CN104492421B - Dearsenification method for tungsten, vanadium and arsenic-containing catalyst - Google Patents

Dearsenification method for tungsten, vanadium and arsenic-containing catalyst Download PDF

Info

Publication number
CN104492421B
CN104492421B CN201410731940.8A CN201410731940A CN104492421B CN 104492421 B CN104492421 B CN 104492421B CN 201410731940 A CN201410731940 A CN 201410731940A CN 104492421 B CN104492421 B CN 104492421B
Authority
CN
China
Prior art keywords
catalyst
dearsenization
vanadium
reaction
arsenic
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.)
Active
Application number
CN201410731940.8A
Other languages
Chinese (zh)
Other versions
CN104492421A (en
Inventor
谢刚
徐庆鑫
和晓才
李怀仁
魏可
徐亚飞
李永刚
崔涛
袁野
徐俊毅
姚云
柯浪
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.)
Kunming Metallurgical Research Institute
Original Assignee
Kunming Metallurgical Research Institute
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 Kunming Metallurgical Research Institute filed Critical Kunming Metallurgical Research Institute
Priority to CN201410731940.8A priority Critical patent/CN104492421B/en
Publication of CN104492421A publication Critical patent/CN104492421A/en
Application granted granted Critical
Publication of CN104492421B publication Critical patent/CN104492421B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Catalysts (AREA)

Abstract

The invention discloses a dearsenification method for a tungsten, vanadium and arsenic-containing catalyst. The method can be used for effectively removing arsenide in the catalyst and further reducing loss of tungsten and vanadium, so that the As2O3 content is less than 0.15%, the dearsenification rate can reach 95% and the WO3 and V2O5 loss rate are less than 30%. The method is simple in process and reliable and feasible. By adopting a method of alkaline leaching to dearsenificate in ultrasonic waves, the arsenide removal rate in the catalyst is relatively high, and an inhibiting agent is added, so that the loss of tungsten and vanadium can be effectively controlled. The wastewater generated in the process can be treated by Ca(OH)2 and is reused in the system. The technical process is a closed system which can be used for realizing cyclic utilization, is free of environmental pollution and further can be used for lowering the cost.

Description

A kind of tungstenic, vanadium, the method for arsenic catalyst dearsenization
Technical field
The present invention relates to catalyst dearsenic technique field, especially a kind of tungstenic, vanadium, the method for arsenic catalyst dearsenization.
Background technology
Nitrogen oxides (nox) are one of Air Pollutants that countries in the world are generally acknowledged.Thermal power plant is China's nitrogen oxides Topmost emission source.In order to control the discharge of nox, many thermal power plants, the generating set of combustion of fossil fuels adopt technology relatively For ripe SCR (scr) gas denitrifying technology, its core is the catalyst being made up of tungsten, vanadium, titanium etc., The life-span of general coal-burning power plant catalyst is 3 ~ 5 years, however, due to containing micro arsenic, gas in high-temperature flue gas in coal-burning boiler State as2o3, it is easily accessible the hole of catalyst, react the stable arsenic acid vfanadium compound of generation with the vanadium in catalyst, vanadium loses work Property, meanwhile, gaseous state arsenic easy blocking catalyst micropore, stop reactant from reaching active sites, also affect the activity of catalyst.Thus dropping The low service life of catalyst.
How to remove tungstenic, vanadium, arsenide in arsenic catalyst, effective control tungsten, vanadium loss, extend catalyst and use simultaneously In the life-span, be problem demanding prompt solution.The arsenic removing method of report includes pyrogenic process and two kinds of wet method at present.Fire arsenic removal effect is poor, And serious secondary pollution can be caused, and very high to equipment requirements, also do not meet the high temperature of large-scale production at present both at home and abroad Stove.Wet method dearsenication document report is more, how to soak dearsenization using alkali, that is, be directly added into sodium hydroxide concentrated alkali solution and leach dearsenization, but For indissoluble arsenate in catalyst, dearsenization effect is less desirable, and tungsten, vanadium together can lose with the removing of arsenic.Therefore, It is necessary to explore one kind and can remove tungstenic, vanadium, arsenide in arsenic catalyst, tungsten, the method for vanadium loss can be controlled simultaneously again.
Content of the invention
Present invention aims to above-mentioned the deficiencies in the prior art, contain arsenic in particular for catalyst and lead Cause problem that its activity reduces it is proposed that a kind of tungstenic, vanadium, the method for arsenic catalyst dearsenization, this method can not only meet efficiently, Safe and environment-friendly dearsenization requirement moreover it is possible to effective control catalyst key component tungsten, the loss of vanadium, thus extending making of catalyst With the life-span, reduce Financial cost.This method of the present invention is stripped of the arsenide in catalyst effectively, can reduce simultaneously again Tungsten, vanadium loss are so that as2o3Content < 0.15%, separating by extraction is up to 95%, and wo therein3、v2o5The equal < of loss rate 30%.
The present invention is achieved through the following technical solutions: a kind of tungstenic, vanadium, the method for arsenic catalyst dearsenization, and step is as follows:
(1), by tungstenic, vanadium, arsenic catalyst, the sodium hydroxide solution being 3~12g/l with concentration, it is placed in ultrasound reactor In carry out the leaching dearsenization reaction of alkali, 30~80 DEG C of controlling reaction temperature, response time 0.5~3h, ventilation 0.8~2.0m3/ H, ultrasonic power 300~900w;In course of reaction, add inhibitor edta and the ammonium hydrogen carbonate of 3~5g/l, after reaction terminates Carry out solid-liquor separation, the catalyst of solid phase is treated to process further;Liquid phase is through ca (oh)2After dearsenization is processed, resulting solution returns one In secondary alkali leaching operation, it is back to whole system, and gained solid phase is cawo4, ca(vo3)2、ca3(aso4)2Directly bank up;
(2) the catalyst that (1) step obtains is carried out secondary alkali leaching, during fill into the sodium hydroxide solution and 1 of 1~3g/l The inhibitor edta of~3g/l and ammonium hydrogen carbonate, are carried out equally in ultrasound reactor, 30~80 DEG C of controlling reaction temperature, instead 0.5~3h, ventilation 0.8~2.0m between seasonable3/ h, ultrasonic power 300~900w;After reaction terminates, the liquid phase obtaining is returned Return in an alkali leaching operation, for the leaching of raw catelyst;The catalyst obtaining carries out next step carrying out washing treatment;
By step (2) in soak the catalyst after dearsenization is processed through secondary alkali and be placed in ultrasound reactor and washed, 25~70 DEG C of controlling reaction temperature, response time 0.5~1.5h, ventilation 0.8~2.0m3/ h, ultrasonic power 100~ 600w;After reaction terminates, resulting solution returns in secondary alkali leaching operation, and gained catalyst dried, after the dearsenization of acquisition As in catalyst2o3Content < 0.15%, separating by extraction is up to 95%, and wo therein3、v2o5The equal < of loss rate 30%.
As the preferred technical solution of the present invention:
In described ultrasound reactor, alkali leaching reaction temperature is 50~70 DEG C, response time 1~2h, ventilation 1.2m3/ H, ultrasonic power 500~700w.
Described ultrasonic wave water washing, temperature is 25~35 DEG C, response time 0.5~1h, ventilation 1.2~1.5m3/ h, ultrasonic Wave power 300~500w.
The invention has the benefit that this procedure is simple, reliable easy, alkali is adopted to soak dearsenization in ultrasound wave Method, in catalyst, arsenide removal efficiency is higher, and add inhibitor, can effective control tungsten, the loss of vanadium, during produce Waste water, can be through ca (oh)2After process, it is back to system, technical process does not pollute ring for closed system it is achieved that recycling Border, reduces cost again.
Brief description:
Fig. 1 is the process chart of the present invention.
Specific embodiment
As in embodiment 1, catalyst containing arsenic2o3Content is 3~4%.First by tungstenic, vanadium, arsenic catalyst, with concentration it is The sodium hydroxide solution of 3g/l, is placed in ultrasound reactor and carries out alkali leaching dearsenization reaction, 30~40 DEG C of controlling reaction temperature, instead 2h, ventilation 1.2m between seasonable3/ h, ultrasonic power 500w.In course of reaction, the inhibitor edta of addition and ammonium hydrogen carbonate are equal For 3g/l.Reaction carries out solid-liquor separation after terminating, and liquid phase is through ca (oh)2After dearsenization is processed, resulting solution can be back to whole body System, and gained slag is cawo4, ca(vo3)2、ca3(aso4)2Can directly bank up.
Catalyst after the leaching of alkali carries out secondary alkali leaching, during fill into sodium hydroxide solution and the suppression of 1g/l Edta the and 1g/l ammonium hydrogen carbonate of agent 1g/l, is carried out equally in ultrasound reactor, 30~40 DEG C of controlling reaction temperature, reaction Time 2h, ventilation 1.2m3/ h, ultrasonic power 500w.After reaction terminates, liquid phase can return to, in an alkali leaching operation, use Leaching in raw catelyst.The catalyst obtaining carries out next step washing again.
Again the catalyst after the leaching dearsenization of secondary alkali is processed is placed in ultrasound reactor and is washed, control reaction 25~35 DEG C of temperature, response time 0.5h, ventilation 1.2m3/ h, ultrasonic power 300w.After reaction terminates, solution returns body System, catalyst dried, as in the dearsenization rear catalyst of acquisition2o3Content is 0.12%, and separating by extraction reaches 95.2%, wo3Loss Rate is 28%, v2o5Loss rate is 22.5%.
As in embodiment 2, catalyst containing arsenic2o3Content is 3~4%.First by tungstenic, vanadium, arsenic catalyst, with concentration it is The sodium hydroxide solution of 5g/l, is placed in ultrasound reactor and carries out alkali leaching dearsenization reaction, 50~60 DEG C of controlling reaction temperature, instead 1.5h, ventilation 1.2m between seasonable3/ h, ultrasonic power 500w.In course of reaction, add inhibitor edta3g/l, bicarbonate Ammonium 4g/l.Reaction carries out solid-liquor separation after terminating, and liquid phase is through ca (oh)2After dearsenization is processed, resulting solution can be back to whole body System, and gained slag is cawo4, ca(vo3)2、ca3(aso4)2Can directly bank up.
Catalyst after the leaching of alkali carries out secondary alkali leaching, during fill into sodium hydroxide solution and the suppression of 2g/l Edta the and 1g/l ammonium hydrogen carbonate of agent 1g/l, is carried out equally in ultrasound reactor, 50~60 DEG C of controlling reaction temperature, reaction Time 1.5h, ventilation 1.2m3/ h, ultrasonic power 500w.After reaction terminates, liquid phase can return in an alkali leaching operation, Leaching for raw catelyst.The catalyst obtaining carries out next step washing again.
Again the catalyst after the leaching dearsenization of secondary alkali is processed is placed in ultrasound reactor and is washed, control reaction 25~35 DEG C of temperature, response time 0.5h, ventilation 1.2m3/ h, ultrasonic power 300w.After reaction terminates, solution returns body System, catalyst dried, as in the dearsenization rear catalyst of acquisition2o3Content is 0.10%, and separating by extraction reaches 95.6%, wo3Loss Rate is 27.4%, v2o5Loss rate is 23.6%.
As in embodiment 3, catalyst containing arsenic2o3Content is 3~4%.First by tungstenic, vanadium, arsenic catalyst, with concentration it is The sodium hydroxide solution of 7g/l, is placed in ultrasound reactor and carries out alkali leaching dearsenization reaction, 60~70 DEG C of controlling reaction temperature, instead 1.0h, ventilation 1.2m between seasonable3/ h, ultrasonic power 700w.In course of reaction, add inhibitor edta4g/l, bicarbonate Ammonium 4g/l.Reaction carries out solid-liquor separation after terminating, and liquid phase is through ca (oh)2After dearsenization is processed, resulting solution can be back to whole body System, and gained slag is cawo4, ca(vo3)2、ca3(aso4)2Can directly bank up.
Catalyst after the leaching of alkali carries out secondary alkali leaching, during fill into sodium hydroxide solution and the suppression of 2g/l Edta the and 2g/l ammonium hydrogen carbonate of agent 2g/l, is carried out equally in ultrasound reactor, 60~70 DEG C of controlling reaction temperature, reaction Time 1.0h, ventilation 1.2m3/ h, ultrasonic power 700w.After reaction terminates, liquid phase can return in an alkali leaching operation, Leaching for raw catelyst.The catalyst obtaining carries out next step washing again.
Again the catalyst after the leaching dearsenization of secondary alkali is processed is placed in ultrasound reactor and is washed, control reaction 25~35 DEG C of temperature, response time 0.5h, ventilation 1.2m3/ h, ultrasonic power 500w.After reaction terminates, solution returns body System, catalyst dried, as in the dearsenization rear catalyst of acquisition2o3Content is 0.11%, and separating by extraction reaches 95.3%, wo3Loss Rate is 26.5%, v2o5Loss rate is 22.8%.
As in embodiment 4, catalyst containing arsenic2o3Content is 3~4%.First by tungstenic, vanadium, arsenic catalyst, with concentration it is The sodium hydroxide solution of 10g/l, is placed in ultrasound reactor and carries out alkali leaching dearsenization reaction, 60~70 DEG C of controlling reaction temperature, Response time 1.0h, ventilation 1.2m3/ h, ultrasonic power 700w.In course of reaction, add inhibitor edta3g/l, carbonic acid Hydrogen ammonium 5g/l.Reaction carries out solid-liquor separation after terminating, and liquid phase is through ca (oh)2After dearsenization is processed, resulting solution can be back to entirely System, and gained slag is cawo4, ca(vo3)2、ca3(aso4)2Can directly bank up.
Catalyst after the leaching of alkali carries out secondary alkali leaching, during fill into sodium hydroxide solution and the suppression of 3g/l Edta the and 3g/l ammonium hydrogen carbonate of agent 1g/l, is carried out equally in ultrasound reactor, 60~70 DEG C of controlling reaction temperature, reaction Time 1.0h, ventilation 1.2m3/ h, ultrasonic power 700w.After reaction terminates, liquid phase can return in an alkali leaching operation, Leaching for raw catelyst.The catalyst obtaining carries out next step washing again.
Again the catalyst after the leaching dearsenization of secondary alkali is processed is placed in ultrasound reactor and is washed, control reaction 50~60 DEG C of temperature, response time 1.0h, ventilation 1.8m3/ h, ultrasonic power 600w.After reaction terminates, solution returns body System, catalyst dried, as in the dearsenization rear catalyst of acquisition2o3Content is 0.10%, and separating by extraction reaches 95.6%, wo3Loss Rate is 27.3%, v2o5Loss rate is 25.2%.

Claims (3)

1. a kind of tungstenic, vanadium, the method for arsenic catalyst dearsenization are it is characterised in that step is as follows:
(1), by tungstenic, vanadium, arsenic catalyst, the sodium hydroxide solution being 3~12g/l with concentration, it is placed in ultrasound reactor Alkali leaching dearsenization reaction of row, 30~80 DEG C of controlling reaction temperature, response time 0.5~3h, ventilation 0.8~2.0m3/ h, surpasses Acoustic power 300~900w;In course of reaction, add the inhibitor edta of 3~5g/l and the ammonium hydrogen carbonate of 3~5g/l, reaction Carry out solid-liquor separation, the catalyst of solid phase is treated to process further, liquid phase is through ca (oh) after end2After dearsenization is processed, resulting solution It is back to an alkali leaching operation, gained solid phase is cawo4, ca(vo3)2、ca3(aso4)2Directly bank up;
(2), the catalyst that (1) step obtains is carried out secondary alkali leaching, during fill into the sodium hydroxide solution of 1~3g/l and 1~ The inhibitor edta of 3g/l and the ammonium hydrogen carbonate of 1~3g/l, are carried out equally in ultrasound reactor, and controlling reaction temperature 30~ 80 DEG C, response time 0.5~3h, ventilation 0.8~2.0m3/ h, ultrasonic power 300~900w;After reaction terminates, obtain Liquid phase returns in an alkali leaching operation, for the leaching of raw catelyst;The catalyst obtaining carries out next step carrying out washing treatment;
(3), by step (2) in soak the catalyst after dearsenization is processed through secondary alkali and be placed in ultrasound reactor and washed, control 25~70 DEG C of reaction temperature processed, response time 0.5~1.5h, ventilation 0.8~2.0m3/ h, ultrasonic power 100~600w; After reaction terminates, resulting solution returns in secondary alkali leaching operation, gained catalyst dried, the dearsenization rear catalyst of acquisition Middle as2o3Content < 0.15%, separating by extraction reaches more than 95%, wo3、v2o5The equal < of loss rate 30%.
2. tungstenic according to claim 1, vanadium, arsenic catalyst dearsenization method it is characterised in that: described ultrasonic response In device, alkali leaching reaction temperature is 50~70 DEG C, response time 1~2h, ventilation 1.2m3/ h, ultrasonic power 500~700w.
3. tungstenic according to claim 1, vanadium, arsenic catalyst dearsenization method it is characterised in that: described ultrasound wave water Wash, temperature is 25~35 DEG C, response time 0.5~1h, ventilation 1.2~1.5m3/ h, ultrasonic power 300~500w.
CN201410731940.8A 2014-12-06 2014-12-06 Dearsenification method for tungsten, vanadium and arsenic-containing catalyst Active CN104492421B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410731940.8A CN104492421B (en) 2014-12-06 2014-12-06 Dearsenification method for tungsten, vanadium and arsenic-containing catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410731940.8A CN104492421B (en) 2014-12-06 2014-12-06 Dearsenification method for tungsten, vanadium and arsenic-containing catalyst

Publications (2)

Publication Number Publication Date
CN104492421A CN104492421A (en) 2015-04-08
CN104492421B true CN104492421B (en) 2017-01-25

Family

ID=52933923

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410731940.8A Active CN104492421B (en) 2014-12-06 2014-12-06 Dearsenification method for tungsten, vanadium and arsenic-containing catalyst

Country Status (1)

Country Link
CN (1) CN104492421B (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105668897A (en) * 2016-03-18 2016-06-15 昆明冶金研究院 Method for dearsenization of arsenic containing waste water generated in regeneration process of vanadium, tungsten and titanium denitration catalyst

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AU2002359585A1 (en) * 2001-12-06 2003-06-23 Kazem Eradat Oskoui Method of extracting contaminants from solid matter
CN100532591C (en) * 2007-02-15 2009-08-26 郴州市金贵有色金属有限公司 Method of removing arsenic for anode mud with high arsenic and lead content
CN101194683B (en) * 2008-01-09 2010-09-29 北京市科威华食品工程技术有限公司 Novel arsenic removing technique for sargassum fusiforme

Also Published As

Publication number Publication date
CN104492421A (en) 2015-04-08

Similar Documents

Publication Publication Date Title
CN102423688B (en) Preparation method for walnut shell active carbon adsorbent for purifying low concentration phosphine
CN103157358B (en) Flue gas denitration method based on advanced oxidization technology
CN105056882A (en) Preparation method of modified charcoal-based adsorbent for removing hydrogen sulfide
CN105709863B (en) A kind of SCR regenerating flue gas denitrifying catalyst liquid and preparation method thereof
CN101406803A (en) Ultrasonic wave denitration method for flue gas
CN105080622A (en) Regeneration method for inactivated selective catalytic reduction (SCR) denitration catalyst
CN105709861A (en) Regeneration method of SCR denitration catalyst
CN102794097A (en) Flue gas wet-type reduction integrated desulfurization and denitration and harmless processing and resource utilization method
CN102764573A (en) Streamer corona plasma flue gas denitrification method
CN105668897A (en) Method for dearsenization of arsenic containing waste water generated in regeneration process of vanadium, tungsten and titanium denitration catalyst
CN102949930A (en) Method for NO oxidation and nitrogen oxide removal at room temperature through synergism of plasma and catalyst
CN103433081B (en) Regeneration method for honeycomb type SCR (Selective Catalytic Reduction) denitration catalyst
CN105289228A (en) Synergistic desulfurization and denitrification method of industrial flue gas
CN106000100A (en) Method for regenerating ineffective SCR catalyst under negative pressure condition
CN105126608A (en) Method for treating nitrogen oxides
CN104492421B (en) Dearsenification method for tungsten, vanadium and arsenic-containing catalyst
CN101972599A (en) Calcium-based CO2 absorbing and regenerating device
CN114146549A (en) System device and method for desulfurization, denitrification and decarburization of flue gas by ammonia process
CN102989302A (en) Smoke wet oxidation denitration method
CN104857998B (en) Efficient regenerating method for As-poisoned denitration catalyst
CN212369892U (en) System for incinerating byproduct hydrochloric acid in flue gas desulfurization and denitrification
CN205115054U (en) Utilize nitrogen oxide water to absorb equipment of rare nitric acid of preparation
CN105664700B (en) A kind of processing method and processing unit of nitrogen-containing oxide industrial waste gas
CN104108780B (en) Method of wastewater treatment in acrylonitrile process subtractive process
CN107096578B (en) Regeneration method of arsenic poisoning SCR denitration catalyst

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CP01 Change in the name or title of a patent holder

Address after: 650031 No. 86 Yuantong North Road, Yunnan, Kunming

Patentee after: Kunming Metallurgical Research Institute Co.,Ltd.

Address before: 650031 No. 86 Yuantong North Road, Yunnan, Kunming

Patentee before: KUNMING METALLURGICAL Research Institute

CP01 Change in the name or title of a patent holder