; Be arranged in the below of reacting furnace inner chamber every hawk (19), for the partition of purge to bottom pipeline, prevent and treat pipeline blockage, ash collection slot (20) is arranged in the both sides every hawk, the dust stratification producing for collecting purge, circulatory pool (14) is led in the outlet of ash collection slot (20).
2. the set composite of active testing before and after SCR denitrating catalyst regeneration according to claim 1 and regeneration, is characterized in that: described active testing system comprises NH3, N2, O2, SO2, NO gas cylinder group (3), water evaporation device (9), mixes preheating furnace (8), reacting furnace (1) and condensation absorption plant (18); Described NH3 gas cylinder is connected directly to reacting furnace entrance by pipeline, described N2, O2, SO2, NO gas cylinder and mix preheating furnace (8) and pass through pipeline connection, each gas passes to mix in preheating furnace and mixes and preheat, described water evaporation device (9) is connected to and is mixed preheating furnace entrance by pipeline, the steam producing passes into and mixes in preheating furnace, described mixing preheating furnace (8), reacting furnace (1) and condensation absorption plant (18) are connected successively with pipeline, each gas, after mixing, preheating, reaction, is discharged through the post processing of condensation absorption plant.
3. the set composite of active testing before and after SCR denitrating catalyst regeneration according to claim 2 and regeneration, it is characterized in that: in described reacting furnace stove, be provided with heater (6) and temperature controller (7), regulate temperature in corresponding stove according to different step.
4. the set composite of active testing before and after SCR denitrating catalyst regeneration according to claim 3 and regeneration, it is characterized in that: described active testing system to reacting furnace, regenerative system is provided with switch valve to the connecting line of reacting furnace, for the mutual isolation of regenerative system and active testing system.
5. the set composite of active testing before and after SCR denitrating catalyst regeneration according to claim 4 and regeneration, it is characterized in that: described mixing preheating furnace is also provided with heater and temperature controller, the temperature of mixing preheating furnace while controlling active testing is 300 DEG C.
6. the set composite of active testing before and after SCR denitrating catalyst regeneration according to claim 5 and regeneration, is characterized in that: described NH 3, N 2, O 2, SO 2, NO gas cylinder connecting line on be provided with pressure-reducing valve (4) and mass flowmenter (5), described water evaporation device and mix on the connecting line of preheating furnace and be also provided with mass flowmenter, for the accurate control to each composition flow rate.
7. the set composite of active testing before and after SCR denitrating catalyst regeneration according to claim 6 and regeneration, it is characterized in that: on the pipeline that described compressed air reservoir is connected with threeway changeover valve, be also provided with pressure-reducing valve and mass flowmenter, for controlling the purging pressure of purge.
8. the set composite of active testing before and after SCR denitrating catalyst regeneration according to claim 7 and regeneration, it is characterized in that: in described circulatory pool, can add deionized water or regenerated liquid, circulating-pump outlet is also provided with mass flowmenter, for controlling to adjust the cleaning flow of cleaning process.
9. the set composite of active testing before and after SCR denitrating catalyst regeneration according to claim 8 and regeneration, is characterized in that: the outer wall of described reacting furnace is also coated with one deck insulating (21).
10. the set composite of active testing before and after SCR denitrating catalyst regeneration according to claim 9 and regeneration, is characterized in that: described circulatory pool is also provided with dosing mouth (15) and floss hole (16), for interpolation and the replacing of solution in pond.
CN201320733299.2U 2013-11-18 2013-11-18 Composite device for testing regeneration of SCR denitration catalyst and activity before and after regeneration Withdrawn - After Issue CN203663847U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201320733299.2U CN203663847U (en) 2013-11-18 2013-11-18 Composite device for testing regeneration of SCR denitration catalyst and activity before and after regeneration

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201320733299.2U CN203663847U (en) 2013-11-18 2013-11-18 Composite device for testing regeneration of SCR denitration catalyst and activity before and after regeneration

Publications (1)

Publication Number Publication Date
CN203663847U true CN203663847U (en) 2014-06-25

Family

ID=50960182

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201320733299.2U Withdrawn - After Issue CN203663847U (en) 2013-11-18 2013-11-18 Composite device for testing regeneration of SCR denitration catalyst and activity before and after regeneration

Country Status (1)

Country Link
CN (1) CN203663847U (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103638991A (en) * 2013-11-18 2014-03-19 广东电网公司电力科学研究院 Composite apparatus for generating SCR denitrification catalyst and testing activity of catalyst before and after regeneration
CN108472644A (en) * 2016-01-22 2018-08-31 康明斯排放处理公司 System and method for remanufacturing selective catalytic reduction system operating

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103638991A (en) * 2013-11-18 2014-03-19 广东电网公司电力科学研究院 Composite apparatus for generating SCR denitrification catalyst and testing activity of catalyst before and after regeneration
CN103638991B (en) * 2013-11-18 2015-06-10 广东电网公司电力科学研究院 Composite apparatus for generating SCR denitrification catalyst and testing activity of catalyst before and after regeneration
CN108472644A (en) * 2016-01-22 2018-08-31 康明斯排放处理公司 System and method for remanufacturing selective catalytic reduction system operating

Similar Documents

Publication Publication Date Title
CN103638991B (en) Composite apparatus for generating SCR denitrification catalyst and testing activity of catalyst before and after regeneration
CN203764106U (en) Flue gas denitrification device implemented by combining SNCR (selective non-catalytic reduction)-ozone oxidation with wet absorption
CN204365100U (en) A kind of regenerative system of desulphurization denitration activated coke
CN205598926U (en) Circulating fluidized bed boiler flue gas SNCR and SCR coupling denitrification facility
CN106382145B (en) A kind of exhaust treatment system and control method based on NTP technology
CN103127963B (en) On-line regeneration system and method of flue gas denitration catalyst
CN203043817U (en) Selective catalytic reduction (SCR) denitration system capable of increasing flue gas temperature by utilizing high-temperature steam
CN201026440Y (en) Absorption, oxidation, concentration combined desulfurizing tower
CN103657367B (en) The desulfurization of a kind of list tower calcium method turns device and the technique of the double-tower type ammonia process of desulfurization
CN203663847U (en) Composite device for testing regeneration of SCR denitration catalyst and activity before and after regeneration
CN205796943U (en) Ozone oxidation double tower ammonia process of desulfurization denitrating system
CN107344788A (en) A kind of desulfurization wastewater treatment system
CN113209823A (en) Low-temperature SCR denitration device and process for waste gas from nonferrous metal Kaldo furnace smelting
CN106557027B (en) The system and method that ozone is run during optimization coking flue gas desulfurization and denitrification
CN204637957U (en) A kind of equipment for denitrifying flue gas
CN204438823U (en) A kind of flue gases of cock oven denitration desulfurization UTILIZATION OF VESIDUAL HEAT IN integrated apparatus
CN207042257U (en) A kind of on-line regeneration facility for low temperature SCR denitration system
CN109381988A (en) A kind of device preventing ammonia process desulfuration tower Crystallization Plugging
CN112370952B (en) Factory-used waste gas desulfurization and denitrification treatment device
CN112717692B (en) Flue gas denitration process for asphalt mixing plant
CN201249101Y (en) Two-stage parallel spray thionizer
CN214681040U (en) Flue gas denitration device for asphalt mixing plant
CN203710904U (en) Transverse semi-drying desulfurization device for tail flue of boiler
CN112705047A (en) Flue gas denitration system of asphalt mixing plant
CN208642269U (en) The denitrification apparatus of the molten gold of wet process and/or Rong Yin workshop section flue gas

Legal Events

Date Code Title Description
C14 Grant of patent or utility model
GR01 Patent grant
AV01 Patent right actively abandoned

Granted publication date: 20140625

Effective date of abandoning: 20150610

RGAV Abandon patent right to avoid regrant