Nothing Special   »   [go: up one dir, main page]

CN105797562B - The double ammonia process integration desulfurization denitration systems of coking flue gas two-part - Google Patents

The double ammonia process integration desulfurization denitration systems of coking flue gas two-part Download PDF

Info

Publication number
CN105797562B
CN105797562B CN201610293501.2A CN201610293501A CN105797562B CN 105797562 B CN105797562 B CN 105797562B CN 201610293501 A CN201610293501 A CN 201610293501A CN 105797562 B CN105797562 B CN 105797562B
Authority
CN
China
Prior art keywords
flue gas
section
ammonia
pipeline
desulphurization denitration
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
CN201610293501.2A
Other languages
Chinese (zh)
Other versions
CN105797562A (en
Inventor
汤志刚
王登富
温燕明
康春清
王杰
陈善龙
李桂花
孙兆俊
段德强
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.)
Jinan Metallurgy Chemical Equipment Co ltd
Original Assignee
Jinan Metallurgy Chemical Equipment 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 Jinan Metallurgy Chemical Equipment Co ltd filed Critical Jinan Metallurgy Chemical Equipment Co ltd
Priority to CN201610293501.2A priority Critical patent/CN105797562B/en
Publication of CN105797562A publication Critical patent/CN105797562A/en
Application granted granted Critical
Publication of CN105797562B publication Critical patent/CN105797562B/en
Active 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency
    • Y02P20/129Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Combustion & Propulsion (AREA)
  • Environmental & Geological Engineering (AREA)
  • Treating Waste Gases (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • Organic Chemistry (AREA)

Abstract

The invention discloses the double ammonia process integration desulfurization denitration systems of coking flue gas two-part,Including denitration in the stove system,Chimney,Denitration in the stove system is connected with coke oven,Coke oven leads to be connected with chimney,Chimney is connected with waste heat boiler,Waste heat boiler is connected with smoke re-heater,Smoke re-heater is connected with flue gas wind turbine,Flue gas blower and pipeline is connected with scrubber,Scrubber is connected with cleaning circulation pump,Cleaning circulation pump is connected with cleaning dust cooler,Cleaning dust cooler is connected with scrubber upper entrance pipeline,Scrubber is connected with pipeline reactor,Pipeline reactor is connected with ozone generator,Pipeline reactor is connected with desulphurization denitration integrated tower,It is connected at the top of desulphurization denitration integrated tower with smoke re-heater,Smoke re-heater is connected with chimney,The purifying smoke for discharging desulphurization denitration integrated tower enters return chimney high altitude discharge after smoke re-heater heat temperature raising.Denitration cost of the present invention is low, efficient.

Description

The double ammonia process integration desulfurization denitration systems of coking flue gas two-part
Technical field
The present invention relates to coking stack gases purification technology field, more particularly to a kind of coking flue gas two-part are double Ammonia(Ammonium)Method integration desulfurization denitration system.
Background technology
The desulphurization denitration processing and the processing of ammonia-containing water of coking flue gas of the prior art have various ways, to reach energy Source recycling, reduce energy consumption, the purpose for reducing environmental pollution and destroying, but these method and apparatus of the prior art are deposited The defects of be:The flue gas desulfurization and denitration method having in the prior art is of high cost, such as high temperature method of the prior art and catalysis Method method of denitration is of high cost;Some desulfurization off sulfide effect are poor, residual quantity is big, and clean-up effect is bad, while vapour phase amount of ammonia slip is more, Environment and air are polluted.
The present invention is applicant on the basis of original applying number is 201510690115.2 patents of invention, passes through persistence techniques Innovation, further reduces technological equipment investment and the operating cost of desulphurization denitration.
The content of the invention
It is to solve the problems, such as that existing flue gases of cock oven desulphurization denitration high expensive, investment are bigger than normal that the purpose of the present invention, which is exactly, There is provided a kind of coking flue gas two-part double ammonia(Ammonium)Method integration desulfurization denitration system.The present invention utilizes the self-produced ammonium hydroxide of coking As alkali source, desulphurization denitration purification is carried out to flue gas, recyclable ammonium sulfate is formed and ammonium nitrate is incorporated to the sulphur of coking flow Ammonium workshop section, the element sulphur in stack gases and nitrogen are converted into can value-added byproduct;Of the invention fully combine in stove takes off Nitre and the outer denitration technology of stove, significantly reduce denitration cost;The present invention uses the ammonium hydroxide desulphurization denitration of various concentrations, and concentrated ammonia liquor can To form resource product, weak aqua ammonia reduces the vapour phase partial pressure of ammonia, reduces the escaping of ammonia;The present invention uses integration apparatus, at the same time Desulphurization denitration, significantly reduces desulphurization denitration investment;The present invention is using hydrogen peroxide denitration in the outer denitration of ozone stove, tower, relatively low At a temperature of realize the removing of NOx, significantly reduce denitration cost;The present invention is washed using coking flow internal resource ammonium sulfate liquor Flue gas is washed, further avoid ammonia process of desulfurization denitration would generally produce the phenomenon of free ammonia vapour phase escape, not increase cost not only, And the inside networking degree of coking flow is improved, efficiently solve the escaping of ammonia phenomenon of desulphurization denitration process.
The present invention solve technical problem technical solution be:
A kind of double ammonia process integration desulfurization denitration systems of coking flue gas two-part, including it is denitration in the stove system, chimney, remaining Heat boiler, smoke re-heater, coke oven, further include flue gas wind turbine, scrubber, cleaning dust circulating pump, cleaning dust cooling Device, ozone generator, pipeline reactor, desulphurization denitration integrated tower, circulation oxidator, the denitration in the stove system are empty by dilution Feed channel or dilution nitrogen pipeline are connected with coke oven, and coke oven is connected by coke oven flue gas pipeline with chimney, and chimney passes through coke oven cigarette Feed channel is connected with waste heat boiler, and waste heat boiler is connected by flue after recovered flue gas high-temperature residual heat with smoke re-heater, Smoke re-heater is connected by flue after recycling low temperature exhaust heat with flue gas wind turbine, flue gas blower and pipeline and cleaning dust Device connects, and scrubber lower part is connected by liquid pipe with cleaning circulation pump, and cleaning circulation pump is exported by lower liquid phase Pipeline is connected with cleaning dust cooler, and cleaning dust cooler is connected with scrubber upper entrance pipeline, cleaning dust Device is connected by pipeline after cleaning dust with pipeline reactor, and pipeline reactor is connected by ozone pipeline with ozone generator, Pipeline reactor is connected by flue after reaction with desulphurization denitration integrated tower, and the flue gas after washing cools down is with coming from The ozone of ozone generator is sufficiently mixed reaction in pipeline reactor, and the nitric oxide in flue gases of cock oven is part or all of After oxidation, it is sent into desulphurization denitration integrated tower and carries out desulphurization denitration processing;Pass through fume pipe after purification at the top of desulphurization denitration integrated tower Road is connected with smoke re-heater, and smoke re-heater is connected by purifying smoke pipeline with chimney, discharge desulphurization denitration integrated tower Purifying smoke enters smoke re-heater, and 100-150 °C of return is increased to using the low temperature exhaust heat heating of flue gas before desulphurization denitration Chimney, high altitude discharge.
The desulphurization denitration integrated tower includes one section of desulphurization denitration section, the two sections of desulphurization denitration sections at middle part of lower part, two sections The top of desulphurization denitration section is equipped with and catches ammonia section, catches ammonia section top and is equipped with physical demister.One section of desulphurization denitration section with The scrubbing ammonia waterpipe of concentrated ammonia liquor pipeline or raw coke oven gas desulfurization regeneration tail gas connects, the concentrated ammonia liquor pipeline and coking ammonia still process The concentrated ammonia liquor pipeline connection of workshop section, the scrubbing ammonia waterpipe of the scrubbing ammonia waterpipe and raw coke oven gas desulfurization regeneration tail gas connect Connect, the alkali of the washing ammonium hydroxide of concentrated ammonia liquor or raw coke oven gas desulfurization regeneration tail gas from coking ammonia still process workshop section as desulphurization denitration Source adds one section of desulphurization denitration section.One section of circulating pump is connected by one section of circulation ammonium liquid pipe road with desulphurization denitration integrated tower, one section Cooler is connected by one section of circulation ammonium liquid pipe road with one section of circulating pump, and one-step cooling device is by one section of circulation ammonium liquid pipe road with taking off Sulphur denitration integrated tower connects, and one section of desulphurization denitration section of desulphurization denitration integrated tower is connected by ammonium liquid side line pipeline and circulation oxidator Connect, the outlet of circulation cycle pump is connected by circulation cycle conduit upper with circulation oxidator top, the circulation cycle pipeline Top is equipped with injector close to the position on circulation oxidator top, the import of circulation cycle pump by circulation cycle pipeline lower part with Circulation oxidator bottom connects, and circulation cycle pump is mixed the ammonium sulfate after oxidation and ammonium nitrate by spur outlet and pipeline Ammonium salt solution is sent to the ammonium sulfate workshop section Resource recovery product of coking or for complex acid;
Two sections of desulphurization denitration sections are connected with the remained ammonia from coking ammonia still process workshop section by pipeline, are steamed from coking The diluent that the remained ammonia of ammonia workshop section is used as vapour phase ammonia density by pipeline adds two sections of desulphurization denitration sections, two sections of desulfurization The bottom of denitration section is connected by two sections of circulation fluid pipelines with two sections of pump inlets, and two sections of circulating-pump outlets pass through two sections of circulations Liquid pipe road is connected with two-step cooling device, and two-step cooling device is connected by the top of two sections of circulation fluid pipelines and two sections of desulphurization denitration sections Connect.Remained ammonia is sent to the ammonia still of the ammonia still process workshop section of coking by pipeline by the spur outlet of two sections of circulating pumps.
The ammonia section of catching is connected with ammonium sulfate liquor pipeline, the flue gas after two sections of desulphurization denitrations, into desulphurization denitration Ammonia section is caught on integrated tower top, washs flue gas using the acid mother liquid of sulfuric acid workshop section, sulphur ammonium acid mother liquid washing flue gas is caught Return to ammonium sulfate workshop section after remaining ammonia, catch ammonia section controlled at 50-70 °C.
The physical demister is intercepted after power eliminates flue gas acid mist by centrifugal force and inertia, and flue gas is from desulfurization Discharge on denitration integrated tower top;Flue gas after catching ammonia section enters the physical demisting dress at the top of desulphurization denitration integrated tower Put, after intercepting power elimination flue gas acid mist by centrifugal force and inertia, flue gas is discharged at the top of desulphurization denitration integrated tower;It is described The temperature control of physical demister is 50-60 °C.
The injector uses venturi tube structure, and injector is connected with external air duct, utilizes the spray of venturi tube structure Oxidant of the air as circulation oxidator is incorporated herein in emitter circulation injection suction, and the circulation pumped by circulation cycle sprays production Raw suction introduces air, and the oxygen in air is fully sufficiently mixed reaction with ammonium liquid, by ammonium sulfite therein generation sulfuric acid Mixed salt solution containing ammonium sulfate and ammonium nitrate, is then sent to the ammonium sulfate workshop section of coking, Resource recovery product, the ring by ammonium Flow controlled at 50-80 °C in oxidator, pH controls are 6.0-6.8.
The dilution air pipeline is dilution air with the flue gas after waste heat recovery or purified flue gas, Huo Zhe It is mixed into inert gas in air, the mixed volume of flue gas or inert gas is the 0-50% of air capacity;It is mixed into heating gas Low-heat value gas, low-heat value gas mixed volume are the 0-70% of heating gas amount, and the nitrogen oxides reduced in coke oven discharge flue gas contains Amount, it is 250-550mg/m3 to make the amount of nitrogen oxides in coke oven discharge flue gas.
Flue gases of cock oven temperature after denitration in the stove system denitration process is 220-350 °C, and flue gases of cock oven is sent into Waste heat boiler recycles flue gas high-temperature residual heat, and the waste heat of waste heat boiler recycling is used as producing steam, or is directly used in ammonia still process heating Distilled ammonia wastewater, or heating conduction oil, after recycling high-temperature residual heat, effluent gas temperature is down to 150-200 °C;Recycled by waste heat boiler Flue gas after high-temperature residual heat is sent into smoke re-heater recycling flue gases at low waste heat, the purification that desulphurization denitration integrated tower is discharged Flue gas is heated to 100-150 °C from 50-80 °C, and own temperature is down to 90-130 °C;Flue after recycling low temperature exhaust heat Gas is sent into scrubber by flue gas wind turbine, is removed wash cycle liquid from washing using cleaning circulation pump in scrubber Dirt device top spray into, with fed from below into flue gas counter current contacting, washing removing flue gas in dust impurity, flue gas into One step is cooled to 60-80 °C.
Flue gas after washing cools down is sufficiently mixed instead with the ozone from ozone generator in pipeline reactor Should, after the nitric oxide in flue gases of cock oven partly or entirely oxidation, it is sent into desulphurization denitration integrated tower and carries out at desulphurization denitration Reason.
Hydrogen peroxide, which is added, in one section of desulphurization denitration section, two sections of desulphurization denitration sections carries out oxidation.Strengthen denitration Efficiency, reduces ozone-depleting, reduces operating cost.
Beneficial effects of the present invention:
1. the present invention carries out desulphurization denitration purification, formation can be returned by the use of the self-produced ammonium hydroxide of coking as alkali source to flue gas The ammonium sulfate and ammonium nitrate of receipts are incorporated to the ammonium sulfate workshop section of coking flow, and the element sulphur in stack gases and nitrogen are converted into can Value-added byproduct;Solid waste and pollution transportation are not produced.
2. of the invention fully combine denitration in the stove and the outer denitration technology of stove, denitration in the stove is using dilution air and dilution coal gas Measure be combined, significantly reduce denitration cost.
3. the present invention uses the ammonium hydroxide desulphurization denitration of various concentrations, concentrated ammonia liquor can form resource product, weak aqua ammonia drop The vapour phase partial pressure of low ammonia, reduces the escaping of ammonia, while the close lotus root of ammonium sulfate workshop section existing with coking and ammonia still process workshop section closes and is connected, fully Using and excavated the automatically cleaning and self-purification function of coking flow;Construction investment and operating cost is greatly reduced.
4. the present invention uses integration apparatus, simultaneous SO_2 and NO removal, resource product, two are generated by one section of desulphurization denitration Section desulphurization denitration and ammonium sulfate liquor catch ammonia section and eliminate the escaping of ammonia, physical demister elimination acid mist, not only complete a variety of work( Can it is integrated, enhance desulphurization and denitration, catch ammonia, defogging effect, also significantly reduce desulphurization denitration investment;Improve Flue gases of cock oven degree of purification and environmental quality.
5. patent of the present invention, using the outer denitration of ozone stove, can be recycled fully more than flue gases of cock oven using oxidizing process Heat, and the removing of nitrogen oxides is realized at a lower temperature, it can effectively reduce denitration cost;By one section of desulphurization denitration section, Two sections of desulphurization denitration sections add hydrogen peroxide and carry out oxidation, strengthen denitration efficiency, reduce ozone-depleting, reduce operating cost.
6. the present invention has fully recycled the UTILIZATION OF VESIDUAL HEAT IN of flue gas.Using waste heat boiler recycle high-temperature residual heat, byproduct steam, Or distilled ammonia wastewater is directly heated, or heating conduction oil;The purified flue gas of desulphurization denitration is heated using low temperature exhaust heat, is effectively disappeared Except the dew point corrosion of flue gas, the high altitude discharge advantage of original chimney is taken full advantage of.By profit using inside coking flow Resource ammonium sulfate liquor washs flue gas, and further avoid ammonia process of desulfurization denitration would generally produce the phenomenon of free ammonia vapour phase escape, Do not increase cost not only, and improve the inside networking degree of coking flow, efficiently solve the escaping of ammonia of desulphurization denitration process Phenomenon.
7. the present invention develops circulation oxidator, sulfite oxidation effect is effectively improved.
Brief description of the drawings
Fig. 1 is the structure diagram of invention.
Embodiment
For a better understanding of the present invention, embodiments of the present invention are explained in detail below in conjunction with the accompanying drawings.
As shown in Figure 1, a kind of double ammonia process integration desulfurization denitration systems of coking flue gas two-part, including denitration in the stove system System 1, chimney 2, waste heat boiler 3, smoke re-heater 4, flue gas wind turbine 5, scrubber 6, cleaning dust circulating pump 7, washing remove Dirt cooler 8, ozone generator 9, pipeline reactor 10, desulphurization denitration integrated tower 11, one sections of circulating pumps 12, one-step cooling devices 13rd, two sections of circulating pumps 14, two-step cooling device 15, circulation oxidator 16, circulation cycle pump 17, injector 18, coke oven 19.The stove Interior denitrating system 1 is connected by dilution air pipeline 29 and dilution gas piping 28 with coke oven 19, and coke oven 19 passes through coke oven flue gas Pipeline is connected with chimney 2, and chimney 2 is connected by coke oven flue gas pipeline with waste heat boiler 3, and waste heat boiler 3 passes through recovered flue gas height Flue is connected with smoke re-heater 4 after warm waste heat, and smoke re-heater 4 is by recycling flue and flue gas after low temperature exhaust heat Wind turbine 5 connects, and flue gas wind turbine 5 is connected by pipeline with scrubber 6, and 6 lower part of scrubber is by liquid pipe with washing Wash circulating pump 7 to connect, cleaning circulation pump 7 is connected by lower liquid phase outlet conduit with cleaning dust cooler 8, and cleaning dust is cold But device 8 is connected with 6 upper entrance pipeline of scrubber, and scrubber 6 passes through pipeline after cleaning dust and pipeline reactor 10 connections, pipeline reactor 10 are connected by ozone pipeline with ozone generator 9, and pipeline reactor 10 passes through fume pipe after reaction Road is connected with desulphurization denitration integrated tower 11.The top of desulphurization denitration integrated tower 11 passes through flue after purification and smoke re-heater 4 Connection, smoke re-heater 4 are connected by purifying smoke pipeline with chimney 2.The purifying smoke for discharging desulphurization denitration integrated tower enters Smoke re-heater, is increased to 100-150 °C using the low temperature exhaust heat heating of flue gas before desulphurization denitration, returns to chimney, high idle discharge Put.
The desulphurization denitration integrated tower includes one section of desulphurization denitration section, the two sections of desulphurization denitration sections at middle part of lower part, two sections The top of desulphurization denitration section is equipped with and catches ammonia section, catches ammonia section top and is equipped with physical demister.One section of desulphurization denitration section with The scrubbing ammonia waterpipe 20 of concentrated ammonia liquor pipeline 21 or raw coke oven gas desulfurization regeneration tail gas connects, the concentrated ammonia liquor pipeline and coking The concentrated ammonia liquor pipeline connection of ammonia still process workshop section, the scrubbing ammonia waterpipe of the scrubbing ammonia waterpipe and raw coke oven gas desulfurization regeneration tail gas Connection, the washing ammonium hydroxide of concentrated ammonia liquor or coal oven dithio-gas desulfurization regeneration tail gas from coking ammonia still process workshop section take off as desulfurization The alkali source of nitre adds one section of desulphurization denitration section.One section of circulating pump 12 passes through one section of circulation ammonium liquid pipe road and desulphurization denitration integrated tower 11 Connection, one-step cooling device 13 are connected by one section of circulation ammonium liquid pipe road with one section of circulating pump 12, and one-step cooling device 13 passes through one section Circulation ammonium liquid pipe road is connected with desulphurization denitration integrated tower 11, and one section of desulphurization denitration section of desulphurization denitration integrated tower 11 passes through ammonium liquid side Spool road is connected with circulation oxidator 16, and the outlet of circulation cycle pump 17 passes through 30 top of circulation cycle pipeline and circulation oxidator 16 tops connect, and 30 top of circulation cycle pipeline is equipped with injector 18, circulation close to the position on 16 top of circulation oxidator The import of circulating pump 17 is connected by circulation cycle pipeline lower part with 16 bottom of circulation oxidator, and circulation cycle pump 17 passes through branch line Ammonium sulfate after oxidation and ammonium nitrate mixed-ammonium salt solution are sent to 27 Resource recovery of ammonium sulfate workshop section of coking by outlet and pipeline Product or for complex acid.
Two sections of desulphurization denitration sections are connected with the remained ammonia from coking ammonia still process workshop section by pipeline 22, from coking The remained ammonia of ammonia still process workshop section by pipeline 22 be used as vapour phase ammonia density diluent add two sections of desulphurization denitration sections, described two sections The bottom of desulphurization denitration section is connected by two sections of circulation fluid pipelines with two sections of 14 imports of circulating pump, and two sections of outlets of circulating pump 14 pass through Two sections of circulation fluid pipelines are connected with two-step cooling device 15, and two-step cooling device 15 passes through two sections of circulation fluid pipelines and two sections of desulphurization denitrations The top connection of section.Remained ammonia is sent to the ammonia still process of the ammonia still process workshop section of coking by pipeline by the spur outlet of two sections of circulating pumps 14 Tower 25.
In two sections of desulphurization denitration sections, the remained ammonia before coking ammonia still process workshop section ammonia still adds two sections of desulphurization denitrations Section, dilutes ammonia vapour phase concentration in the flue gas after one section of desulphurization denitration section.Most of remained ammonia passes through two sections of circulating pumps Two sections of recirculation coolers are sent into, after one section of recirculation cooler controls temperature, two are added from the top of one section of desulphurization denitration tower Section desulphurization denitration section, with entering from two sections of desulphurization denitration pars infrasegmentalises, the flue gases of cock oven from one section of desulphurization denitration section countercurrently connects Touch, on the one hand complete the removing of remaining sulfur dioxide and nitrogen oxides, on the other hand reduce the ammonia partial pressure in gas phase, control ammonia is escaped Ease.According to the principle of material balance, small part circulation fluid returns to the ammonia still of coking ammonia still process workshop section.The control of one section of desulphurization denitration section Temperature processed is 50-80 °C, and pH controls are 5.5-6.2.
Hydrogen peroxide, which is added, in one section of desulphurization denitration section, two sections of desulphurization denitration sections carries out oxidation.In Ta Neijia Enter hydrogen peroxide oxidation effect, improve denitration efficiency, can also reduce ozone usage, reduce operating cost.
The ammonia section of catching is connected with ammonium sulfate liquor pipeline 23, utilizes the ammonium sulfate liquor washing two-stage desulfurization purification of sulfuric acid workshop section Flue gas afterwards, ammonium sulfate liquor, which is washed after flue gas catches remaining ammonia, passes through pipeline return ammonium sulfate workshop section 24.Taken off by two sections of desulfurization Flue gas after nitre, ammonia section is caught into desulphurization denitration integrated tower top, and flue gas is washed using the acid mother liquid of ammonium sulfate workshop section, Acid mother liquid washing flue gas returns to ammonium sulfate workshop section after catching remaining ammonia.Catch ammonia section controlled at 50-70 °C.If pass through two After section desulphurization denitration, the ammonia content in flue gas is up to standard, this, which catches ammonia section, can be used as spare measure, not put into operation.
The physical demister is intercepted after power eliminates flue gas acid mist by centrifugal force and inertia, and flue gas is from desulfurization Discharge on 11 top of denitration integrated tower.Flue gas after catching ammonia section enters the demister at the top of desulphurization denitration integrated tower, leads to After crossing centrifugal force and inertia interception power elimination flue gas acid mist, flue gas is discharged at the top of desulphurization denitration integrated tower, into flue gas Reheater, after the low temperature exhaust heat heating using flue gas before desulphurization denitration, returns to chimney, high altitude discharge.Physical demister Temperature control be 50-60 °C.
The injector 18 uses venturi tube structure, and injector 18 is connected with external air duct 26, utilizes Venturi tube knot Oxidant of the air as circulation oxidator is incorporated herein in 18 circulation of the injector injection suction of structure.In circulation oxidator, lead to The suction introducing air that the circulation injection of circulation cycle pump produces is crossed, fully reaction is sufficiently mixed with ammonium liquid, by sulfurous therein Sour ammonium generates ammonium sulfate, and the mixed salt solution most at last containing ammonium sulfate and ammonium nitrate is sent to the ammonium sulfate workshop section of coking, Resource recovery Change product.Controlled at 50-100 °C in circulation oxidator, pH controls are 6.0-6.8.
The dilution air pipeline 29 is dilution air with the flue gas after waste heat recovery or purified flue gas, or It is mixed into inert gas in atmosphere, the mixed volume of the flue gas or inert gas is the 0-50% of air capacity;In heating gas In be mixed into low-heat value gas, such as blast furnace gas, vaporization coal gas and water coal gas dilution coal gas measure, mixed volume is heating gas amount 0-70%, reduce coke oven discharge flue gas in amount of nitrogen oxides, make coke oven discharge flue gas in amount of nitrogen oxides be 250- 550mg/M3。
Flue gases of cock oven temperature after 1 denitration process of denitration in the stove system is 220-350 °C, and flue gases of cock oven is sent into Waste heat boiler recycles flue gas high-temperature residual heat, and the waste heat of waste heat boiler recycling is used as producing steam, or is directly used in ammonia still process heating Distilled ammonia wastewater, or heating conduction oil, after recycling high-temperature residual heat, effluent gas temperature is down to 150-200 °C;Recycled by waste heat boiler Flue gas after high-temperature residual heat is sent into smoke re-heater recycling flue gases at low waste heat, the purification that desulphurization denitration integrated tower is discharged Flue gas is heated to 100-150 °C from 50-80 °C, and own temperature is down to 90-130 °C;Flue after recycling low temperature exhaust heat Gas is sent into scrubber by flue gas wind turbine, is removed wash cycle liquid from washing using cleaning circulation pump in scrubber Dirt device top spray into, with fed from below into flue gas counter current contacting, washing removing flue gas in dust impurity, flue gas into One step is cooled to 60-80 °C.The dust obtained after spray is enriched with scrubber bottom precipitation, is periodically discharged it, as Fixed-end forces.Wash cycle liquid can use clear water, the outer draining of available cycles, it is also possible to waste water after waste water or biochemical treatment after ammonia still process.
Flue gas after washing cools down is sufficiently mixed instead with the ozone from ozone generator in pipeline reactor Should, after the nitric oxide in flue gases of cock oven partly or entirely oxidation, it is sent into desulphurization denitration integrated tower and carries out at desulphurization denitration Reason.According to technique needs, this oxidation reactor, which may also placed in desulphurization denitration integrated tower, realizes oxidation reaction function.
The washing at the top of one section of desulphurization denitration section, concentrated ammonia liquor or coke oven gas desulfurization regenerator from coking ammonia still process workshop section Liquid adds one section of desulphurization denitration section, anti-with being sent into sulfur dioxide and nitrogen oxides in flue gases of cock oven from one section of desulphurization denitration section Should, the solution of generation ammonium sulfite and ammonium nitrate, most of ammonium salt solution is pumped into one section of recirculation cooler by one section of circulation, After one section of recirculation cooler controls temperature, one section of desulphurization denitration section is added from the top of one section of desulphurization denitration tower, and from one The flue gases of cock oven counter current contacting of section desulphurization denitration pars infrasegmentalis, completes desulphurization denitration process.According to the principle of material balance, few portion Divide ammonium liquid to be sent into circulation oxidator further to aoxidize.One section of desulphurization denitration section controlled at 50-80 °C, pH controls are 5.8- 6.5。
In circulation oxidator, by circulation cycle pump circulation injection produce suction, introduce air, fully with ammonium liquid Reaction is sufficiently mixed, ammonium sulfite therein is generated into ammonium sulfate, the mixed salt solution most at last containing ammonium sulfate and ammonium nitrate is sent Toward the ammonium sulfate workshop section of coking, Resource recovery product.Controlled at 50-80 °C in circulation oxidator, pH controls are 6.0- 6.8。
Technical indicator after present invention processing is as follows:
Index after gas cleaning
SO2: ≤50mg/Nm3
NOX: ≤100mg/Nm3
NH3:≤1mg/Nm3
Dust content:≤5mg/Nm3
Sulphuric acid mist content:≤5mg/Nm3
Although above-mentioned be described the embodiment of invention with reference to attached drawing, not to the scope of the present invention Limitation, on the basis of technical scheme, those skilled in the art, which need not make the creative labor, to be made Various modifications or deformation still within protection scope of the present invention.

Claims (5)

1. a kind of double ammonia process integration desulfurization denitration systems of coking flue gas two-part, including denitration in the stove system, chimney, waste heat Boiler, smoke re-heater, coke oven, it is characterized in that, further include flue gas wind turbine, scrubber, cleaning dust circulating pump, washing remove Dirt cooler, ozone generator, pipeline reactor, desulphurization denitration integrated tower, circulation oxidator, the denitration in the stove system pass through Dilution air pipeline and dilution gas piping are connected with coke oven, and coke oven is connected by coke oven flue gas pipeline with chimney, and chimney passes through Coke oven flue gas pipeline is connected with waste heat boiler, and waste heat boiler passes through flue and smoke re-heater after recovered flue gas high-temperature residual heat Connection, smoke re-heater are connected by flue after recycling low temperature exhaust heat with flue gas wind turbine, and flue gas blower and pipeline is with washing Deduster connection is washed, scrubber lower part is connected by liquid pipe with cleaning circulation pump, and cleaning circulation pump passes through lower part liquid Phase outlet conduit is connected with cleaning dust cooler, and cleaning dust cooler is connected with scrubber upper entrance pipeline, is washed Wash deduster to be connected with pipeline reactor by pipeline after cleaning dust, pipeline reactor passes through ozone pipeline and ozone generator Connection, pipeline reactor are connected by flue after reaction with desulphurization denitration integrated tower, the flue gas after washing cools down Reaction is sufficiently mixed in pipeline reactor with the ozone from ozone generator, by the nitric oxide part in flue gases of cock oven Or all after oxidation, it is sent into desulphurization denitration integrated tower and carries out desulphurization denitration processing;After desulphurization denitration integrated tower top is by purification Flue is connected with smoke re-heater, and smoke re-heater is connected by purifying smoke pipeline with chimney, discharges desulphurization denitration one The purifying smoke of body tower enters smoke re-heater, and 100-150 ° is increased to using the low temperature exhaust heat heating of flue gas before desulphurization denitration C returns to chimney, high altitude discharge;
The desulphurization denitration integrated tower includes one section of desulphurization denitration section, the two sections of desulphurization denitration sections at middle part of lower part, two sections of desulfurization The top of denitration section is equipped with and catches ammonia section, catches ammonia section top and is equipped with physical demister, one section of desulphurization denitration Duan Yunong ammonia The scrubbing ammonia waterpipe of waterpipe or raw coke oven gas desulfurization regeneration tail gas connects, the concentrated ammonia liquor pipeline and coking ammonia still process workshop section The connection of concentrated ammonia liquor pipeline, the scrubbing ammonia waterpipe is connected with the scrubbing ammonia waterpipe of raw coke oven gas desulfurization regeneration tail gas, The washing ammonium hydroxide of concentrated ammonia liquor or raw coke oven gas desulfurization regeneration tail gas from coking ammonia still process workshop section adds as the alkali source of desulphurization denitration Enter one section of desulphurization denitration section, one section of circulating pump is connected by one section of circulation ammonium liquid pipe road with desulphurization denitration integrated tower, one-step cooling Device is connected by one section of circulation ammonium liquid pipe road with one section of circulating pump, and one-step cooling device is taken off by one section of circulation ammonium liquid pipe road with desulfurization Nitre integrated tower connects, and one section of desulphurization denitration section of desulphurization denitration integrated tower is connected by ammonium liquid side line pipeline with circulation oxidator, The outlet of circulation cycle pump is connected by circulation cycle conduit upper with circulation oxidator top, the circulation cycle conduit upper Injector is equipped with close to the position on circulation oxidator top, the import of circulation cycle pump passes through circulation cycle pipeline lower part and circulation Oxidator bottom connects, and circulation cycle pump is molten by the ammonium sulfate after oxidation and ammonium nitrate mixed-ammonium salt by spur outlet and pipeline Liquid is sent to the ammonium sulfate workshop section Resource recovery product of coking or for complex acid;
Two sections of desulphurization denitration sections are connected with the remained ammonia from coking ammonia still process workshop section by pipeline, from coking ammonia still process work The diluent that the remained ammonia of section is used as vapour phase ammonia density by pipeline adds two sections of desulphurization denitration sections, two sections of desulphurization denitrations The bottom of section is connected by two sections of circulation fluid pipelines with two sections of pump inlets, and two sections of circulating-pump outlets pass through two sections of circulation liquid pipes Road is connected with two-step cooling device, and two-step cooling device is connected by two sections of circulation fluid pipelines with the top of two sections of desulphurization denitration sections, and two Remained ammonia is sent to the ammonia still of the ammonia still process workshop section of coking by pipeline by the spur outlet of section circulating pump;
The ammonia section of catching is connected with ammonium sulfate liquor pipeline, the flue gas after two sections of desulphurization denitrations, into desulphurization denitration one Ammonia section is caught on tower top, washs flue gas using the acid mother liquid of sulfuric acid workshop section, sulphur ammonium acid mother liquid washing flue gas catches remaining Ammonium sulfate workshop section is returned after ammonia, catch ammonia section controlled at 50-70 °C;
The physical demister is intercepted after power eliminates flue gas acid mist by centrifugal force and inertia, and flue gas is from desulphurization denitration Discharge on integrated tower top;Flue gas after catching ammonia section enters the physical demister at the top of desulphurization denitration integrated tower, leads to After crossing centrifugal force and inertia interception power elimination flue gas acid mist, flue gas is discharged at the top of desulphurization denitration integrated tower, into flue gas Reheater, after the low temperature exhaust heat heating using flue gas before desulphurization denitration, returns to chimney, high altitude discharge;The physical demisting The temperature control of device is 50-60 °C.
2. the double ammonia process integration desulfurization denitration systems of coking flue gas two-part as claimed in claim 1, it is characterized in that, it is described Injector uses venturi tube structure, and injector is connected with external air duct, is sprayed using the injector circulation of venturi tube structure Oxidant of the air as circulation oxidator is incorporated herein in suction, and the suction that the circulation injection pumped by circulation cycle produces introduces Air, the oxygen in air are fully sufficiently mixed reaction with ammonium liquid, and ammonium sulfite therein is generated ammonium sulfate, then will be contained The mixed salt solution of ammonium sulfate and ammonium nitrate is sent to the ammonium sulfate workshop section of coking, Resource recovery product, the circulation oxidator internal control Temperature processed is 50-80 °C, and pH controls are 6.0-6.8.
3. the double ammonia process integration desulfurization denitration systems of coking flue gas two-part as claimed in claim 1, it is characterized in that, it is described Dilution air pipeline is dilution air with the flue gas after waste heat recovery or purified flue gas, or is mixed into atmosphere lazy Property gas, the mixed volume of flue gas or inert gas is the 0-50% of air capacity;Low-heat value gas is mixed into heating gas, Low-heat value gas mixed volume is the 0-70% of heating gas amount, reduces the amount of nitrogen oxides in coke oven discharge flue gas, arranges coke oven The amount of nitrogen oxides gone out in flue gas is 250-550mg/m3.
4. the double ammonia process integration desulfurization denitration systems of coking flue gas two-part as claimed in claim 1, it is characterized in that, pass through Flue gases of cock oven temperature after denitration in the stove system denitration process is 220-350 °C, and flue gases of cock oven is sent into waste heat boiler recycling Flue gas high-temperature residual heat, the waste heat of waste heat boiler recycling are used as producing steam, or are directly used in ammonia still process heating distilled ammonia wastewater, or add Thermal conductivity deep fat, recycling high-temperature residual heat rear pass temperature degree are down to 150-200 °C;Cigarette after waste heat boiler recycles high-temperature residual heat Road pneumatic transmission enters smoke re-heater recycling flue gases at low waste heat, and the purification flue gas that desulphurization denitration integrated tower is discharged is from 50-80 ° C is heated to 100-150 °C, and own temperature is down to 90-130 °C;Flue gas after recycling low temperature exhaust heat passes through flue gas wind turbine Scrubber is sent into, is sprayed into wash cycle liquid from scrubber top using cleaning circulation pump in scrubber, With fed from below into flue gas counter current contacting, the dust impurity in washing removing flue gas, flue gas is further cooled to 60- 80°C。
5. the double ammonia process integration desulfurization denitration systems of coking flue gas two-part as claimed in claim 1, it is characterized in that, in institute One section of desulphurization denitration section, the two sections of desulphurization denitration sections stated add hydrogen peroxide and carry out oxidation.
CN201610293501.2A 2016-05-05 2016-05-05 The double ammonia process integration desulfurization denitration systems of coking flue gas two-part Active CN105797562B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610293501.2A CN105797562B (en) 2016-05-05 2016-05-05 The double ammonia process integration desulfurization denitration systems of coking flue gas two-part

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610293501.2A CN105797562B (en) 2016-05-05 2016-05-05 The double ammonia process integration desulfurization denitration systems of coking flue gas two-part

Publications (2)

Publication Number Publication Date
CN105797562A CN105797562A (en) 2016-07-27
CN105797562B true CN105797562B (en) 2018-05-15

Family

ID=56455411

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610293501.2A Active CN105797562B (en) 2016-05-05 2016-05-05 The double ammonia process integration desulfurization denitration systems of coking flue gas two-part

Country Status (1)

Country Link
CN (1) CN105797562B (en)

Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106268230A (en) * 2016-08-18 2017-01-04 山东铁雄冶金科技有限公司 A kind of waste heat of coke-oven flue gas reclaim and purify system and technique
CN106422702A (en) * 2016-10-31 2017-02-22 中钢集团鞍山热能研究院有限公司 Desulfuration, denitration and energy conservation integrated purification system for coke oven flue gas and control method of system
CN106621768A (en) * 2016-12-20 2017-05-10 亚太环保股份有限公司 Ammonia process of desulfurization integral purification device and method for acid gas sulfur recovery tail gas
US10919016B2 (en) * 2017-02-15 2021-02-16 General Electric Technology Gmbh Oxidation control for improved flue gas desulfurization performance
CN108970352A (en) * 2018-06-19 2018-12-11 山东师范大学 A kind of flue gas low-temperature denitration method
CN111068492B (en) * 2018-10-18 2022-12-02 中国石油化工股份有限公司 Coking tail gas treatment process and device
CN109210955B (en) * 2018-10-19 2024-03-26 上海孚旺炉业有限公司 Industrial furnace low temperature flue gas waste heat utilization and SOx/NOx removal white smoke integrated system

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5451250A (en) * 1994-05-11 1995-09-19 The Babcock & Wilcox Company Method of convert a double-loop flue gas desulfurization system to a single-loop system
CN104707454A (en) * 2015-03-27 2015-06-17 山东钢铁股份有限公司 Residual heat utilization and simultaneous desulfurization and denitrification system for tower type coke oven flue gas
CN104830351A (en) * 2015-04-28 2015-08-12 马鞍山市江海节能科技有限公司 Control system and method for reducing oxynitride in coke oven waste gas
CN105195005A (en) * 2015-10-21 2015-12-30 济南冶金化工设备有限公司 Dual-effect purification system for integrated treatment of coked fuel gas and ammonia containing wastewater
CN205815447U (en) * 2016-05-05 2016-12-21 济南冶金化工设备有限公司 The double ammonia process integration desulfurization denitration system of coking flue gas two-part

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5451250A (en) * 1994-05-11 1995-09-19 The Babcock & Wilcox Company Method of convert a double-loop flue gas desulfurization system to a single-loop system
CN104707454A (en) * 2015-03-27 2015-06-17 山东钢铁股份有限公司 Residual heat utilization and simultaneous desulfurization and denitrification system for tower type coke oven flue gas
CN104830351A (en) * 2015-04-28 2015-08-12 马鞍山市江海节能科技有限公司 Control system and method for reducing oxynitride in coke oven waste gas
CN105195005A (en) * 2015-10-21 2015-12-30 济南冶金化工设备有限公司 Dual-effect purification system for integrated treatment of coked fuel gas and ammonia containing wastewater
CN205815447U (en) * 2016-05-05 2016-12-21 济南冶金化工设备有限公司 The double ammonia process integration desulfurization denitration system of coking flue gas two-part

Also Published As

Publication number Publication date
CN105797562A (en) 2016-07-27

Similar Documents

Publication Publication Date Title
CN105797562B (en) The double ammonia process integration desulfurization denitration systems of coking flue gas two-part
CN205815447U (en) The double ammonia process integration desulfurization denitration system of coking flue gas two-part
CN200998639Y (en) Concentrated crystallization and absorbed oxidation combined type ammonia process desulfuration tower
CN106430116B (en) A method of the sulphur-bearing waste solution extracting sulfuric acid generated using coal gas wet oxidation method
CN100427391C (en) Tail gas treatment and reutilization for calcium carbide stove
EP1950176A2 (en) Process for removing contaminants from gas streams
CN206680184U (en) A kind of system that high-concentration sulfuric acid is continuously and stably produced using sour gas
CN102205202A (en) Processing method for acid gas containing H2S
CN103072957A (en) Technology for preparing sulfuric acid
CN105749704B (en) A kind of ammonium sulfite desulphurization system and technique
CN104560223B (en) A kind of gas desulfurizer and method thereof
CN106379868A (en) Method for preparing sulfuric acid by burning sulfur-containing waste liquid
CN205653162U (en) System for sulphuric acid is prepared to sulphur waste liquid that contains that utilizes coal gas wet oxidation process to produce
CN110314505B (en) Device and method for treating ammonia-containing tail gas in ammonium drying section in alkali industry
CN110282606B (en) Wet processing system and process for aqueous sulfur paste and desulfurization waste liquid
CN107983133A (en) A kind of system and method for flue gas wet type combined desulfurization and denitration
CN102151475B (en) Two-tower ammonia method desulfurization device and method
CN207016486U (en) A kind of system that sulfuric acid is produced using sour gas
CN104056538B (en) Flue gas purifying system and method with integration of desulfurization and denitrification
CN211274164U (en) Ammonia-containing tail gas treatment device for dry ammonium workshop section in alkali industry
CN107930387A (en) A kind of coke oven flue gas integration desulfurization denitration system
CN109517630B (en) Process and system for deamination production of ammonium sulfate by coke oven gas ammonium sulfite method
CN104190228B (en) A kind of composite efficient energy-saving ammonia process desulfuration tower
CN108434948A (en) A kind of acid gas absorbs oxidizing tower and its working method
CN108261870A (en) A kind of desulfurizer and its sulfur method for refining oil high-temperature flue gas

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
PE01 Entry into force of the registration of the contract for pledge of patent right

Denomination of invention: Integrated desulfurization and denitrification system for coking flue gas using two-stage double ammonia process

Effective date of registration: 20230317

Granted publication date: 20180515

Pledgee: Postal Savings Bank of China Limited Jinan Changqing District sub branch

Pledgor: JINAN METALLURGY CHEMICAL EQUIPMENT CO.,LTD.

Registration number: Y2023980035136

PE01 Entry into force of the registration of the contract for pledge of patent right