CN107961818A - The renovation process and production equipment of flue gas SCR catalyst - Google Patents

The renovation process and production equipment of flue gas SCR catalyst Download PDF

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Publication number
CN107961818A
CN107961818A CN201711273172.6A CN201711273172A CN107961818A CN 107961818 A CN107961818 A CN 107961818A CN 201711273172 A CN201711273172 A CN 201711273172A CN 107961818 A CN107961818 A CN 107961818A
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China
Prior art keywords
solution
flue gas
scr catalyst
catalyst
regeneration
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CN201711273172.6A
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Chinese (zh)
Inventor
吴敏
秦艳涛
张仲琨
孟徐
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NANJING WEIAN NEW MATERIAL SCIENCE & TECHNOLOGY Co Ltd
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NANJING WEIAN NEW MATERIAL SCIENCE & TECHNOLOGY Co Ltd
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Priority to CN201711273172.6A priority Critical patent/CN107961818A/en
Publication of CN107961818A publication Critical patent/CN107961818A/en
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J38/00Regeneration or reactivation of catalysts, in general
    • B01J38/02Heat treatment
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8621Removing nitrogen compounds
    • B01D53/8625Nitrogen oxides
    • B01D53/8628Processes characterised by a specific catalyst
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/90Injecting reactants
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J38/00Regeneration or reactivation of catalysts, in general
    • B01J38/48Liquid treating or treating in liquid phase, e.g. dissolved or suspended
    • B01J38/485Impregnating or reimpregnating with, or deposition of metal compounds or catalytically active elements
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J38/00Regeneration or reactivation of catalysts, in general
    • B01J38/48Liquid treating or treating in liquid phase, e.g. dissolved or suspended
    • B01J38/50Liquid treating or treating in liquid phase, e.g. dissolved or suspended using organic liquids
    • B01J38/52Liquid treating or treating in liquid phase, e.g. dissolved or suspended using organic liquids oxygen-containing
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Environmental & Geological Engineering (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Thermal Sciences (AREA)
  • Physics & Mathematics (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)

Abstract

The invention belongs to catalyst regeneration techniques field, the more particularly to a kind of renovation process and production equipment of flue gas SCR catalyst, renovation process, comprises the following steps:S1, configuration trishydroxymethylaminomethane weak solution, add tetrabutylammonium hydroxide phosphorus, and solution A is made in heating;S2, to spray solution A on flue gas SCR catalyst, maintain temperature at 70 80 DEG C;S3, configuration phenylacetate weak solution, add double (lemon diethyl phthalate) dipropoxy zirconium chelates, and solution B is made in heating;S4, by flue gas SCR catalyst immerse solution B, ultrasound after, solid is put into Muffle furnace high-temperature roasting;Can rapid regeneration inactivation flue gas SCR catalyst, the flue gas SCR catalyst after regeneration, denitration efficiency is up to more than 90%, and can Reusability, service life length;The regeneration production equipment of flue gas SCR catalyst of the present invention, by set catalyst fix rotation axis so that solution spray uniformly in catalyst plates, can highly efficient regeneration SCR catalyst, use manpower and material resources sparingly, raising production efficiency.

Description

The renovation process and production equipment of flue gas SCR catalyst
Technical field
The invention belongs to catalyst regeneration techniques field, the renovation process of more particularly to a kind of flue gas SCR catalyst and life Produce equipment.
Background technology
SCR catalyst refers to the catalyst applied in SCR denitration system, in SCR reactions, promotes reducing agent selective The material that ground chemically reacts at a certain temperature with the nitrogen oxides in flue gas;Catalyst is the core of SCR technology, Determine the denitration efficiency and economy of SCR system, its construction cost accounts for more than the 20% of Flue Gas Denitrification Engineering cost, runs into Originally more than 30% is accounted for;Using after a certain period of time, denitration efficiency reduces, it is necessary to be regenerated SCR catalyst.
The content of the invention
The present invention solves above-mentioned technical problem existing in the prior art, there is provided a kind of regeneration side of flue gas SCR catalyst Method and production equipment.
To solve the above problems, technical scheme is as follows:
The renovation process of flue gas SCR catalyst, comprises the following steps:
S1,100 parts by weight trishydroxymethylaminomethane weak solutions of configuration, add the tetrabutylammonium hydroxide of 12-16 parts by weight Phosphorus, is heated to 70-80 DEG C, and solution A is made;
S2, to spray solution A on flue gas SCR catalyst, maintain temperature to continue 30-60 minutes at 70-80 DEG C;
S3,100 parts by weight phenylacetate weak solutions of configuration, add double (lemon diethyl phthalate) dipropyl oxygen of 7-10 parts by weight Base zirconium chelate, is heated to 80-90 DEG C, and solution B is made;
S4, will handle obtained flue gas SCR catalyst through step 2 and immerse solution B, when ultrasonic 2-3 is small, remove solution, will Solid is put into Muffle furnace high-temperature roasting.
Preferably, the mass fraction of the trishydroxymethylaminomethane weak solution is 1-2%.
Preferably, the mass fraction of the phenylacetate is 3-5%.
Preferably, the phenylacetate is sodium phenylacetate or phenylacetic acid potassium.
Preferably, the condition of step 4 high-temperature roasting is 420-460 DEG C, when 3-5 is small.
The regeneration production equipment of flue gas SCR catalyst, including regeneration production room, solution A storage room and solution B storage room;
The solution A storage room bottom sets flusher, and the flusher is positioned at the surface of regeneration production room;
The regeneration production room sets two catalyst charge discharge ports, respectively positioned at regeneration production room both sides with respect to position Put;Lid and catalyst is set to fix rotation axis on the catalyst charge discharge port, the catalyst fixes rotation axis from lid Body center opening is stretched into regeneration production room, and one end that rotation axis of the catalyst fixing stretches into regeneration production room is set Geometrical clamp, for fixed catalyst plate, the other end is connected with electric rotating machine;
The solution B storage room is connected by pipeline with regeneration production room, and the entrance is arranged on regeneration production On side wall below the catalyst charge discharge port of room.
Preferably, the regeneration production room bottom sets liquid outlet opening.
Preferably, the regeneration production room bottom sets Vltrasonic device.
Preferably, regeneration production room, solution A storage room and the solution B storage room interior set heater strip.
Relative to the prior art, advantages of the present invention is as follows,
The present invention method can rapid regeneration inactivation flue gas SCR catalyst, the flue gas SCR catalyst after regeneration, denitration It is efficient up to more than 90%, and can Reusability, service life length;The regeneration production equipment of flue gas SCR catalyst of the present invention, leads to Cross setting catalyst fix rotation axis so that solution spray uniformly in catalyst plates, can highly efficient regeneration SCR catalyst, saving Manpower and materials, improve production efficiency.
Brief description of the drawings
Fig. 1 is the regeneration production equipment schematic diagram of flue gas SCR catalyst;
In figure, 1 be regeneration production room, 2 be solution A storage room, 3 be solution B storage room, 4 be flusher, 5 be catalysis Agent charging discharge port, 6 be lid, 7 be catalyst fix rotation axis, 8 be catalyst plates, 9 be electric rotating machine, 10 be pipeline, 11 It is Vltrasonic device, 12 is heater strip, 13 is liquid outlet opening.
Embodiment
Embodiment 1:
The regeneration production equipment of flue gas SCR catalyst, including regeneration production room 1, solution A storage room 2 and solution B storage room 3;
2 bottom of solution A storage room sets flusher 4, the flusher 4 positioned at regeneration production room 1 just on Side;
The regeneration production room 1 sets two catalyst charge discharge ports 5, opposite positioned at regeneration production 1 both sides of room respectively Position;Lid 6 and catalyst is set to fix rotation axis 7 on the catalyst charge discharge port 5, the catalyst fixes rotation axis 7 stretch into regeneration production room 1 from 6 center opening of lid, and rotation axis 7 of the catalyst fixing stretches into regeneration production room 1 One end set geometrical clamp, for fixed catalyst plate 8, the other end is connected with electric rotating machine 9;
The solution B storage room 3 is connected by pipeline 10 with regeneration production room 1, and 10 entrance of pipeline is arranged on again On the side wall of 5 lower section of production 1 catalyst charge discharge port of room.
Preferably, regeneration production 1 bottom of room sets liquid outlet opening 13, easy to remove the unnecessary of step 3 generation Solution B is removed after solution A, and step 4 ultrasound.
Preferably, regeneration production 1 bottom of room sets Vltrasonic device 11.
Preferably, regeneration production room 1, solution A storage room 2 and 3 interior of solution B storage room set heater strip 12。
Embodiment 2:
The renovation process of flue gas SCR catalyst, comprises the following steps:
The trishydroxymethylaminomethane aqueous solution that S1,100 parts by weight mass fractions of configuration are 1-2%, adds 12 parts by weight Tetrabutylammonium hydroxide phosphorus, be heated to 70-80 DEG C, solution A be made;
S2, to spray solution A on flue gas SCR catalyst, maintain temperature to continue 30-60 minutes at 70-80 DEG C;
The phenylacetic acid aqueous solutions of potassium that S3,100 parts by weight mass fractions of configuration are 3-5%, adds double (lemons of 7 parts by weight Diethyl phthalate) dipropoxy zirconium chelate, 80-90 DEG C is heated to, solution B is made;
S4, will handle obtained flue gas SCR catalyst through step 2 and immerse solution B, when ultrasonic 2-3 is small, remove solution, will Solid is put into Muffle furnace high-temperature roasting, and temperature setting is 420 DEG C, when the time 3 is small, after cooling, completes regeneration.
Embodiment 3:
The renovation process of flue gas SCR catalyst, comprises the following steps:
The trishydroxymethylaminomethane aqueous solution that S1,100 parts by weight mass fractions of configuration are 1-2%, adds 16 parts by weight Tetrabutylammonium hydroxide phosphorus, be heated to 70-80 DEG C, solution A be made;
S2, to spray solution A on flue gas SCR catalyst, maintain temperature to continue 30-60 minutes at 70-80 DEG C;
The sodium phenylacetate aqueous solution that S3,100 parts by weight mass fractions of configuration are 3-5%, adds double (lemons of 10 parts by weight Diethyl phthalate) dipropoxy zirconium chelate, 80-90 DEG C is heated to, solution B is made;
S4, will handle obtained flue gas SCR catalyst through step 2 and immerse solution B, when ultrasonic 2-3 is small, remove solution, will Solid is put into Muffle furnace high-temperature roasting, and temperature setting is 460 DEG C, when the time 5 is small, after cooling, completes regeneration.
Embodiment 4:
The renovation process of flue gas SCR catalyst, comprises the following steps:
The trishydroxymethylaminomethane aqueous solution that S1,100 parts by weight mass fractions of configuration are 1-2%, adds 14 parts by weight Tetrabutylammonium hydroxide phosphorus, be heated to 70-80 DEG C, solution A be made;
S2, to spray solution A on flue gas SCR catalyst, maintain temperature to continue 30-60 minutes at 70-80 DEG C;
The phenylacetic acid aqueous solutions of potassium that S3,100 parts by weight mass fractions of configuration are 3-5%, adds double (lemons of 8 parts by weight Diethyl phthalate) dipropoxy zirconium chelate, 80-90 DEG C is heated to, solution B is made;
S4, will handle obtained flue gas SCR catalyst through step 2 and immerse solution B, when ultrasonic 2-3 is small, remove solution, will Solid is put into Muffle furnace high-temperature roasting, and temperature setting is 440 DEG C, when the time 4 is small, after cooling, completes regeneration.
Embodiment 5:
The renovation process of flue gas SCR catalyst, with embodiment 4, difference is, changes adding for tetrabutylammonium hydroxide phosphorus Enter amount:
A groups:10 parts by weight;
B groups:16 parts by weight.
Embodiment 6:
The renovation process of flue gas SCR catalyst, with embodiment 4, difference is, changes double (lemon diethyl phthalates) two The addition of propoxyl group zirconium chelate:
A groups:4 parts by weight;
B groups:13 parts by weight.
Embodiment 7:
The renovation process of flue gas SCR catalyst, with embodiment 4, difference is, changes the step 4 calcination temperature:
A groups:380℃;
B groups:500℃.
Embodiment 8:
Denitrating flue gas tower will be used for by the regenerated catalyst of the method for embodiment 2-7, denitration efficiency is as shown in the table:
Regenerate SCR catalyst group Denitration efficiency %
SCR catalyst (raw material that each embodiment uses) before regeneration 61.3
Embodiment 2 89.1
Embodiment 3 87.6
Embodiment 4 92.1
Embodiment 5-A groups 72.4
Embodiment 5-B groups 76.5
Embodiment 6-A groups 75.1
Embodiment 6-B groups 64.5
Embodiment 7-A groups 42.3
Embodiment 7-B groups 77.3
It should be noted that above-described embodiment is only presently preferred embodiments of the present invention, it is not used for limiting the present invention's Protection domain, the equivalent substitution or replacement made on the basis of the above belong to protection scope of the present invention.

Claims (9)

1. the renovation process of flue gas SCR catalyst, it is characterised in that comprise the following steps:
S1,100 parts by weight trishydroxymethylaminomethane weak solutions of configuration, add the tetrabutylammonium hydroxide phosphorus of 12-16 parts by weight, add Solution A is made to 70-80 DEG C in heat;
S2, to spray solution A on flue gas SCR catalyst, maintain temperature to continue 30-60 minutes at 70-80 DEG C;
S3,100 parts by weight phenylacetate weak solutions of configuration, add double (lemon diethyl phthalate) dipropoxy zirconiums of 7-10 parts by weight Chelate, is heated to 80-90 DEG C, and solution B is made;
S4, will handle obtained flue gas SCR catalyst through step 2 and immerse solution B, when ultrasonic 2-3 is small, solution be removed, by solid It is put into Muffle furnace high-temperature roasting.
2. the renovation process of flue gas SCR catalyst as claimed in claim 1, it is characterised in that the trihydroxy methyl amino first The mass fraction of alkane weak solution is 1-2%.
3. the renovation process of flue gas SCR catalyst as claimed in claim 1, it is characterised in that the quality of the phenylacetate Fraction is 3-5%.
4. the renovation process of flue gas SCR catalyst as claimed in claim 1, it is characterised in that the phenylacetate is benzene second Sour sodium or phenylacetic acid potassium.
5. the renovation process of flue gas SCR catalyst as claimed in claim 1, it is characterised in that the condition of step 4 high-temperature roasting For 420-460 DEG C, when 3-5 is small.
6. the regeneration production equipment of the flue gas SCR catalyst as described in claim 1-5, it is characterised in that produced including regeneration Room, solution A storage room and solution B storage room;
The solution A storage room bottom sets flusher, and the flusher is positioned at the surface of regeneration production room;
The regeneration production room sets two catalyst charge discharge ports, respectively positioned at regeneration production room both sides relative position;Institute State and set lid and catalyst to fix rotation axis on catalyst charge discharge port, the catalyst fixes rotation axis from lid center Position opening stretches into regeneration and produces in room, and one end that rotation axis of the catalyst fixing stretches into regeneration production room sets fixation Folder, for fixed catalyst plate, the other end is connected with electric rotating machine;
The solution B storage room is connected by pipeline with regeneration production room, and the entrance is arranged on regeneration production room and urges On side wall below agent charging discharge port.
7. regeneration production equipment as claimed in claim 6, it is characterised in that the regeneration production room bottom sets liquid to discharge Mouthful.
8. regeneration production equipment as claimed in claim 6, it is characterised in that the regeneration production room bottom sets ultrasound dress Put.
9. regeneration production equipment as claimed in claim 6, it is characterised in that the regeneration production room, solution A storage room and molten Liquid B storage rooms interior sets heater strip.
CN201711273172.6A 2017-12-06 2017-12-06 The renovation process and production equipment of flue gas SCR catalyst Pending CN107961818A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114314928A (en) * 2022-01-04 2022-04-12 湖南烯富环保科技有限公司 Integrated production line and method for removing chloride ions and regenerating dechlorination agent from dechlorination slag

Citations (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101314127A (en) * 2007-05-31 2008-12-03 中国科学院大连化学物理研究所 Oxide catalyst for selective reduction of nitrogen oxide, preparation and uses thereof
CN103736527A (en) * 2014-01-12 2014-04-23 高同柱 Manufacturing method and process device of reactivated cleaning agent for regeneration of honeycomb SCR (selective catalytic reduction) denitration catalyst
CN104209123A (en) * 2014-08-11 2014-12-17 中国海洋石油总公司 Light alkane dehydrogenation catalyst containing silver and boron and preparation method thereof
WO2015044038A1 (en) * 2013-09-25 2015-04-02 Caterpillar Sarl Engine exhaust gas purifier
CN104888869A (en) * 2015-06-12 2015-09-09 河南博苑新未来环保科技有限公司 Waste flue gas denitration catalyst regeneration method and equipment
CN104923316A (en) * 2015-05-13 2015-09-23 湖北大清科技有限公司 Regeneration method and equipment of selective catalytic reduction (SCR) denitration catalyst
CN105381716A (en) * 2015-09-11 2016-03-09 福建紫荆环境工程技术有限公司 Deactivated SCR denitration catalyst purging device, activation device and regeneration system and corresponding methods
CN105797789A (en) * 2016-03-22 2016-07-27 浙江海亮环境材料有限公司 Regeneration method of denitration catalyst
CN105983340A (en) * 2015-03-05 2016-10-05 中石化洛阳工程有限公司 Regeneration method for low-temperature SCR denitration catalyst
CN206103713U (en) * 2016-08-29 2017-04-19 河北唯沃环境工程科技有限公司 Supporting quick catalyst regeneration device of SCR denitration
CN106622397A (en) * 2017-02-16 2017-05-10 宁波诺威尔大气污染控制科技有限公司 Automatic regeneration device for SCR (Selective Catalytic Reduction) denitration catalyst module and regeneration process thereof
CN106694467A (en) * 2017-01-09 2017-05-24 安徽元琛环保科技股份有限公司 Cleaning device and method and regeneration method for waste denitration catalyst
CN107413394A (en) * 2016-05-24 2017-12-01 北京清树科技发展有限公司 A kind of renovation process for the SCR denitration that fails
CN107952427A (en) * 2017-12-06 2018-04-24 南京威安新材料科技有限公司 The production method and production equipment of SCR catalyst

Patent Citations (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101314127A (en) * 2007-05-31 2008-12-03 中国科学院大连化学物理研究所 Oxide catalyst for selective reduction of nitrogen oxide, preparation and uses thereof
WO2015044038A1 (en) * 2013-09-25 2015-04-02 Caterpillar Sarl Engine exhaust gas purifier
CN103736527A (en) * 2014-01-12 2014-04-23 高同柱 Manufacturing method and process device of reactivated cleaning agent for regeneration of honeycomb SCR (selective catalytic reduction) denitration catalyst
CN104209123A (en) * 2014-08-11 2014-12-17 中国海洋石油总公司 Light alkane dehydrogenation catalyst containing silver and boron and preparation method thereof
CN105983340A (en) * 2015-03-05 2016-10-05 中石化洛阳工程有限公司 Regeneration method for low-temperature SCR denitration catalyst
CN104923316A (en) * 2015-05-13 2015-09-23 湖北大清科技有限公司 Regeneration method and equipment of selective catalytic reduction (SCR) denitration catalyst
CN104888869A (en) * 2015-06-12 2015-09-09 河南博苑新未来环保科技有限公司 Waste flue gas denitration catalyst regeneration method and equipment
CN105381716A (en) * 2015-09-11 2016-03-09 福建紫荆环境工程技术有限公司 Deactivated SCR denitration catalyst purging device, activation device and regeneration system and corresponding methods
CN105797789A (en) * 2016-03-22 2016-07-27 浙江海亮环境材料有限公司 Regeneration method of denitration catalyst
CN107413394A (en) * 2016-05-24 2017-12-01 北京清树科技发展有限公司 A kind of renovation process for the SCR denitration that fails
CN206103713U (en) * 2016-08-29 2017-04-19 河北唯沃环境工程科技有限公司 Supporting quick catalyst regeneration device of SCR denitration
CN106694467A (en) * 2017-01-09 2017-05-24 安徽元琛环保科技股份有限公司 Cleaning device and method and regeneration method for waste denitration catalyst
CN106622397A (en) * 2017-02-16 2017-05-10 宁波诺威尔大气污染控制科技有限公司 Automatic regeneration device for SCR (Selective Catalytic Reduction) denitration catalyst module and regeneration process thereof
CN107952427A (en) * 2017-12-06 2018-04-24 南京威安新材料科技有限公司 The production method and production equipment of SCR catalyst

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
陈昆柏: "《火电厂废烟气脱硝催化剂处理与处置》", 30 June 2017, 河南科学技术出版社 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114314928A (en) * 2022-01-04 2022-04-12 湖南烯富环保科技有限公司 Integrated production line and method for removing chloride ions and regenerating dechlorination agent from dechlorination slag
CN114314928B (en) * 2022-01-04 2023-09-08 湖南烯富环保科技有限公司 Integrated production line and method for chloride ion removal and chlorine removal slag regeneration chlorine removal agent

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