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CN103588340A - Method for treating sodium-alkali desulfurization waste liquid by causticization-acidification method - Google Patents

Method for treating sodium-alkali desulfurization waste liquid by causticization-acidification method Download PDF

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CN103588340A
CN103588340A CN201310609080.6A CN201310609080A CN103588340A CN 103588340 A CN103588340 A CN 103588340A CN 201310609080 A CN201310609080 A CN 201310609080A CN 103588340 A CN103588340 A CN 103588340A
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sodium
waste liquid
filtrate
calcium
thiocyanate
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CN103588340B (en
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崔平
江静
张超群
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Anhui University of Technology AHUT
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Abstract

本发明公开一种用苛化-酸化法处理钠碱法脱硫废液的方法,属于脱硫废液处理技术领域。本发明方法包括废液预处理除杂质、加热分解脱色、氧化苛化-分离、酸化-分离、蒸发浓缩以及冷却结晶-分离工艺过程。本发明方法用于处理钠碱法脱除煤气或其他气体中硫化氢、氰化氢工艺产生的脱硫废液,该方法能够在常温条件下,通过加热分解、氧化、苛化将钠碱法脱硫废液中的硫代硫酸钠、多硫化钠、硫酸钠转化成亚硫酸钙、硫化钙和硫酸钙沉淀,同时提取高纯度的碳酸钠和硫氰酸钠,回收钠碱重新返回脱硫系统循环,降低脱硫操作的碱耗。

Figure 201310609080

The invention discloses a method for treating sodium-alkali desulfurization waste liquid by a causticization-acidification method, and belongs to the technical field of desulfurization waste liquid treatment. The method of the invention comprises waste liquid pretreatment to remove impurities, heat decomposition and decolorization, oxidative causticization-separation, acidification-separation, evaporation concentration and cooling crystallization-separation process. The method of the present invention is used to treat the desulfurization waste liquid produced by the process of removing hydrogen sulfide and hydrogen cyanide in coal gas or other gases by sodium-alkali method, and the method can desulfurize the sodium-alkali method through thermal decomposition, oxidation and causticization under normal temperature conditions Sodium thiosulfate, sodium polysulfide, and sodium sulfate in the waste liquid are converted into calcium sulfite, calcium sulfide, and calcium sulfate precipitates, and high-purity sodium carbonate and sodium thiocyanate are extracted at the same time, and the recovered sodium alkali is returned to the desulfurization system for circulation. Reduce the alkali consumption of desulfurization operation.

Figure 201310609080

Description

With causticization-acidization, process the method for soda method desulfurization waste liquor
Technical field:
The invention belongs to desulfurization waste liquor processing technology field, be specifically related to a kind of method of processing soda method desulfurization waste liquor with causticization-acidization.
Background technology:
In the chemical fields such as Coal Chemical Industry, petrochemical complex and Sweet natural gas, gas adopts Wet Catalytic Oxidation Method technique to remove hydrogen sulfide, the feature of its technique is that the hydrogen sulfide of absorption is catalytically converted into sulfur foam, separate out the water of equimolecular number, due to system, there is element or the compounds such as prussic acid, oxygen, sulphur, alkali simultaneously, therefore the side reaction of salt occurs to generate simultaneously.The secondary salt generating during as alkali source with sodium carbonate is mainly Sodium Thiocyanate 99, Sulfothiorine, sodium polysulphide, sodium sulfate etc., the accumulation of side reaction salt declines the receptivity of doctor solution, so outer row partly contains the doctor solution (being commonly called as desulfurization waste liquor) of secondary salt continuously, and supplementary new doctor solution maintains quality and the sweetening power of doctor solution to alleviate the load of secondary salt.Outer row must be through processing containing the desulfurization waste liquor of secondary salt, and desulfurization waste liquor contaminate environment and the water body of untreated direct discharge, have strong corrosive power to hardware.The treatment process of existing soda method desulfurization waste liquor is mainly as follows:
1, the method for treating waste liquid matching with modified ADA desulfurizer technique, is to adopt substep evaporating, concentrating and crystallizing method to extract Sulfothiorine and Sodium Thiocyanate 99 coarse products, and the method is also called " freezing Steppecd crystallization " technique.The method feature is first to carry out vacuum evaporation, then Vacuum Heat filters except carbonic acid sodium impurity, filtrate is cooled to-5 ℃ with refrigerated water, separate out Sulfothiorine crystallization, through centrifugation, extract the thick product of Sulfothiorine, remove filtrate after Sulfothiorine as the raw material that extracts Sodium Thiocyanate 99, by the same method, extract rough Sodium Thiocyanate 99.The method requires to adopt the refrigerated water cooling concentration liquid of-5 ℃ to make Sulfothiorine crystallization, so processing unit configuration is many, needs auxiliary construction refrigerator device, long flow path, power consumption is high, and concentrated solution forms complicated, and crystallized product impurity is many, be difficult for primary crystallization acquisition straight product.
2, Japan's " ammonia type-Taka Haake this " sulfur removal technology mainly adopts the uncommon Luo Hakesi process for treating waste liquor that is called " wet oxidation process ", and final product is ammonium sulfate.And Japan's " sodium type-Taka Haake this " sulfur removal technology liquid waste disposal is mainly to adopt " reduction combustion method " burning waste liquid and sulphur, final product is sulfuric acid and sodium carbonate.The shortcoming of the method is that process for treating waste liquor route is long, and added value of product is not high, and production equipment construction cost and maintenance cost are high, so overall economic benefit is low, in waste liquid, more valuable Sodium Thiocyanate 99 does not reclaim in addition.
Summary of the invention:
The present invention is directed to the problem existing in existing soda method desulfurization waste liquor treatment process, a kind of method of processing soda method desulfurization waste liquor with causticization-acidization is provided.
A kind of method concrete steps with causticization-acidization processing soda method desulfurization waste liquor provided by the present invention are as follows:
(1) at normal temperatures and pressures, use entrained solid impurity in the sorbing material fractionation by adsorption soda method desulfurization waste liquors such as coke or gac;
(2) the soda method desulfurization waste liquor after described step (1) is processed is through evaporation concentration, make unsettled Sulfothiorine and sodium polysulphide in waste liquid be decomposed into respectively S-WAT and sodium sulphite, and when separating out elemental sulfur, to being blown into pressurized air in described soda method desulfurization waste liquor, carry out oxidizing reaction, make through decomposing the S-WAT and the sodium sulphite that produce, to be oxidized to sodium sulfate in described soda method desulfurization waste liquor, the temperature of described thermolysis-oxidizing reaction is 85~125 ℃, the volume that described pressurized air is blown into is 20~160 times of described soda method desulfurization waste liquor volume,
(3) step (2), after the soda method desulfurization waste liquor filtering and impurity removing after thermolysis-oxidizing reaction is processed, is added to milk of lime Ca (OH) in filtrate 2carry out causticizing reaction, the temperature of causticizing reaction is 85~125 ℃, makes the sodium sulfate Na in filtrate 2sO 4and remaining S-WAT Na 2sO 3with sodium sulphite Na 2s changes into respectively calcium sulfate and calcium sulfite and sulfurated lime precipitation, and sodium ion reacts with hydroxide ion and generates sodium hydroxide, by after calcium sulfite, sulfurated lime and calcium sulfate filtering, and the filtrate that obtains being rich in Sodium Thiocyanate 99 and sodium hydroxide;
(4) filtrate of being rich in Sodium Thiocyanate 99 and sodium hydroxide step (3) being obtained is placed in acidifier, in described acidifier, be blown into the stack gas through purifying, make carbonic acid gas in described stack gas with described in be rich in the sodium hydroxide generation neutralization reaction in the filtrate of Sodium Thiocyanate 99 and sodium hydroxide, reaction product is sodium bicarbonate, the sodium bicarbonate that neutralization reaction generates further reacts generation sodium carbonate with the sodium hydroxide that described step (3) causticizing reaction generates, simultaneously, carbonic acid gas in described purifying flue gas with described in be rich in calcium hydroxide reaction residual in the filtrate of Sodium Thiocyanate 99 and sodium hydroxide and generate precipitation of calcium carbonate, reacted filtrate is removed by filter to the acidizing fluid that obtains being rich in Sodium Thiocyanate 99 and sodium carbonate after precipitation of calcium carbonate,
(5) acidizing fluid that is rich in Sodium Thiocyanate 99 and sodium carbonate step (4) being obtained is put into the first crystallisation by cooling groove through heating after solid impurity is removed in concentrated and charcoal absorption, by the water at low temperature that temperature is 18~25 ℃, be cooled to 35~45 ℃, after cool slurry, separate out crystals of sodium carbonate, the slurries that contain crystals of sodium carbonate are put into sodium carbonate centrifugal filter and filter out crystals of sodium carbonate;
(6) filtrate step (5) being filtered out after crystals of sodium carbonate is put into the second crystallisation by cooling groove, by the water at low temperature that temperature is 18~25 ℃, be cooled to 25~30 ℃, separate out Sodium Thiocyanate 99 crystal, the slurry impouring Sodium Thiocyanate 99 centrifugal filter that contains Sodium Thiocyanate 99 crystal is filtered, obtain Sodium Thiocyanate 99 crystal;
(7) filtrate filtering out after Sodium Thiocyanate 99 crystal is returned to desulphurization system.
The related principles of chemistry of the inventive method are specific as follows:
First solution is heated to concentration, make the compound decomposition such as unsettled sodium polysulphide, Sulfothiorine separate out elemental sulfur, generate S-WAT, sodium sulphite etc., the atmospheric oxidation being then blown into generates sodium sulfate.
Na 2S 2O 3 === Na 2SO 3 + S
Na 2Sx+1=== Na 2S + xS
2Na 2SO 3 + O 2=== 2Na 2SO 4
Na 2S + 2O 2=== Na 2SO 4
With milk of lime Ca (OH) 2by the sodium sulfate N in waste liquid a2sO 4and remaining S-WAT N a2sO 3with sodium sulphite N a2s carries out respectively causticizing reaction and changes into calcium sulfate and calcium sulfite and sulfurated lime precipitation, and sodium ion reacts with hydroxide ion and generates sodium hydroxide, by after calcium sulfite, sulfurated lime and calcium sulfate filtering, and the filtrate that obtains being rich in Sodium Thiocyanate 99 and sodium hydroxide.
Na 2SO 3+Ca(OH) 2== CaSO 3 ↓+ 2NaOH
Na 2SO 4 +Ca(OH) 2 == CaSO 4↓ + 2NaOH
Na 2S + Ca(OH) 2 === CaS↓+ 2NaOH
Because Sodium Thiocyanate 99 and calcium hydroxide do not react, so only deposit sodium hydroxide and Sodium Thiocyanate 99 and a small amount of superfluous calcium hydroxide in the solution after sediment separate out.Then the filtrate after filtering precipitate is placed in acidifier, and be blown into the stack gas through purifying in acidifier, make the carbonic acid gas in stack gas and be rich in the sodium hydroxide generation neutralization reaction in Sodium Thiocyanate 99 and sodium hydroxide filtrate, generate sodium bicarbonate, further there is causticizing reaction and generate sodium carbonate in sodium bicarbonate and carbonic acid gas, simultaneously, in carbonic acid gas in purifying flue gas and filtrate, residual calcium hydroxide reaction generates precipitation of calcium carbonate, reacted filtrate is removed by filter to the acidizing fluid that obtains being rich in Sodium Thiocyanate 99 and sodium carbonate after precipitation of calcium carbonate.
CO 2 + Ca(OH) 2 == CaCO 3 ↓ + H 2O
CO 2 + NaOH == NaHCO 3
NaHCO 3+ NaOH == Na 2CO 3 +H 2O
The acidizing fluid that is rich in Sodium Thiocyanate 99 and sodium carbonate is removed to solid impurity through heating concentrated and charcoal absorption.
Because the dissolubility difference of sodium carbonate and two kinds of compound crystals of Sodium Thiocyanate 99 is larger, can adopt crystallisation by cooling method successively to extract respectively sodium carbonate and Sodium Thiocyanate 99 crystal product, sodium carbonate returns to desulphurization circulating liquid system, and Sodium Thiocyanate 99 crystal is as the finished product export trade.
The inventive method comprises following process links: waste liquid pretreatment impurity removing, thermal degradation decolouring, oxidation causticization-separation, acidifying-separation, evaporation concentration, crystallisation by cooling-separation.
" waste liquid pretreatment process " is to remove the organic or inorganic solid impurity entering at random in waste liquid, as sulphur, tar, ferruginization compound.
" thermal degradation bleaching process " is that thermolysis Sulfothiorine and sodium polysulphide are separated out elemental sulfur and S-WAT and sodium sulphite, and removes catalyst residue, and solution is become colorless.
" oxidation causticization-separation circuit " is to be oxidized to sodium sulfate with S-WAT and sodium sulphite that air generates " thermal degradation bleaching process "; With milk of lime Ca (OH) 2with sodium sulfate N a2sO 4and remaining S-WAT N a2sO 3with sodium sulphite N a2s carries out respectively causticizing reaction and generates calcium sulfate and calcium sulfite and sulfurated lime precipitation; Sodium ion in solution reacts with hydroxide ion and generates sodium hydroxide; By after calcium sulfite, sulfurated lime and calcium sulfate filtering, the filtrate that obtains being rich in Sodium Thiocyanate 99 and sodium hydroxide.
" acidifying-separation circuit " is the filtrate after separated with causticizing reaction in the carbonic acid gas utilizing in stack gas, make sodium hydroxide generate sodium bicarbonate, sodium bicarbonate further reacts with sodium hydroxide and generates sodium carbonate, meanwhile, excessive hydrogen calcium oxide neutralization residual in filtrate is generated to precipitation of calcium carbonate; Reacted filtrate is removed by filter to the acidizing fluid that obtains being rich in Sodium Thiocyanate 99 and sodium carbonate after precipitation of calcium carbonate.
" evaporation concentration operation " by removing after calcium carbonate, the acidizing fluid concentration and evaporation that is rich in Sodium Thiocyanate 99 and sodium carbonate reduces moisture.
" crystallisation by cooling-separation circuit " is according to the dissolubility difference of sodium carbonate and Sodium Thiocyanate 99, and concentrated solution is cooled to relevant temperature, and substep is separated out crystals of sodium carbonate and Sodium Thiocyanate 99 crystal.
" freezing Steppecd crystallization " that the inventive method is partly introduced with background technology compares, and has advantages of that device is simple, operational path is shorter, and saves refrigerator system, and process cost is low, and process cost is existing methods 35% to 40%.Industrial electro depletion lacks 75% to 80%, reclaims sodium carbonate 80% to 85% from waste liquid, makes the sodium carbonate outsourcing amount in sweetening process directly reduce 65% to 70%.Existing method need to be chilled to-5 ℃ of following refrigerated waters as crystallization water coolant in addition, and the Sulfothiorine of extraction and Sodium Thiocyanate 99 product purity are low, and can not make up the sodium carbonate alkali source that desulphurization system needs.
The inventive method removes the desulfurization waste liquor of hydrogen sulfide in coal gas or other gas, HCN generation for the treatment of soda method, the method can be under normal temperature condition, by thermal degradation, oxidation, causticization, Sulfothiorine, sodium polysulphide, sodium sulfate in soda method desulfurization waste liquor are changed into calcium sulfite, sulfurated lime and calcium sulfate precipitation, extract highly purified sodium carbonate and Sodium Thiocyanate 99 simultaneously, reclaim soda and return to desulphurization system circulation, reduce the alkaline consumption of desulfurization operations.
Accompanying drawing explanation:
Fig. 1 the inventive method process flow diagram.
In figure: 1-strainer, 2-thermal degradation device, 3-causticizer, 4-carbonic acid gas acidifier, 5-heats concentration kettle, 6-the first crystallisation by cooling groove, 7-the second crystallisation by cooling groove, 8-the first strainer, 9-the second strainer, 10-the 3rd strainer, 11-the 4th strainer, 12-sodium carbonate whizzer, 13-Sodium Thiocyanate 99 whizzer, 14-acidifying liquid bath, 15-filtrate medial launder, A-stock liquid, B-calcium sulfate, C-crystallize sodium carbonate filter cake, D-Sodium Thiocyanate 99, the new gac of E-, F-pressurized air, G-decompose slag, H-calcium carbonate, I-milk of lime, J-purifying flue gas, K-carries filtrate after Sodium Thiocyanate 99, S-steam, W-water coolant, P-waste active carbon.
Embodiment:
First the inventive method is that stock liquid A puts into strainer 1 by soda method desulfurization waste liquor, the built-in coke of strainer 1 or gac or other sorbing material, stock liquid A is by entrained solid impurity in fractionation by adsorption waste liquid after coke or active carbon adsorption material at normal temperatures and pressures, strainer can operate continuously several months very several weeks, when absorption reaches capacity or can or change sorbent material by recoil during resistance increment, keep adsorber working properly.
Stock liquid A after rough purification is sent into thermal degradation device 2, with steam S, heat, making the decomposition of components such as Sulfothiorine, sodium polysulphide is S-WAT and sodium sulphite, and separate out elemental sulfur and evaporate part moisture, be blown into the S-WAT and the sodium sulphite that in pressurized air F oxidation stock liquid A, generate simultaneously, convert it into sodium sulfate.Oxidizing reaction service temperature is controlled within the scope of 85~125 ℃.When heating the decomposition of components such as Sulfothiorine, sodium polysulphide be S-WAT and sodium sulphite, and separate out elemental sulfur.
Reaction solution after thermolysis-oxidizing reaction is put into the first strainer 8 elimination impurity G, and filtrate is sent into causticizer 3, adds milk of lime I to carry out causticizing reaction, makes sodium sulfate and remaining S-WAT N a2sO 3with sodium sulphite N a2s changes into respectively calcium sulfate and calcium sulfite and sulfurated lime precipitation, and sodium ion reacts with hydroxide ion and generates sodium hydroxide, and causticizing reaction temperature is within the scope of 85~125 ℃.Causticizing reaction liquid is sent into the second strainer 9 and is leached calcium sulfate and calcium sulfite and sulfurated lime B, enrichment Sodium Thiocyanate 99 and sodium hydroxide in filtrate, filtrate moves into carbonic acid gas acidifier 4, be blown into purifying flue gas J simultaneously, the neutralization reaction of carbonic acid gas and sodium hydroxide occurs in acidifier, and reaction final product is sodium carbonate.Acidification reaction is removed calcium hydroxide superfluous in filtrate simultaneously and is generated precipitation of calcium carbonate and solution separating.Acidizing fluid removes by filter precipitation of calcium carbonate H through the 3rd strainer 10.Filtrate collection is to acidifying liquid bath 14.In acidizing fluid enrichment Sodium Thiocyanate 99 and sodium carbonate, as extracting product Sodium Thiocyanate 99 and reclaiming the stock liquid of sodium carbonate.So far the pre-treatment of stock liquid finishes.Acidizing fluid is moved into heating concentration kettle 5, and solution heats concentrated in still, and adds new gac E absorption to remain in the solid impurity in solution, makes solution more colourless clean.Concentrated end put into the 4th strainer 11 by concentrated solution, removes by filter impurity and takes out waste active carbon P.Concentrated solution is put into the first crystallisation by cooling groove 6 use water at low temperature (18~25 ℃) later and be cooled to specified temperature (35~45 ℃), cool slurry is separated out crystals of sodium carbonate, and slurries are put into sodium carbonate centrifugal filter 12, filters out crystallize sodium carbonate thing C.And then filtrate is put into the second crystallisation by cooling groove 7 use water at low temperature (18~25 ℃) be cooled to specified temperature (25~30 ℃), separate out object product Sodium Thiocyanate 99 crystal, slurry impouring Sodium Thiocyanate 99 whizzer 13 is filtered, take out crystalline product Sodium Thiocyanate 99 D product, filtrate collection is to filtrate medial launder 15.This is the final filtrate of the inventive method, does not contain Sulfates, only contains a small amount of sodium carbonate and Sodium Thiocyanate 99, and this class filtrate K returns to desulphurization circulating liquid system.From the isolated sodium carbonate of sodium carbonate centrifugal filter, also return to desulfurization workshop section as desulfurization alkali, regeneration sodium carbonate can partly substitute new alkali.

Claims (1)

1.一种用苛化—酸化法处理钠碱法脱硫废液的方法,其特征在于该方法具体步骤如下: 1. a method for treating sodium-alkali desulfurization waste liquid with causticization-acidification, is characterized in that the method concrete steps are as follows: (1)在常温常压下,使用焦炭或活性炭等吸附材料吸附分离钠碱法脱硫废液中夹带的固体杂质; (1) At normal temperature and pressure, use coke or activated carbon and other adsorption materials to adsorb and separate the solid impurities entrained in the sodium-alkali desulfurization waste liquid; (2)经过所述步骤(1)处理后的钠碱法脱硫废液经蒸发浓缩,使得废液中不稳定的硫代硫酸钠和多硫化钠分别分解为亚硫酸钠和硫化钠,并析出单质硫的同时,向所述钠碱法脱硫废液中吹入压缩空气进行氧化反应,使所述钠碱法脱硫废液中经分解产生的亚硫酸钠和硫化钠氧化成硫酸钠,所述热分解-氧化反应的温度为85~125℃,所述压缩空气吹入的体积量是所述钠碱法脱硫废液体积量的20~160倍; (2) The sodium-alkali desulfurization waste liquid treated in the step (1) is evaporated and concentrated, so that the unstable sodium thiosulfate and sodium polysulfide in the waste liquid are decomposed into sodium sulfite and sodium sulfide respectively, and elemental sulfur is precipitated At the same time, compressed air is blown into the sodium-alkali desulfurization waste liquid to carry out the oxidation reaction, so that the sodium sulfite and sodium sulfide produced by decomposition in the sodium-alkali desulfurization waste liquid are oxidized into sodium sulfate, and the thermal decomposition-oxidation The reaction temperature is 85-125°C, and the volume of the compressed air blown in is 20-160 times the volume of the sodium-alkali desulfurization waste liquid; (3)将步骤(2)经过热分解-氧化反应处理后的钠碱法脱硫废液过滤除杂后,在滤液中加入石灰乳Ca(OH)2进行苛化反应,苛化反应的温度为85~125℃,使滤液中的硫酸钠Na2SO4及残存的亚硫酸钠Na2SO3和硫化钠Na2S分别转化成硫酸钙及亚硫酸钙和硫化钙沉淀,钠离子与氢氧根离子反应生成氢氧化钠,将亚硫酸钙、硫化钙和硫酸钙滤除后,得到富含硫氰酸钠和氢氧化钠的滤液; (3) After filtering and removing impurities from the sodium-alkali desulfurization waste liquid treated by thermal decomposition-oxidation reaction in step (2), add lime milk Ca(OH) 2 to the filtrate to carry out causticization reaction. The temperature of causticization reaction is 85~125℃, the sodium sulfate Na 2 SO 4 in the filtrate and the remaining sodium sulfite Na 2 SO 3 and sodium sulfide Na 2 S are converted into calcium sulfate, calcium sulfite and calcium sulfide, respectively, and sodium ions and hydroxide ions The reaction generates sodium hydroxide, and after calcium sulfite, calcium sulfide and calcium sulfate are filtered out, a filtrate rich in sodium thiocyanate and sodium hydroxide is obtained; (4)将步骤(3)得到的富含硫氰酸钠和氢氧化钠的滤液置于酸化器内,向所述酸化器中吹入经过净化的烟道气,使所述烟道气中的二氧化碳与所述富含硫氰酸钠和氢氧化钠的滤液中的氢氧化钠发生中和反应,反应产物是碳酸氢钠,中和反应生成的碳酸氢钠与所述步骤(3)苛化反应生成的氢氧化钠进一步反应生成碳酸钠,同时,所述净化烟道气中的二氧化碳与所述富含硫氰酸钠和氢氧化钠的滤液中残留的氢氧化钙反应生成碳酸钙沉淀,将反应后的滤液过滤除去碳酸钙沉淀后得到富含硫氰酸钠和碳酸钠的酸化液; (4) The filtrate rich in sodium thiocyanate and sodium hydroxide obtained in step (3) is placed in the acidifier, and the purified flue gas is blown into the acidifier to make the flue gas The carbon dioxide and the sodium hydroxide in the filtrate rich in sodium thiocyanate and sodium hydroxide are neutralized, the reaction product is sodium bicarbonate, and the sodium bicarbonate generated by the neutralization reaction reacts with the step (3) harsh The sodium hydroxide generated by the oxidation reaction further reacts to generate sodium carbonate, and at the same time, the carbon dioxide in the purified flue gas reacts with the residual calcium hydroxide in the filtrate rich in sodium thiocyanate and sodium hydroxide to generate calcium carbonate precipitation , after the filtrate after the reaction is filtered to remove the calcium carbonate precipitate, an acidified solution rich in sodium thiocyanate and sodium carbonate is obtained;  (5)将步骤(4)得到的富含硫氰酸钠和碳酸钠的酸化液经加热浓缩以及活性炭吸附除去固体杂质后放入第一冷却结晶槽,用温度为18~25℃的低温水冷却到35~45℃,冷却浆液后析出碳酸钠晶体,将含有碳酸钠晶体的浆液放入碳酸钠离心过滤机过滤出碳酸钠晶体; (5) Put the acidified solution rich in sodium thiocyanate and sodium carbonate obtained in step (4) into the first cooling crystallization tank after being concentrated by heating and adsorbed by activated carbon to remove solid impurities. Cool to 35-45°C, precipitate sodium carbonate crystals after cooling the slurry, put the slurry containing sodium carbonate crystals into a sodium carbonate centrifugal filter to filter out sodium carbonate crystals;  (6)将步骤(5)过滤出碳酸钠晶体后的滤液放入第二冷却结晶槽,用温度为18~25℃的低温水冷却至25~30℃,析出硫氰酸钠晶体,将含有硫氰酸钠晶体的结晶浆液倾入硫氰酸钠离心过滤机过滤,得到硫氰酸钠晶体; (6) Put the filtrate after filtering out the sodium carbonate crystals in step (5) into the second cooling crystallization tank, cool to 25-30°C with low-temperature water with a temperature of 18-25°C, and separate out sodium thiocyanate crystals, which will contain The crystal slurry of sodium thiocyanate crystals is poured into a sodium thiocyanate centrifugal filter and filtered to obtain sodium thiocyanate crystals; (7)过滤出硫氰酸钠晶体后的滤液返回脱硫系统。 (7) The filtrate after filtering out sodium thiocyanate crystals is returned to the desulfurization system.
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CN111484211A (en) * 2020-06-09 2020-08-04 河南东泰制药有限公司 Treatment method and device for high-concentration alkaline waste liquid in 2, 6-dichlorodiphenylamine production
CN112340911A (en) * 2020-09-29 2021-02-09 陕西陕焦化工有限公司 Method for recycling desulfurization waste liquid
CN112499813A (en) * 2020-11-20 2021-03-16 成都千砺金科技创新有限公司 Production method for full resource recycling of waste water in titanium dioxide production by sulfuric acid process
CN113292191A (en) * 2021-05-31 2021-08-24 陕西延长中煤榆林能源化工有限公司 Residual oil catalytic pyrolysis and coal-to-olefin waste alkali liquor resource utilization device
CN115090096A (en) * 2022-06-06 2022-09-23 武汉天源环保股份有限公司 Landfill leachate deodorization method and system
CN115784482A (en) * 2022-09-07 2023-03-14 浙江伽能环境工程有限责任公司 A method for oxygen pressure treatment of waste liquid containing sodium polysulfide

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CN111484211A (en) * 2020-06-09 2020-08-04 河南东泰制药有限公司 Treatment method and device for high-concentration alkaline waste liquid in 2, 6-dichlorodiphenylamine production
CN112340911A (en) * 2020-09-29 2021-02-09 陕西陕焦化工有限公司 Method for recycling desulfurization waste liquid
CN112499813A (en) * 2020-11-20 2021-03-16 成都千砺金科技创新有限公司 Production method for full resource recycling of waste water in titanium dioxide production by sulfuric acid process
CN113292191A (en) * 2021-05-31 2021-08-24 陕西延长中煤榆林能源化工有限公司 Residual oil catalytic pyrolysis and coal-to-olefin waste alkali liquor resource utilization device
CN115090096A (en) * 2022-06-06 2022-09-23 武汉天源环保股份有限公司 Landfill leachate deodorization method and system
CN115784482A (en) * 2022-09-07 2023-03-14 浙江伽能环境工程有限责任公司 A method for oxygen pressure treatment of waste liquid containing sodium polysulfide

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