CN108211759A - The processing method of the salt slurry waste generated in chlorine industry and its application - Google Patents

The processing method of the salt slurry waste generated in chlorine industry and its application Download PDF

Info

Publication number
CN108211759A
CN108211759A CN201611201151.9A CN201611201151A CN108211759A CN 108211759 A CN108211759 A CN 108211759A CN 201611201151 A CN201611201151 A CN 201611201151A CN 108211759 A CN108211759 A CN 108211759A
Authority
CN
China
Prior art keywords
salt slurry
salt
processing method
powder
slurry liquid
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.)
Pending
Application number
CN201611201151.9A
Other languages
Chinese (zh)
Inventor
饶辉凯
蒲文晶
王俊
杨晓明
钟大辉
盛光
刘成刚
李明
李一明
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.)
China Petroleum and Natural Gas Co Ltd
Original Assignee
China Petroleum and Natural Gas 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 China Petroleum and Natural Gas Co Ltd filed Critical China Petroleum and Natural Gas Co Ltd
Priority to CN201611201151.9A priority Critical patent/CN108211759A/en
Publication of CN108211759A publication Critical patent/CN108211759A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • B01D53/501Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound
    • B01D53/502Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound characterised by a specific solution or suspension

Abstract

The present invention relates to the processing methods of salt slurry waste generated in a kind of chlorine industry, comprise the steps of:Salt slurry liquid is subjected to washing process, obtains supernatant and concentration salt slurry liquid;Concentration salt slurry liquid is subjected to filter-press dehydration processing, obtains filtrate and dehydration salt slurry;Screening process is ground to dehydration salt slurry, obtains powder salt slurry.After salt slurry liquid is by method provided by the invention processing, alternative part commodity desulfurizing agent calcium lime powder, for boiler smoke semi-dry desulphurization.Salt slurry liquid process flow is short in the present invention, method is simple to operation, processing cost is low, processing procedure is discharged without " three wastes ", solve the disposal difficulties of chlorine industry salt slurry liquid, waste recycling is realized again, need not be changed original sulfur removal technology using the desulfurizing agent, be reduced the desulphurization cost of boiler smoke.

Description

The processing method of the salt slurry waste generated in chlorine industry and its application
Technical field
The present invention relates to a kind of application of solid waste salt slurry in boiler flue gas desulfurization of chlorine industry, and in particular to Part commodity desulfurizing agent calcium lime powder is substituted for boiler smoke semi-dry desulphurization for the salt slurry after a kind of be effectively treated, and belongs to solid Body utilization of waste as resource field and field of environment protection.
Background technology
Chlorine industry produces NaOH, Cl by being electrolysed the method for saturation NaCl solution2And H2, and produced using them as raw material A series of chemical products.Chlorine industry is removed using crude salt as raw material, in the saturation NaCl solution that crude salt is obtained by salt dissolving mainly to be contained Outside NaCl, also containing a small amount of Ca2+And Mg2+, if do not removed it, in alkali producing process, they can form precipitation, be attached to and set It on standby or duct wall or remains in alkali, influence normal operating or reduces product purity, therefore needed before being electrolysed to obtained full Removal Ca therein is refined with NaCl solution2+And Mg2+
In industrial production, usually by adding double alkali NaOH-Na2CO3Method saturation NaCl solution is refined, at this During one, a certain amount of solid waste salt slurry liquid is given off.Due to crude salt place of production difference, impurity content is different, salt slurry The discharge capacity of slurries is also different, and the discharge capacity for usually producing 1 ton of caustic soda salt slurry liquid is 0.4~0.8m3.Salt slurry liquid moisture content 80% or so, the main component of butt is CaCO3、Mg(OH)2With Ca (OH)2, also containing a small amount of Na2CO3With NaCl etc..Mesh Before, the country is to note well or landfill as solid waste to the main method of disposal of salt slurry liquid, this method not only waste of resource, but also Environment is polluted, while also needs to inject capital into, increases the operating cost of enterprise.
Contain a large amount of SO in the flue gas of discharged from coal-fired boiler2.Flue gas desulfurization is generally by desulfurizing agent and SO2Reaction life Into stable compound by SO2Immobilization.It is divided into wet method, semidry method by how much sulfur removal technologies of desulfurizing agent moisture content and does Method.Can have much as the substance of desulfurizing agent, what is be commonly used is resourceful calcium type desulfurizing agent, i.e. lime stone or stone Ash, other desulfurizing agents also have caustic soda, soda ash, magnesium hydroxide, ammonia and seawater etc..
The main component of salt slurry butt is the active ingredient of desulfurizing agent, as can by salt slurry for boiler flue gas desulfurization, a side Face reduces discharge of the salt slurry as solid waste, on the other hand can also realize the recycling of salt slurry, has certain environment Benefit and economic benefit.
Patent application No. is 201310391191.4 is after lime-flue gas method two level salt slurry is washed, and is added with water to solid Content is 5~30% slurries, then the organic additive of salt slurry quality 0.05~1% is added in into slurries, after mixing It substitutes agstone and is used for smoke-gas wet desulfurization;Patent application No. is 201310389205.9 is to wash two alkaline process salt slurries Afterwards, the slurries that solid content is 5~30% are added with water to, then the organic acid addition of salt slurry quality 0.05~1% is added in into slurries Agent substitutes agstone and is used for smoke-gas wet desulfurization after mixing;Patent CN101219328A is modulated into salt slurry and water Slurries absorbing sulfur dioxide in flue simultaneously aoxidizes, and absorbs serum recycle Reusability, and control liquid-gas ratio is 6~15L/m3, pH value It is 5~7.
These inventions are all using salt slurry as raw material, for smoke-gas wet desulfurization.The present invention is the salt using salt slurry liquid as raw material Slurry liquid is used for the semidry method of flue gas after being effectively treated after uniformly being mixed according to a certain percentage with commodity desulfurizing agent calcium lime powder Desulfurization does not need to change original semi-dry desulphurization facility and sulfur removal technology.
Invention content
The purpose of the present invention is to provide a kind of methods of disposal of the salt slurry liquid of chlorine industry, and salt slurry liquid is through effectively place After reason, alternative part commodity desulfurizing agent calcium lime powder, for boiler smoke semi-dry desulphurization.Both chlorine industry salt slurry had been solved The disposal difficulties of slurries, and waste recycling is realized, reduce the desulphurization cost of boiler smoke.
The present invention discloses the processing method of salt slurry waste generated in a kind of chlorine industry, comprises the steps of:
(1) the salt slurry liquid by three layers of mud cleaning bucket discharge carries out washing process, obtains supernatant and concentration salt slurry liquid;
(2) above-mentioned concentration salt slurry liquid is transported to progress filter-press dehydration processing in plate and frame filter press, obtains filtrate and taken off Water salt slurry;
(3) screening process is ground to above-mentioned dehydration salt slurry, obtains powder salt slurry.
The processing method of salt slurry of the present invention, wherein, in the step (1), the volume ratio of salt slurry liquid and water is excellent It is selected as 1:1~2, washing times are preferably 1~2 time.
The processing method of salt slurry of the present invention, wherein, in step (1), Na in the concentration salt slurry liquid+、K+With Cl-Percentage composition based on salt slurry butt is preferably respectively Na+< 0.5%, K+< 0.1%, Cl-< 0.4%.
The processing method of salt slurry of the present invention, wherein, in step (1), preferably described supernatant is back to salt dissolving tank It is dissolved for crude salt, recycles salinity therein.
The processing method of salt slurry of the present invention, wherein, in step (2), the moisture content of the dehydration salt slurry is preferably 10~15%.
The processing method of salt slurry of the present invention, wherein, in step (2), preferably described filtrate is back to salt dissolving tank use It is dissolved in crude salt, recycles salinity therein.
The processing method of salt slurry of the present invention, wherein, in the step (3), the preferred grain size of powder salt slurry<1mm.
The processing method of salt slurry of the present invention, wherein, in the step (3), 90% powder salt slurry grain size is preferred In 0.5~0.9mm.
The powder salt slurry that processing method of the present invention obtains preferably is preparing the semi-dry desulphurization as boiler smoke With the application in desulfurizing agent.
Application of the present invention, wherein, the weight ratio of the powder salt slurry and commodity desulfurizing agent calcium lime powder is preferably 0.2~0.4:1.
Using three layers of mud cleaning bucket, washing fresh water is inversely contacted with salt mud every time washes washing process of the present invention It washs, once washing divides three phases to carry out, i.e., often washed once, and has actually carried out triphasic washing, washing effect is good, more has Conducive to the wash-off of sodium, potassium, chlorion in salt slurry liquid.
Present invention concentration salt slurry dewatering slurries process is dehydrated, dehydration 20 using plate and frame filter press under -0.8 atmospheric pressure Minute can reach 10~15% moisture content, and the dehydration salt slurry of gained is directly entered grinding screening machine, is carried out after grinding Screening, oversize return to system and are ground again again.
In the present invention, the moisture content of dehydration salt slurry is preferably 10~15% after filter-press dehydration processing, this moisture content It is to be more advantageous to required by subsequent process of lapping and moisture content as semi-dry desulphurization agent addition agent.
In the present invention, it is preferred to the grain size of 90% powder salt slurry, in 0.5~0.9mm, this particle size is that semidry method takes off Particle size required by sulphur agent, grain size are more than 0.9mm, and desulfuration efficiency declines;Grain size is less than 0.5mm, in flue gas after desulfurization Dust concentration can bigger.
The content of magnesium hydroxide is higher in the powder salt slurry of the present invention, due to magnesium hydroxide and a kind of good desulfurization Agent, and magnesium hydroxide has hygroscopicity, is more advantageous to the progress of sweetening process, i.e. and salt slurry of the invention is added to commodity desulfurization Generated increased desulfurization benefit part can be attributed to the presence of magnesium hydroxide in powder salt slurry in agent.
The powder salt slurry of the present invention can also directly as desulfurizing agent for flue gas desulfurization, but directly as desulfurizing agent, Desulfuration efficiency is relatively low, below 70%;With commodity desulphurizer mixing desulfurization, in the case where various operating modes are constant, desulfuration efficiency More than 6% can be improved, total desulfuration efficiency reaches more than 92%.The powder salt slurry of the present invention exists with the mixing ratio of commodity desulfurizing agent 0.4:When less than 1, desulfurization effect increases with the increase of mixing ratio, when more than 0.4:When 1, desulfuration efficiency does not increase again substantially Add.
The salt slurry of the present invention has catalytic and hygroscopicity, and the salt slurry of the present invention is added in commodity desulfurizing agent, can be increased Add more than 6% desulfurization benefit.
In the present invention, the split salt slurry of the magnesium hydroxide containing high-content is after commodity desulphurizer mixing for desulfurization When completely without the device for changing original calcium desulfurizing.
Beneficial effects of the present invention:
(1) present invention gives birth to by the solid waste salt slurry liquid of chlorine industry discharge through being effectively treated with commodity desulfurizing agent For boiler smoke semi-dry desulphurization after pulverized limestone mixing, not only solved the disposal difficulties of chlorine industry salt slurry liquid, but also realize Waste recycling reduces the desulphurization cost of flue gas.
(2) salt slurry liquid process flow is short, and method is simple to operation, and processing cost is low, supernatant and dehydration after washing Filtrate recycle dissolved in the salt dissolving tank of device for crude salt, recycle salinity therein, processing procedure is discharged without " three wastes ".
(3) present invention, without changing original sulfur removal technology, takes off without being transformed to original semidry process desulfurizer Sulphur ash is disposed by original processing method.
Specific embodiment
It elaborates below to the embodiment of the present invention:The present embodiment is carried out lower based on the technical solution of the present invention Implement, give detailed embodiment and process, but protection scope of the present invention is not limited to following embodiments, following implementation The technological parameter of actual conditions is not specified in example, usually according to normal condition.
Embodiment 1:
By the salt slurry liquid of three layers of mud cleaning bucket discharge in certain enterprise's electrolysis unit refining crude salt unit by volume 1:1 adds water Agitator treating 2 times, Na in salt slurry liquid+Content be 0.03%, K+Content be 0.01%, Cl-Content for 0.03%, wash It washs the supernatant after precipitation and is back to salt dissolving tank for crude salt dissolving, recycle salinity therein.Salt slurry liquid after washing is defeated Plate and frame filter press is sent to, under the pressure of 0.4MPa, filter-press dehydration is after 15 minutes, CaCO in salt slurry3Content be 49.8%, Mg (OH)2Content for 25.9%, moisture content 12%, insoluble substance content is 10.6%, and the salts substances of dissolving are 1.5%.After the dewatered ground screening of salt slurry, all salt slurry grain sizes are in 0.5~0.9mm.
Through the above method treated salt slurry by weight 0.3:1 uniformly mixed with commodity desulfurizing agent calcium lime powder after formed New desulfurizing agent, with Mr. Yu enterprise fire coal boiler fume semi-dry desulphurization.Exhaust gas volumn after electric precipitation is 136000Nm3/ h, cigarette SO in gas2A concentration of 1680mg/Nm3, desulfurizing tower entrance flue gas temperature is 149 DEG C, using humidification cycle fluid bed outside Desulphurization half Dry desulfurizing process, control Ca/S are 1.4, and Desulphurization recycle ratio is 150, and the flue gas after desulfurization discharges after bag-type dust, outside Smoke discharging SO2A concentration of 131mg/Nm3, desulfurizing tower exit flue-gas temperature is 77 DEG C, smoke desulfurization efficiency 92.2%.
Embodiment 2:
By the salt slurry liquid of three layers of mud cleaning bucket discharge in certain enterprise's electrolysis unit refining crude salt unit by volume 1:1 adds water Agitator treating 1 time, the Na in salt slurry liquid+Content be 0.04%, K+Content be 0.01%, Cl-Content for 0.04%, Supernatant after washing precipitation is back to salt dissolving tank and is dissolved for crude salt, recycles salinity therein.By the salt slurry liquid after washing Plate and frame filter press is transported to, under the pressure of 0.4MPa, filter-press dehydration is after 18 minutes, CaCO in salt slurry3Content for 50.8%, Mg(OH)2Content for 26.3%, moisture content 10.5%, insoluble substance content is 10.7%, and the salts substances of dissolving are 1.5%.After the dewatered ground screening of salt slurry, all salt slurry grain sizes are in 0.5~0.9mm.
Through the above method treated salt slurry by weight 0.4:1 uniformly mixed with commodity desulfurizing agent calcium lime powder after formed New desulfurizing agent, for 1 same fire coal boiler fume semi-dry desulphurization of embodiment.Exhaust gas volumn after electric precipitation is 136000Nm3/ h, SO in flue gas2A concentration of 1680mg/Nm3, desulfurizing tower entrance flue gas temperature is 149 DEG C, is increased using outside Desulphurization Wet circulating fluid bed semi-drying method sulfur removal technology, control Ca/S are 1.4, and Desulphurization recycle ratio is 150, and the flue gas after desulfurization is through cloth bag It is discharged after dedusting, discharged gas fume SO2A concentration of 124mg/Nm3, desulfurizing tower exit flue-gas temperature is 76 DEG C, smoke desulfurization efficiency It is 92.6%.
As seen from the above-described embodiment, because the powder salt slurry of the present invention has moisture retention and catalytic, in the powder of the present invention Body salt slurry is added to as additive in commodity desulfurizing agent, and above two property can improve desulfurization benefit, therefore desulfurization ratio can To be less than 1.5, indirectly for saved the consumption of desulfurizing agent, realize waste recycling, use powder salt slurry and the quotient of the present invention The mixture of product desulfurizing agent need not change original sulfur removal technology when as desulfurizing agent, reduce the desulphurization cost of boiler smoke.

Claims (10)

1. the processing method of salt slurry waste generated in a kind of chlorine industry, comprises the steps of:
(1) the salt slurry liquid by three layers of mud cleaning bucket discharge carries out washing process, obtains supernatant and concentration salt slurry liquid;
(2) above-mentioned concentration salt slurry liquid is transported to progress filter-press dehydration processing in plate and frame filter press, obtains filtrate and dehydration salt Mud;
(3) screening process is ground to above-mentioned dehydration salt slurry, obtains powder salt slurry.
2. the processing method of salt slurry as described in claim 1, which is characterized in that in the step (1), salt slurry liquid and water Volume ratio is 1:1~2, washing times are 1~2 time.
3. the processing method of salt slurry as described in claim 1, which is characterized in that in step (1), in the concentration salt slurry liquid Na+、K+And Cl-Percentage composition based on salt slurry butt is respectively Na+< 0.5%, K+< 0.1%, Cl-< 0.4%.
4. the processing method of salt slurry as described in claim 1, which is characterized in that in step (1), being back to of supernatant Salt tank dissolves for crude salt, recycles salinity therein.
5. the processing method of salt slurry as described in claim 1, which is characterized in that described to be dehydrated the aqueous of salt slurry in step (2) Rate is 10~15%.
6. the processing method of salt slurry as described in claim 1, which is characterized in that in step (2), the filtrate is back to salt dissolving Bucket dissolves for crude salt, recycles salinity therein.
7. the processing method of salt slurry as described in claim 1, which is characterized in that in the step (3), the grain size of powder salt slurry <1mm。
8. the processing method of salt slurry as claimed in claim 7, which is characterized in that in the step (3), 90% powder salt slurry Grain size is in 0.5~0.9mm.
9. the powder salt slurry that the processing method described in claim 1-8 obtains is preparing the semi-dry desulphurization use as boiler smoke Application in desulfurizing agent.
10. application as claimed in claim 9, which is characterized in that the weight of the powder salt slurry and commodity desulfurizing agent calcium lime powder Amount is than being 0.2~0.4:1.
CN201611201151.9A 2016-12-22 2016-12-22 The processing method of the salt slurry waste generated in chlorine industry and its application Pending CN108211759A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201611201151.9A CN108211759A (en) 2016-12-22 2016-12-22 The processing method of the salt slurry waste generated in chlorine industry and its application

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201611201151.9A CN108211759A (en) 2016-12-22 2016-12-22 The processing method of the salt slurry waste generated in chlorine industry and its application

Publications (1)

Publication Number Publication Date
CN108211759A true CN108211759A (en) 2018-06-29

Family

ID=62656353

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201611201151.9A Pending CN108211759A (en) 2016-12-22 2016-12-22 The processing method of the salt slurry waste generated in chlorine industry and its application

Country Status (1)

Country Link
CN (1) CN108211759A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110563426A (en) * 2019-10-21 2019-12-13 河南城建学院 Steam-cured high-strength brick prepared from mine salt mud and preparation method thereof
CN112125416A (en) * 2020-08-18 2020-12-25 中盐金坛盐化有限责任公司 Technology for washing salt mud by lime flue gas method
CN112456832A (en) * 2020-12-09 2021-03-09 泰安燊豪化工有限公司 Treatment method of salt mud containing high calcium sulfate
CN114873890A (en) * 2022-04-12 2022-08-09 博华工程技术有限公司 Treatment process for semi-dry salt mud generated by wastewater treatment by doping desulfurizer
CN115321776A (en) * 2022-09-22 2022-11-11 中国轻工业长沙工程有限公司 Comprehensive recycling process for waste residue and waste water in chlor-alkali industry

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4990677A (en) * 1972-12-29 1974-08-29
CN101219328A (en) * 2007-10-08 2008-07-16 史汉祥 Sulphur dioxide salty mud absorbent
CN101274206A (en) * 2007-12-25 2008-10-01 江苏省井神盐业有限公司 Method for producing sulfur absorbing agent by 'salty mud'
CN103551015A (en) * 2013-08-31 2014-02-05 中盐金坛盐化有限责任公司 Sulfur dioxide absorbent prepared from two-alkali salt slurry

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4990677A (en) * 1972-12-29 1974-08-29
CN101219328A (en) * 2007-10-08 2008-07-16 史汉祥 Sulphur dioxide salty mud absorbent
CN101274206A (en) * 2007-12-25 2008-10-01 江苏省井神盐业有限公司 Method for producing sulfur absorbing agent by 'salty mud'
CN103551015A (en) * 2013-08-31 2014-02-05 中盐金坛盐化有限责任公司 Sulfur dioxide absorbent prepared from two-alkali salt slurry

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110563426A (en) * 2019-10-21 2019-12-13 河南城建学院 Steam-cured high-strength brick prepared from mine salt mud and preparation method thereof
CN110563426B (en) * 2019-10-21 2021-12-21 河南城建学院 Steam-cured high-strength brick prepared from mine salt mud and preparation method thereof
CN112125416A (en) * 2020-08-18 2020-12-25 中盐金坛盐化有限责任公司 Technology for washing salt mud by lime flue gas method
CN112125416B (en) * 2020-08-18 2022-11-15 中盐金坛盐化有限责任公司 Technology for washing salt mud by lime flue gas method
CN112456832A (en) * 2020-12-09 2021-03-09 泰安燊豪化工有限公司 Treatment method of salt mud containing high calcium sulfate
CN114873890A (en) * 2022-04-12 2022-08-09 博华工程技术有限公司 Treatment process for semi-dry salt mud generated by wastewater treatment by doping desulfurizer
CN115321776A (en) * 2022-09-22 2022-11-11 中国轻工业长沙工程有限公司 Comprehensive recycling process for waste residue and waste water in chlor-alkali industry

Similar Documents

Publication Publication Date Title
CN108211759A (en) The processing method of the salt slurry waste generated in chlorine industry and its application
CN101391794B (en) Novel method for preparing light calcium carbonate by recovering solid white slime through alkaline pulping
CN101274206A (en) Method for producing sulfur absorbing agent by &#39;salty mud&#39;
CN104028085B (en) Flue gas desulfurization technology based on iron ore sintering process
CN106242003A (en) A kind of organic-inorganic composite efficient flocculant and preparation method thereof
CN1989292A (en) Method for black liquor treatment
CN102161495A (en) Method for recycling soda waste mud from soda plant
CN101823822A (en) Method for treating waste brine sludge of soda by hydrochloric acid
CN102806004A (en) Magnesium desulfurization byproduct recovery process
CN103157437A (en) Filter aid and regeneration method thereof
CN103626205B (en) Method for separating potassium sulfate from ammonium sulfate
CN103480265B (en) One utilizes magnesia to administer SO 2waste gas reclaims the method for byproduct simultaneously
CN112174093B (en) Method for producing bleaching powder by using carbide slag
CN101830584A (en) Method for processing and forming distilled waste liquid of calcined soda with hydrochloric acid
CN102001687B (en) Method for preparing calcium chloride with co-produced sodium chloride and gypsum by using sodium carbonate distillation waste liquor
RU2471556C1 (en) Method of treatment of used regenerants of sodium cation-exchange filter salts
CN101823736A (en) Method for co-production of calcium carbonate and sodium silicate in preparation of light magnesium carbonate by chlor-alkali brine sludge
CN214866045U (en) Automatic grading treatment application device for high-content calcium sulfate salt mud
KR20100131895A (en) Method for absorbing co2 in the emission gas and recycling calcium carbonate by utilizing eluate of coal ash in the anthracite-fired fluidized-bed power plant
CN112919503A (en) Zero-discharge process for desulfurization wastewater and desulfurization slag
CN101837997B (en) Method for preparing magnesium carbonate and co-producing sodium carbonate and calcium sulfate from soda ash salt mud
CN101823737B (en) Method for co-production of ultra-fine calcium carbonate and sodium silicate in preparation of light magnesium carbonate by chlor-alkali brine sludge
CN109331620A (en) A kind of calcium and magnesium composite desulfurizing agent and its calcium and magnesium compound desulfurizing process
CN220098580U (en) Alkali residue solid waste innocent treatment device
CN109626795A (en) A kind of mud dewatering method containing powdered carbon of sintering device flue gas purification Wastewater from Acid Preparation

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20180629