CN103785263B - A kind of method that ammonia vent gas treatment reclaims - Google Patents

A kind of method that ammonia vent gas treatment reclaims Download PDF

Info

Publication number
CN103785263B
CN103785263B CN201410050253.XA CN201410050253A CN103785263B CN 103785263 B CN103785263 B CN 103785263B CN 201410050253 A CN201410050253 A CN 201410050253A CN 103785263 B CN103785263 B CN 103785263B
Authority
CN
China
Prior art keywords
ammonia
dust
spray
tail gas
containing exhaust
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.)
Expired - Fee Related
Application number
CN201410050253.XA
Other languages
Chinese (zh)
Other versions
CN103785263A (en
Inventor
李军
田磊
赵会团
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.)
GANZHOU HUAMAO TUNGSTEN MATERIAL Co Ltd
Original Assignee
GANZHOU HUAMAO TUNGSTEN MATERIAL 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 GANZHOU HUAMAO TUNGSTEN MATERIAL Co Ltd filed Critical GANZHOU HUAMAO TUNGSTEN MATERIAL Co Ltd
Priority to CN201410050253.XA priority Critical patent/CN103785263B/en
Publication of CN103785263A publication Critical patent/CN103785263A/en
Application granted granted Critical
Publication of CN103785263B publication Critical patent/CN103785263B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

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

Landscapes

  • Treating Waste Gases (AREA)

Abstract

The present invention relates to ammonium paratungstate in tungsten powder smelting industry and calcine the ammonia tail gas disposal technique produced, in particular, relate to by the recovery realizing tungsten oxide dust and ammonia with the method for sour spray-absorption of gathering dust in ammonia vent gas treatment process, tail gas qualified discharge after process.The present invention includes (1) to gather dust, (2) Water spray gathers dust, (3) condensation, (4) acid absorbs, (5) evaporative crystallization steps, the ammonia-containing exhaust of variable concentrations can be processed, also can process the ammonia-containing exhaust containing other combustible, after treatment, the tungsten oxide dust in tail gas can all reclaim the ammonia tail gas that converter produces, ammonia all can be converted into sulfate of ammoniac (or ammonium chloride, ammonium nitrate) crystal, no longer produces the problem of ammonia pollution and secondary environmental pollution.

Description

A kind of method that ammonia vent gas treatment reclaims
Technical field
The present invention relates to ammonium paratungstate in tungsten powder smelting industry and calcine the ammonia tail gas disposal technique produced, in particular, relate to by the recovery realizing tungsten oxide dust and ammonia with the method for sour spray-absorption of gathering dust in ammonia vent gas treatment process, tail gas qualified discharge after process.
Background technology
At home in tungsten powder smelt production, use converter calcining ammonium paratungstate to produce obtained tungsten oxide product, containing the ammonia of 5% in ammonium paratungstate, when calcining and decomposing, produce tail gas, containing NH in tail gas 3, H 2o, O 2, N 2with tungsten oxide dust, ammonia is colourless, the alkaline irritative gas of high water soluble, and after discharge, stench is pungent, trees withered or died, the respiratory system of infringement people and skin, it is atmosphere pollution not only, and can body eutrophication be made after formation rainwater, polluted source, cause Heavy environmental pollution.At present, in process converter calcining ammonium paratungstate generation ammonia tail gas, some enterprises adopt Water spray method process ammonia, this method can not absorb ammonia completely, effectively can not reclaim the tungsten powder dirt in converter calcination process, absorbing liquid enters waste water, causes the ammonia-nitrogen content in industrial wastewater to exceed standard, creates new secondary pollution.Along with the progress for the treatment of tail gas technology, the new technologies such as biological filtering tower combined working technology and incineration technology have been had now to the process of ammonia tail gas, biological filtering tower combined working technology is mainly used in the NH_3-N treating in waste water, and incineration technology also only adapts to process containing the high petrochemical industry of ammonia density, and need consume fuel gas to provide combustion heat energy for it, and with CO 2deng the discharge of tail gas.
Chinese patent " ammonia-containing tail gas treating furnace " (patent No. 2009101153431), discloses one and ammonia is placed in high temperature, catalyst, has H 2when O, make the equipment of its catalytic decomposition, its reactive group present principles is:
2NH 3=N 2﹢3H 2
2H 2﹢ O 2=2H 2o+ heat
Utilize its process ammonia tail gas, shortcoming one does not have the ammonia in synthetical recovery ammonia tail gas, but discharged by its Direct Resolution, causes the waste of resource; Two is do not collect tungsten oxide dust in ammonia tail gas, effectively can not improve the rate of recovery of tungsten; Three is need high temperature in catalytic process, creates thermal pollution, and relates to combustion of hydrogen acquisition energy, adds the potential safety hazards such as blast, fire.
Summary of the invention
The object of the invention is to provide a kind of method that ammonia vent gas treatment reclaims, it can be accomplished without harmful tailpipe emissions, effectively can also reclaim converter calcining ammonium paratungstate to produce in tungsten oxide product process with the ammonia of tail gas discharge and tungsten powder dirt, both secondary resource comprehensive utilization had been accomplished, it also avoid the impact that ammonia emission causes atmospheric environment, realize the environmental requirement without ammonia pollution, not only environmental protection but also economic.
Technical solution of the present invention: a kind of method that ammonia vent gas treatment reclaims, comprises the following steps:
(1) gather dust
Produce with converter calcining ammonium paratungstate the ammonia tail gas discharged in tungsten oxide product process to deliver in dust collecting system and carry out cyclone dust collection or gravity gathers dust (cyclone dust collection also can be adopted to add gravity gather dust), effectively to reclaim the tungsten oxide dust in the ammonia-containing exhaust of converter generation, and purify ammonia-containing exhaust;
(2) Water spray gathers dust
In ammonia tail gas larger particles tungsten oxide dust through step (1) major part remove, wherein in ammonia tail gas, remaining fine grained tungsten oxide dust absorbs through Venturi tube or absorption tower Water spray again, after absorbing liquid reaches capacity, crystal structure is allowed to separate out by the method cooled, solution circulation uses, and tail gas enters next step and carries out advanced treating;
(3) condensation
Be passed in condenser by the ammonia tail gas after Water spray gathers dust, control at 30-80 DEG C by its temperature, can collect in condensation chamber and obtain high concentration ammoniacal liquor, the ammoniacal liquor obtained can fully utilize or sell, thus protection of the environment;
(4) acid absorbs
Gather dust with condensed ammonia tail gas by absorption tower through Water spray, be ammonium salt solution with a kind of spray-absorption in sulfuric acid, hydrochloric acid, nitric acid, phosphoric acid, tail gas directly discharges.Reaction equation is:
2NH 3+H 2SO 4=(NH 4) 2SO 4
NH 3+HCl=NH 4Cl
NH 3+HNO 3=NH 4NO 3
(5) evaporative crystallization
One in ammonia tail gas and pH value≤6 sulfuric acid, hydrochloric acid, nitric acid, phosphoric acid is constantly reacted, when pH value reaches neutrality, obtain sulfate solution or ammonium chloride, ammonium nitrate, the ammonium phosphate solution of saturated concentration, by solution evaporative crystallization, the Water circulation that evaporation obtains carries out secondary Water spray in step (2) and gathers dust, the sulfate of ammoniac obtained or ammonium chloride, ammonium nitrate crystals, as byproduct, can be used for the raw materials for production of composite fertilizer, accomplish that resource comprehensive utilization utilizes.
Beneficial effect of the present invention: the ammonia-containing exhaust that can process variable concentrations, also can process the ammonia-containing exhaust containing other combustible, the ammonia tail gas that converter produces after treatment, tungsten oxide dust in tail gas can all reclaim, ammonia all can be converted into sulfate of ammoniac (or ammonium chloride, ammonium nitrate) crystal, no longer produces the problem of ammonia pollution and secondary environmental pollution; Cost of investment is low, and processing method is simple, and byproduct ammoniacal liquor can be used for other smelting chemical field, and sulfate of ammoniac (or ammonium chloride, ammonium nitrate etc.) can be used for composite fertilizer field, has not only accomplished protection of the environment, and has accomplished the comprehensive utilization of resource.
Accompanying drawing explanation
Accompanying drawing is embodiment of the present invention process chart.
Detailed description of the invention
Below in conjunction with embodiment, the present invention is further illustrated, and institute's use equipment is prior art.
Embodiment 1: the present invention includes one-level and gather dust, secondary Water spray gathers dust, condensation, three grades, sulfuric acid (pH value≤6) spray, evaporative crystallization prepares high-purity sulphuric acid ammonia crystal step, gather dust in step in above-mentioned one-level, first converter high-temperature calcination is decomposed in ammonium paratungstate and produce ammonia-containing exhaust and carry out cyclone dust collection or gravity gathers dust, to be gathered dust by one cyclonic or gravity gathers dust the bulky grain tungsten oxide dust that can fully reclaim in ammonia-containing exhaust, also the effect that next step Water spray gathers dust can be strengthened, secondary Water spray subsequently gathers dust in step, ammonia tail gas after dedusting is carried out secondary gathered dust by the spray tower that gathers dust, remove granule tungsten oxide dust further, ammoniacal liquor is collected again after condensing steps, remaining ammonia tail gas is through persulfuric acid three grades spray, last ammonia tail gas reaches the discharge standard of national regulation, by exhaust blower, gas is entered air, the tungsten oxide dust of the larger particles that one-level is collected after gathering dust and ammonia-containing exhaust being carried out cyclone settling or gravitational settling in step returns converter feeding mouth, terminates to enter down one step, ammonia tail gas after one-level is gathered dust passes in Water spray dust arrester installation, and spray gathers dust in process, ensures that water droplet is by high atomisation, carries out after atomizing spray gathers dust, terminating to enter down one step, ammonia tail gas after being gathered dust by secondary Water spray passes in condenser, controls temperature at 50 DEG C, until condensator outlet is emerged without steam, terminates to enter down one step, condensed ammonia-containing exhaust is passed into three grades of sour spray equipments, acid spray sprays from top to down, and ammonia-containing exhaust is discharged from bottom to top, both reverse abundant haptoreactions, terminates to enter down one step, ammonia-containing exhaust after three grades of acid sprays is entered air by exhaust blower, described ammonia-containing exhaust≤5mg/m 3, described ammonia-containing exhaust is through the ammoniacal liquor of Water spray and condensation gained, and the concentration of its free ammonia is 28g/L, and the concentration of tungstenic is 55g/L, completely can by mending after ammonia for the analyzing step in APT production process, described ammonia-containing exhaust carries out spray neutralization reaction by acid, so need to carry out replacing eo-acid according to the pH value of reactant liquor, to maintain the acid degree in spray column, when described spray liquid pH value reaches neutrality, obtain the sulfate solution that concentration is saturated, by solution evaporative crystallization, evaporate the Water circulation obtained to gather dust in secondary Water spray, the sulfate of ammoniac crystal obtained, as byproduct, can be used for the raw materials for production of composite fertilizer, accomplishes that resource comprehensive utilization utilizes.
Embodiment 2: the present invention includes one-level and gather dust, secondary Water spray gathers dust, condensation, three grades, nitric acid (pH value≤6) spray, evaporative crystallization prepares high pure nitric acid ammonia crystal step, gather dust in step in above-mentioned one-level, first converter high-temperature calcination is decomposed in ammonium paratungstate and produce ammonia-containing exhaust and carry out cyclone dust collection or gravity gathers dust, to be gathered dust by one cyclonic or gravity gathers dust the bulky grain tungsten oxide dust that can fully reclaim in ammonia-containing exhaust, also the effect that next step Water spray gathers dust can be strengthened, secondary Water spray subsequently gathers dust in step, ammonia tail gas after dedusting is carried out secondary gathered dust by the spray tower that gathers dust, remove granule tungsten oxide dust further, ammoniacal liquor is collected again after condensing steps, remaining ammonia tail gas is through pernitric acid three grades spray, last ammonia tail gas reaches the discharge standard of national regulation, by exhaust blower, gas is entered air, the tungsten oxide dust of the larger particles that described ammonia-containing exhaust one-level is collected after gathering dust and ammonia-containing exhaust being carried out cyclone settling or gravitational settling in step returns converter feeding mouth, terminates to enter down one step, ammonia tail gas after one-level is gathered dust passes in Water spray dust arrester installation, and spray gathers dust in process, ensures that water droplet is by high atomisation, carries out after atomizing spray gathers dust, terminating to enter down one step, ammonia tail gas after being gathered dust by secondary Water spray passes in condenser, controls temperature at 40 DEG C, until condensator outlet is emerged without steam, terminates to enter down one step, condensed ammonia-containing exhaust is passed into three grades of sour spray equipments, acid spray sprays from top to down, and ammonia-containing exhaust is discharged from bottom to top, both reverse abundant haptoreactions, terminates to enter down one step, ammonia-containing exhaust after three grades of acid sprays is entered air by exhaust blower, described ammonia-containing exhaust≤4mg/m 3, described ammonia-containing exhaust is through the ammoniacal liquor of Water spray and condensation gained, and the concentration of its free ammonia is 32g/L, and the concentration of tungstenic is 70g/L, completely can by mending after ammonia for the analyzing step in APT production process, described ammonia-containing exhaust carries out spray neutralization reaction by acid, so need to carry out replacing eo-acid according to the pH value of reactant liquor, to maintain the acid degree in spray column, when described spray liquid pH value reaches neutrality, obtain the nitric acid ammonia solution that concentration is saturated, by solution evaporative crystallization, evaporate the Water circulation obtained to gather dust in secondary Water spray, the nitric acid ammonia crystal obtained, as byproduct, can be used for the raw materials for production of composite fertilizer, accomplishes that resource comprehensive utilization utilizes.

Claims (1)

1. a method for ammonia vent gas treatment recovery, is characterized in that:
Comprise one-level to gather dust, secondary Water spray gathers dust, condensation, three grades, pH value≤6 sulfuric acid spray, evaporative crystallization prepares high-purity sulphuric acid ammonia crystal step, gather dust in step in above-mentioned one-level, first cyclone dust collection is carried out by producing ammonia-containing exhaust in converter high-temperature calcination decomposition ammonium paratungstate, to be gathered dust the bulky grain tungsten oxide dust that can fully reclaim in ammonia-containing exhaust by one cyclonic, also the effect that next step Water spray gathers dust can be strengthened, secondary Water spray subsequently gathers dust in step, ammonia tail gas after dedusting is carried out secondary gathered dust by the spray tower that gathers dust, remove granule tungsten oxide dust further, ammoniacal liquor is collected again after condensing steps, remaining ammonia tail gas is through persulfuric acid three grades spray, last ammonia tail gas reaches the discharge standard of national regulation, by exhaust blower, gas is entered air, the tungsten oxide dust of the larger particles that one-level is collected after gathering dust and ammonia-containing exhaust being carried out cyclone settling in step returns converter feeding mouth, ammonia tail gas after one-level is gathered dust passes in Water spray dust arrester installation, and spray gathers dust in process, ensures that water droplet is by high atomisation, carries out after atomizing spray gathers dust, terminating to enter down one step, ammonia tail gas after being gathered dust by secondary Water spray passes in condenser, controls temperature at 50 DEG C, until condensator outlet is emerged without steam, terminates to enter down one step, condensed ammonia-containing exhaust is passed into three grades of sour spray equipments, acid spray sprays from top to down, and ammonia-containing exhaust is discharged from bottom to top, both reverse abundant haptoreactions, terminates to enter down one step, ammonia-containing exhaust after three grades of acid sprays is entered air by exhaust blower, enters the ammonia-containing exhaust≤5mg/m of air 3, described ammonia-containing exhaust is through the ammoniacal liquor of Water spray and condensation gained, and the concentration of its free ammonia is 28g/L, and the concentration of tungstenic is 55g/L, completely can by mending after ammonia for the analyzing step in APT production process, described ammonia-containing exhaust carries out spray neutralization reaction by acid, so need to carry out replacing eo-acid according to the pH value of reactant liquor, to maintain the acid degree in spray column, when spray liquid pH value reaches neutrality, obtain the sulfate solution that concentration is saturated, by solution evaporative crystallization, evaporate the Water circulation obtained and gather dust in secondary Water spray, the sulfate of ammoniac crystal obtained is as byproduct.
CN201410050253.XA 2014-02-14 2014-02-14 A kind of method that ammonia vent gas treatment reclaims Expired - Fee Related CN103785263B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410050253.XA CN103785263B (en) 2014-02-14 2014-02-14 A kind of method that ammonia vent gas treatment reclaims

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410050253.XA CN103785263B (en) 2014-02-14 2014-02-14 A kind of method that ammonia vent gas treatment reclaims

Publications (2)

Publication Number Publication Date
CN103785263A CN103785263A (en) 2014-05-14
CN103785263B true CN103785263B (en) 2016-01-20

Family

ID=50661577

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410050253.XA Expired - Fee Related CN103785263B (en) 2014-02-14 2014-02-14 A kind of method that ammonia vent gas treatment reclaims

Country Status (1)

Country Link
CN (1) CN103785263B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107543903A (en) * 2017-08-25 2018-01-05 北京林业大学 A kind of method and apparatus for monitoring dewatering technology of mud ammonia and hydrogen sulfide on-line

Families Citing this family (16)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104630490B (en) * 2015-02-10 2017-01-11 江西稀有金属钨业控股集团有限公司 Method for preparing ammonium tungstate
CN105236446B (en) * 2015-11-24 2017-12-15 攀钢集团攀枝花钢铁研究院有限公司 A kind of recycling method of waste hydrochloric acid
CN107089685A (en) * 2017-06-26 2017-08-25 江西省修水赣北钨业有限公司 A kind of circulation utilization method for producing ammine in ammonium paratungstate gas
CN110170222B (en) * 2019-05-14 2022-09-23 江西理工大学 Treatment method and system for tungsten smelting waste gas
CN110963508B (en) * 2020-01-15 2024-05-14 河南申越检测技术有限公司 Device and process for preparing solid ammonium chloride from ammonia-containing waste gas
CN111482059A (en) * 2020-03-26 2020-08-04 厦门钨业股份有限公司 Treatment method of ammonia-containing tail gas and ammonia-containing tail gas treatment system
CN111442968A (en) * 2020-05-27 2020-07-24 北京航天益来电子科技有限公司 Denitration tail gas online monitoring and ammonia removal device and method
CN112354328A (en) * 2020-10-29 2021-02-12 山东合力泰化工有限公司 Tail gas absorption process and device in melamine production process
CN112933940B (en) * 2021-03-03 2022-08-19 江苏科技大学 Ammonia gas recovery and ammonium sulfate crystallization system and working method thereof
CN113429317A (en) * 2021-06-22 2021-09-24 四川金象赛瑞化工股份有限公司 Non-liquid phase production method of phthalonitrile
CN113429314A (en) * 2021-06-22 2021-09-24 四川金象赛瑞化工股份有限公司 Ammonium nitrate and xylylenediamine coproduction method and heat exchange network
CN114515499B (en) * 2022-02-21 2023-04-07 新泰市日进化工科技有限公司 Intelligent ammonia-containing tail gas recovery control system and method for acid sprayer
CN114984733A (en) * 2022-05-10 2022-09-02 成都虹波钼业有限责任公司 Method for treating mixed gas containing carbon dioxide and ammonia
WO2023222433A1 (en) 2022-05-17 2023-11-23 Basf Se Process for preparing ammonium chloride
CN115057568B (en) * 2022-06-08 2023-10-31 厦门钨业股份有限公司 Method for treating ammonium paratungstate crystallization mother liquor
CN117326982A (en) * 2022-09-30 2024-01-02 四川元理材料科技有限公司 Industrial process for synthesizing isophorone dicarbamic acid n-butyl ester by urea method

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101530737A (en) * 2009-03-03 2009-09-16 福建金鑫钨业股份有限公司 Method for processing waste water/gas from tungsten smelting and a device thereof
CN101816841A (en) * 2010-05-17 2010-09-01 赣州华兴钨制品有限公司 Method for recovering ammonia nitrogen from ammonia-containing steam
CN101857245A (en) * 2010-05-28 2010-10-13 厦门嘉鹭金属工业有限公司 Ammonia recovery method in tungsten metallurgy
CN102688607A (en) * 2012-05-24 2012-09-26 崇义章源钨业股份有限公司 Ammonia tail gas recycling method and system
CN202526935U (en) * 2012-05-10 2012-11-14 毕节金河化工有限公司 Treatment device for tail gas produced by synthetic ammonia process

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101530737A (en) * 2009-03-03 2009-09-16 福建金鑫钨业股份有限公司 Method for processing waste water/gas from tungsten smelting and a device thereof
CN101816841A (en) * 2010-05-17 2010-09-01 赣州华兴钨制品有限公司 Method for recovering ammonia nitrogen from ammonia-containing steam
CN101857245A (en) * 2010-05-28 2010-10-13 厦门嘉鹭金属工业有限公司 Ammonia recovery method in tungsten metallurgy
CN202526935U (en) * 2012-05-10 2012-11-14 毕节金河化工有限公司 Treatment device for tail gas produced by synthetic ammonia process
CN102688607A (en) * 2012-05-24 2012-09-26 崇义章源钨业股份有限公司 Ammonia tail gas recycling method and system

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107543903A (en) * 2017-08-25 2018-01-05 北京林业大学 A kind of method and apparatus for monitoring dewatering technology of mud ammonia and hydrogen sulfide on-line

Also Published As

Publication number Publication date
CN103785263A (en) 2014-05-14

Similar Documents

Publication Publication Date Title
CN103785263B (en) A kind of method that ammonia vent gas treatment reclaims
US10213739B2 (en) Dust removal and desulfurization of FCC exhaust gas
WO2016192272A1 (en) Integrated flue gas treatment device and method
CN102489149B (en) Flue-gas purification handling method
WO2016192274A1 (en) Flue gas treatment device and method
US10125024B2 (en) System and method for purifying and preparing high-purity vanadium pentoxide powder
CN104707451B (en) Method for ammonia-process capture of carbon in flue gas and synthesis of chemical products
CN105217580B (en) A kind of method for preparing sulfuric acid with electrolytic manganese residues high temperature desulfurizing enriched flue gas
US20180009675A1 (en) System and Method for Producing High-Purity Vanadium Pentoxide Powder
US20180009674A1 (en) System and method for producing high-purity vanadium tetraoxide powder
CN210107409U (en) Hazardous waste burns flue gas clean system
CN113559690B (en) System and method for integrally purifying waste incineration flue gas and fly ash
CN105233647A (en) Desulphurization denitration method for ammonium sulfide solution
CN102600710B (en) Treatment method of high-concentration ammonia nitrogen wastewater
CN103100294A (en) Method for removing oxynitride from flue gas through ozone oxidation method
CN110332552B (en) Resourceful treatment system and method for chlorine-sulfur-containing organic waste liquid
US11292718B2 (en) Process for preparing sulfur from reduction of sulfate/ nitrate by iron-carbon and recovering desulfurization/ denitration agents
CN103588220B (en) A kind of ammonium chloride decomposes soda acid joint process and the system of preparing ammonia and hydrochloric acid
CN111514736A (en) Flue gas desulfurization and denitrification system and method combining ozone oxidation with ammonia spraying
CN106178725A (en) The desulphurization denitration dust collecting process of a kind of glass kiln and device
CN104445335A (en) Process and system for producing anhydrous calcium chloride by utilizing organic matter-containing waste hydrochloric acid
CN113251420A (en) Industrial waste treatment method and device
CN218741200U (en) Semi-dry treatment system for flue gas desulfurization and denitrification
CN105498504B (en) Iron pellet sintering exhaust gas cleaner and its purification method and application
CN212757996U (en) Flue gas desulfurization and denitrification system adopting ozone oxidation and ammonia spraying

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
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20160120

Termination date: 20200214

CF01 Termination of patent right due to non-payment of annual fee