CN111287011A - A method for comprehensive recycling and utilization of pulping waste liquid - Google Patents
A method for comprehensive recycling and utilization of pulping waste liquid Download PDFInfo
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- 238000004537 pulping Methods 0.000 title claims abstract description 46
- 239000002699 waste material Substances 0.000 title claims abstract description 33
- 238000000034 method Methods 0.000 title claims abstract description 30
- 238000004064 recycling Methods 0.000 title claims abstract description 27
- 239000007788 liquid Substances 0.000 title claims description 23
- 238000002485 combustion reaction Methods 0.000 claims abstract description 37
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 36
- 239000005416 organic matter Substances 0.000 claims abstract description 33
- 238000006243 chemical reaction Methods 0.000 claims abstract description 32
- 238000010411 cooking Methods 0.000 claims abstract description 24
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 19
- 239000003546 flue gas Substances 0.000 claims abstract description 19
- 238000001704 evaporation Methods 0.000 claims abstract description 8
- 239000000155 melt Substances 0.000 claims abstract description 7
- 239000011734 sodium Substances 0.000 claims description 102
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 39
- 239000007789 gas Substances 0.000 claims description 24
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims description 18
- 241000565357 Fraxinus nigra Species 0.000 claims description 18
- 235000011941 Tilia x europaea Nutrition 0.000 claims description 18
- 239000000839 emulsion Substances 0.000 claims description 18
- 239000004571 lime Substances 0.000 claims description 18
- 239000002994 raw material Substances 0.000 claims description 16
- 230000003647 oxidation Effects 0.000 claims description 13
- 238000007254 oxidation reaction Methods 0.000 claims description 13
- 239000002893 slag Substances 0.000 claims description 13
- 239000000126 substance Substances 0.000 claims description 13
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 claims description 12
- -1 alkyl sulfide Chemical compound 0.000 claims description 12
- 229910001570 bauxite Inorganic materials 0.000 claims description 12
- 238000009993 causticizing Methods 0.000 claims description 12
- 239000012141 concentrate Substances 0.000 claims description 12
- 238000001914 filtration Methods 0.000 claims description 12
- 238000010438 heat treatment Methods 0.000 claims description 12
- 239000010446 mirabilite Substances 0.000 claims description 12
- 239000002244 precipitate Substances 0.000 claims description 11
- XUIMIQQOPSSXEZ-UHFFFAOYSA-N Silicon Chemical compound [Si] XUIMIQQOPSSXEZ-UHFFFAOYSA-N 0.000 claims description 9
- 229910052710 silicon Inorganic materials 0.000 claims description 9
- 239000010703 silicon Substances 0.000 claims description 9
- 238000005406 washing Methods 0.000 claims description 9
- 239000002585 base Substances 0.000 claims description 7
- 229910052751 metal Inorganic materials 0.000 claims description 7
- 239000002184 metal Substances 0.000 claims description 7
- 150000003839 salts Chemical class 0.000 claims description 7
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 6
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 claims description 6
- 229910000503 Na-aluminosilicate Inorganic materials 0.000 claims description 6
- ISWSIDIOOBJBQZ-UHFFFAOYSA-N Phenol Chemical compound OC1=CC=CC=C1 ISWSIDIOOBJBQZ-UHFFFAOYSA-N 0.000 claims description 6
- 239000004115 Sodium Silicate Substances 0.000 claims description 6
- 239000002253 acid Substances 0.000 claims description 6
- 239000003513 alkali Substances 0.000 claims description 6
- ANBBXQWFNXMHLD-UHFFFAOYSA-N aluminum;sodium;oxygen(2-) Chemical compound [O-2].[O-2].[Na+].[Al+3] ANBBXQWFNXMHLD-UHFFFAOYSA-N 0.000 claims description 6
- 238000001354 calcination Methods 0.000 claims description 6
- 229910052799 carbon Inorganic materials 0.000 claims description 6
- 238000000354 decomposition reaction Methods 0.000 claims description 6
- 230000029087 digestion Effects 0.000 claims description 6
- 238000010790 dilution Methods 0.000 claims description 6
- 239000012895 dilution Substances 0.000 claims description 6
- 238000009826 distribution Methods 0.000 claims description 6
- 230000000694 effects Effects 0.000 claims description 6
- 239000000835 fiber Substances 0.000 claims description 6
- 125000002485 formyl group Chemical class [H]C(*)=O 0.000 claims description 6
- 239000012535 impurity Substances 0.000 claims description 6
- 238000002156 mixing Methods 0.000 claims description 6
- 125000000896 monocarboxylic acid group Chemical group 0.000 claims description 6
- 239000002245 particle Substances 0.000 claims description 6
- 239000000047 product Substances 0.000 claims description 6
- 229910052708 sodium Inorganic materials 0.000 claims description 6
- 229910001388 sodium aluminate Inorganic materials 0.000 claims description 6
- 239000000429 sodium aluminium silicate Substances 0.000 claims description 6
- 235000012217 sodium aluminium silicate Nutrition 0.000 claims description 6
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 claims description 6
- 150000003388 sodium compounds Chemical class 0.000 claims description 6
- NTHWMYGWWRZVTN-UHFFFAOYSA-N sodium silicate Chemical compound [Na+].[Na+].[O-][Si]([O-])=O NTHWMYGWWRZVTN-UHFFFAOYSA-N 0.000 claims description 6
- 229910052911 sodium silicate Inorganic materials 0.000 claims description 6
- 239000007921 spray Substances 0.000 claims description 6
- 238000002347 injection Methods 0.000 claims description 5
- 239000007924 injection Substances 0.000 claims description 5
- 238000009834 vaporization Methods 0.000 claims description 5
- 230000008016 vaporization Effects 0.000 claims description 5
- 238000011084 recovery Methods 0.000 claims description 4
- 239000000203 mixture Substances 0.000 claims 1
- 239000002351 wastewater Substances 0.000 abstract description 7
- 235000011121 sodium hydroxide Nutrition 0.000 description 11
- 150000002894 organic compounds Chemical class 0.000 description 5
- 239000002918 waste heat Substances 0.000 description 3
- 238000004061 bleaching Methods 0.000 description 2
- 238000013386 optimize process Methods 0.000 description 2
- 239000010893 paper waste Substances 0.000 description 2
- 238000003911 water pollution Methods 0.000 description 2
- 229920002488 Hemicellulose Polymers 0.000 description 1
- 229920002472 Starch Polymers 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000007844 bleaching agent Substances 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 235000011116 calcium hydroxide Nutrition 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 239000007857 degradation product Substances 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 239000011552 falling film Substances 0.000 description 1
- 239000012633 leachable Substances 0.000 description 1
- 229920005610 lignin Polymers 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 150000007524 organic acids Chemical class 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 239000000049 pigment Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 150000003377 silicon compounds Chemical class 0.000 description 1
- 239000000344 soap Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000008107 starch Substances 0.000 description 1
- 235000019698 starch Nutrition 0.000 description 1
- 239000003784 tall oil Substances 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
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Classifications
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- D—TEXTILES; PAPER
- D21—PAPER-MAKING; PRODUCTION OF CELLULOSE
- D21C—PRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
- D21C11/00—Regeneration of pulp liquors or effluent waste waters
- D21C11/0064—Aspects concerning the production and the treatment of green and white liquors, e.g. causticizing green liquor
-
- D—TEXTILES; PAPER
- D21—PAPER-MAKING; PRODUCTION OF CELLULOSE
- D21C—PRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
- D21C11/00—Regeneration of pulp liquors or effluent waste waters
- D21C11/0064—Aspects concerning the production and the treatment of green and white liquors, e.g. causticizing green liquor
- D21C11/0078—Treatment of green or white liquors with other means or other compounds than gases, e.g. in order to separate solid compounds such as sodium chloride and carbonate from these liquors; Further treatment of these compounds
-
- D—TEXTILES; PAPER
- D21—PAPER-MAKING; PRODUCTION OF CELLULOSE
- D21C—PRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
- D21C11/00—Regeneration of pulp liquors or effluent waste waters
- D21C11/12—Combustion of pulp liquors
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- Paper (AREA)
Abstract
本发明公开了一种制浆废液综合回收利用的方法,首先从制浆蒸煮液中提取出稀黑液,然后对稀黑液预处理,最后采用混流式间接蒸发法对经预处理后的稀黑液蒸发浓缩;然后采用喷射炉燃烧,黑液中的有机物燃烧后产生的高温烟气在炉内上升,无机物熔融从燃烧炉下方的溜槽流入溶解槽中,且溶解于稀白液或水中形成绿液,绿液成分包括Na2CO3、Na2S;对溶解于稀白液或水中的无机熔融物所形成的绿液进行苛化反应;最后对绿液苛化反应产生的产物进行回收利用。本发明解决了现有技术中存在的制浆造纸废水污染严重、处理难度大的问题。
The invention discloses a method for comprehensive recycling and utilization of pulping waste liquor. First, dilute black liquor is extracted from pulping and cooking liquor, then the dilute black liquor is pretreated, and finally the pretreated pulp is treated by a mixed-flow indirect evaporation method. The dilute black liquor is evaporated and concentrated; then it is burned in a jet furnace, the high temperature flue gas generated by the combustion of the organic matter in the black liquor rises in the furnace, and the inorganic matter melts from the chute below the combustion furnace into the dissolving tank, and dissolves in the dilute white liquor or The green liquor is formed in the water, and the components of the green liquor include Na 2 CO 3 and Na 2 S; the green liquor formed by dissolving the inorganic melt in dilute white liquor or water is subjected to the causticization reaction; finally, the products produced by the causticization reaction of the green liquor are for recycling. The invention solves the problems of serious pollution and difficult treatment of pulp and papermaking wastewater existing in the prior art.
Description
技术领域technical field
本发明属于废液处理技术领域,具体涉及一种制浆废液综合回收利用的方法。The invention belongs to the technical field of waste liquid treatment, and in particular relates to a method for comprehensive recycling and utilization of pulping waste liquid.
背景技术Background technique
制浆造纸业是传统的用水大户,也是造成水污染的重要污染源之。随着经济的发展,企业日益面临水资源短缺、原料匮乏的问题,而另一方面,水污染也越来越严重。目前,我国制浆造纸行业废水排放量及COD排放量均居我国各类工业排放量的首位,所以为了防止制浆造纸废液中的污染物对我国环境造成破环,对制浆造纸废液进行处理已成为必不可少的环节。The pulp and paper industry is a traditional large water user and one of the important sources of water pollution. With the development of economy, enterprises are increasingly faced with the problem of water shortage and raw material shortage. On the other hand, water pollution is becoming more and more serious. At present, the discharge of wastewater and COD from the pulp and paper industry in China ranks first in the discharge of various industries in my country. Therefore, in order to prevent the pollutants in the pulp and paper waste liquid from causing damage to my country's environment, the pulp and paper waste liquid Processing has become an essential link.
制浆废液是指化学法制浆产生的蒸煮废液和洗浆漂白过程中产生的废水。我国的制浆方法以碱法蒸煮为主,其固形物可分为无机物和有机物,碱法黑液的无机物约占30%~35%、有机物约占65%~70%;无机物主要是蒸煮废液中残余的化学药品,以及和制浆原料中的有机物化合的金属盐基、制浆原料本身带来的无机成分,如硅的化合物等;有机物主要包括制浆原料在蒸煮过程中降解产物、溶出物等,如木素、纤维素、半纤维素、淀粉、树脂、色素及有机酸等。洗浆是为了最大限度提取黑液、提高化学药品的回收率,其少量的清洗水呈棕黑色,有机污染物浓度很高。漂白是在多段过程中进行的,并使用不同的漂白剂,该工段是工厂外排废水的主要来源,有毒、处理难度较大。The pulping waste liquor refers to the cooking waste liquor produced by chemical pulping and the waste water produced in the pulp washing and bleaching process. my country's pulping method is mainly based on alkaline cooking, and its solids can be divided into inorganic and organic substances. It is the residual chemicals in the cooking waste liquid, as well as the metal salt base that is combined with the organic matter in the pulping raw material, and the inorganic components brought by the pulping raw material itself, such as silicon compounds; the organic matter mainly includes the pulping raw material in the cooking process. Degradation products, leachables, etc., such as lignin, cellulose, hemicellulose, starch, resin, pigment and organic acid, etc. The purpose of pulp washing is to maximize the extraction of black liquor and improve the recovery rate of chemicals. A small amount of washing water is brown-black and has a high concentration of organic pollutants. Bleaching is carried out in a multi-stage process and uses different bleaching agents. This section is the main source of wastewater discharged from the factory, which is toxic and difficult to handle.
废液排入江河中不仅严重影响污染水源,也会造成大量资源浪费。如何消除制浆造纸废水污染并使废液中宝贵资源得到利用是一项具有重大社会意义和经济价值的工作,应当受到重视。The discharge of waste liquid into rivers not only seriously affects the pollution of water sources, but also causes a lot of waste of resources. How to eliminate the pollution of pulp and papermaking wastewater and make use of the precious resources in the wastewater is a work of great social significance and economic value, which should be paid attention to.
发明内容SUMMARY OF THE INVENTION
本发明的目的是提供一种制浆废液综合回收利用的方法,解决了现有技术中存在的制浆造纸废水污染严重、处理难度大的问题。The purpose of the present invention is to provide a method for comprehensive recycling and utilization of pulping waste liquid, which solves the problems of serious pollution and difficult treatment of pulping and papermaking waste water in the prior art.
本发明所采用的技术方案是,一种制浆废液综合回收利用的方法,具体按照以下步骤实施:The technical scheme adopted in the present invention is, a method for comprehensive recycling and utilization of pulping waste liquid, which is specifically implemented according to the following steps:
步骤1、从制浆蒸煮液中提取出稀黑液,然后对稀黑液预处理,最后采用混流式间接蒸发法对经预处理后的稀黑液蒸发浓缩;Step 1. Extract the dilute black liquor from the pulping and cooking liquor, then pretreat the dilute black liquor, and finally adopt the mixed-flow indirect evaporation method to evaporate and concentrate the pretreated dilute black liquor;
步骤2、对经步骤1浓缩后的黑液采用喷射炉燃烧,黑液中的有机物燃烧后产生的高温烟气在炉内上升,无机物熔融从燃烧炉下方的溜槽流入溶解槽中,且溶解于稀白液或水中形成绿液,绿液成分包括Na2CO3、Na2S;Step 2. The black liquor concentrated in step 1 is burned in a jet furnace. The high-temperature flue gas generated by the combustion of the organic matter in the black liquor rises in the furnace, and the inorganic matter melts from the chute below the combustion furnace into the dissolving tank, and dissolves. Form green liquor in dilute white liquor or water, and the components of green liquor include Na 2 CO 3 and Na 2 S;
步骤3、对溶解于稀白液或水中的无机熔融物所形成的绿液进行苛化反应;Step 3, causticizing the green liquor formed by the inorganic melt dissolved in dilute white liquor or water;
步骤4、对绿液苛化反应产生的产物进行回收利用。Step 4: Recycling the product produced by the causticization reaction of the green liquor.
本发明的特点还在于,The present invention is also characterized in that,
步骤1中提取出的稀黑液成分为70%可燃烧的有机物质,30%无机物,无机物包括蒸煮废液中残余的化学药品,如NaOH,Na2S,以及和制浆原料中的有机物化合的金属盐基、制浆原料本身带来的无机成分。The dilute black liquor extracted in step 1 is composed of 70% combustible organic matter and 30% inorganic matter. The inorganic matter includes the residual chemicals in the cooking waste liquor, such as NaOH, Na 2 S, and the raw materials for pulping. The metal salt base of organic compounds and the inorganic components brought by the pulping raw material itself.
步骤1中对稀黑液预处理包括除渣、氧化、除硅,除渣即对黑液中含有的细小纤维和各种残渣进行去除;氧化即将黑液中的Na2S氧化为稳定的Na2SO4和Na2S2O3,具体反应为:2Na2S+2O2+H2O=Na2S2O3+2NaOH,Na2S+2O2=Na2SO4;除硅即采用铝土矿除硅法,将适量的铝土矿,在燃烧前加入到黑液中,在燃烧过程中形成的铝酸钠,绿液中与硅酸钠反应生成硅铝酸钠复合体沉淀而被除去。In step 1, the pretreatment of the dilute black liquor includes slag removal, oxidation and silicon removal. The slag removal is to remove the fine fibers and various residues contained in the black liquor; the oxidation is to oxidize Na 2 S in the black liquor to stable Na 2 SO 4 and Na 2 S 2 O 3 , the specific reaction is: 2Na 2 S+2O 2 +H 2 O=Na 2 S 2 O 3 +2NaOH, Na 2 S+2O 2 =Na 2 SO 4 ; Using the bauxite desilicon method, an appropriate amount of bauxite is added to the black liquor before combustion, and the sodium aluminate formed during the combustion process reacts with sodium silicate in the green liquor to form a sodium aluminosilicate complex precipitate. and removed.
步骤1中对经预处理后的稀黑液蒸发浓缩,具体为:首先采用混流式加热,加热过程中水分汽化逸出浓度浓缩到45%~48%,再使用烟气余热加热浓缩至浓度值为50%~65%。In step 1, the pretreated dilute black liquor is evaporated and concentrated, specifically: firstly adopting mixed-flow heating, during the heating process, the concentration of water vaporization escapes is concentrated to 45% to 48%, and then the waste heat of flue gas is used to heat and concentrate to the concentration value 50% to 65%.
步骤2具体按照以下步骤实施:Step 2 is implemented according to the following steps:
步骤2.1、第一阶段:入炉黑液在热炉气的作用下进一步干燥至浓度为85%时,形成黑灰,烟气中所含的SO2、SO3以及CO2与黑液中的活性碱及有机结合钠起化学反应;黑液中的游离NaOH和大部分的Na2S均转变为Na2CO3、Na2SO3、Na2SO4和Na2S2O3;Step 2.1, the first stage: when the black liquor entering the furnace is further dried to a concentration of 85% under the action of the hot furnace gas, black ash is formed, and the SO 2 , SO 3 and CO 2 contained in the flue gas and the black liquor The active alkali and organically bound sodium react chemically; the free NaOH and most of Na 2 S in the black liquor are transformed into Na 2 CO 3 , Na 2 SO 3 , Na 2 SO 4 and Na 2 S 2 O 3 ;
步骤2.2、第二阶段:黑灰最后剩下的水分逐渐被蒸发掉,温度迅速升高到350℃~450℃时,有机物快速分解为CH3OH、CH3COOH、CH3SH、H2S、酚、低分子的醛酸以及结构复杂的烷基硫化物有机气体,并与进入炉膛的二次风和三次风混合后发生气相燃烧,生成SO2、SO3、CO、H2O、H2S气体;还有一部分有机物发生碳化作用,变成元素碳,供芒硝还原用;另外,与有机物结合生成的钠化合物也发生分解反应,生成Na2CO3;Step 2.2, the second stage: the last remaining water of the black ash is gradually evaporated. When the temperature rises rapidly to 350℃~450℃, the organic matter is rapidly decomposed into CH 3 OH, CH 3 COOH, CH 3 SH, H 2 S , phenol, low molecular aldehyde acid and complex structure of alkyl sulfide organic gas, and mixed with the secondary air and tertiary air entering the furnace, gas-phase combustion occurs to generate SO 2 , SO 3 , CO, H 2 O, H 2 S gas; a part of the organic matter is carbonized and becomes elemental carbon for the reduction of mirabilite; in addition, the sodium compound formed by combining with the organic matter also undergoes a decomposition reaction to generate Na 2 CO 3 ;
为使黑灰在还原条件下充分燃烧,入炉空气需预先加热到140~150℃,一次风在燃烧炉的还原区加入,二次风在还原区的上方及黑液喷射入口附近加入,三次风在黑液喷枪上方加入,一、二、三次风的风量分配比大致为50:20:30,一次风压力为0.8~1.2KPa、二、三次风压力为1.5~3KPa。In order to fully burn the black ash under reducing conditions, the air entering the furnace needs to be preheated to 140-150 °C, the primary air is added in the reduction area of the combustion furnace, and the secondary air is added above the reduction area and near the injection inlet of the black liquor, three times. The air is added above the black liquor spray gun. The air volume distribution ratio of the primary, secondary and tertiary air is roughly 50:20:30, the primary air pressure is 0.8~1.2KPa, and the secondary and tertiary air pressure is 1.5~3KPa.
步骤2.3、第三阶段:使无机物在高温下熔融,同时补加芒硝。Step 2.3, the third stage: the inorganic matter is melted at high temperature, and then mirabilite is added at the same time.
步骤3具体按照以下步骤实施:Step 3 is implemented according to the following steps:
步骤3.1、将溶解槽中的绿液进行澄清,除去不溶性的杂质绿泥,然后将剩余的粗绿泥进行洗涤、沉淀处理以回收绿泥中夹带的绿液;Step 3.1, clarify the green liquor in the dissolving tank, remove the insoluble impurity green mud, then wash and precipitate the remaining crude green mud to recover the green liquor entrained in the green mud;
步骤3.2、将澄清后的绿液和绿泥中夹带的绿液进行消化反应,具体反应为CaO+H2O=Ca(OH)2,加料时间控制在60~130min,为了进一步提高苛化效率,需要将CaO进行研磨,将粒径控制为3~4μm;Step 3.2, the clarified green liquor and the green liquor entrained in the green mud are digested, the specific reaction is CaO+H 2 O=Ca(OH) 2 , and the feeding time is controlled at 60-130min, in order to further improve the causticizing efficiency , CaO needs to be ground, and the particle size is controlled to 3-4 μm;
步骤3.3、石灰消化后形成的初始苛化乳液进入分离器,将未消化的石灰渣料除去后,送到连续苛化器系统苛化,具体反应为Ca(OH)2+Na2CO3=CaCO3↓+2NaOH;Step 3.3. The initial causticized emulsion formed after lime digestion enters the separator, and after removing the undigested lime residue, it is sent to the continuous causticizer system for causticization. The specific reaction is Ca(OH) 2 +Na 2 CO 3 = CaCO 3 ↓+2NaOH;
步骤3.4、从连续苛化器系统出来的浓白液送到白液澄清器中,以除去白液中的白泥;Step 3.4, the concentrated white liquor from the continuous causticizer system is sent to the white liquor clarifier to remove the white mud in the white liquor;
步骤3.5、澄清的白液经过进一步的过滤处理后送入浓白液槽,然后送到蒸煮工段,从白液过滤设备来的白泥送到白泥洗涤器经热水稀释、洗涤、混合均匀后得到稀白液和白泥乳液;Step 3.5. After further filtration treatment, the clarified white liquor is sent to the concentrated white liquor tank, and then sent to the cooking section. The white mud from the white liquor filtration equipment is sent to the white mud scrubber for dilution, washing and mixing with hot water. Afterwards, dilute white liquor and white mud emulsion are obtained;
步骤3.6、将稀白液和白泥乳液送入离心机系统进行处理,再次回收部分稀白液,而白泥送入白泥处理系统。In step 3.6, the dilute white liquor and white mud emulsion are sent to the centrifuge system for processing, part of the dilute white liquor is recovered again, and the white mud is sent to the white mud treatment system.
步骤4具体按照以下步骤实施:Step 4 is implemented according to the following steps:
步骤4.1、将所述步骤3苛化工段出来的白泥送入煅烧炉后,在高温炉气的作用下蒸发干燥并形成颗粒状白泥;Step 4.1, after the lime mud from the causticization section of the step 3 is sent into the calciner, evaporate and dry under the effect of high temperature furnace gas and form granular white mud;
步骤4.2、干燥后的白泥进一步预热到600℃,CaCO3开始分解;然后将白泥加热至825℃,此时CaCO3开始迅速分解,即进入煅烧段,生成可循环利用的CaO,具体反应为:CaCO3=CaO+CO2↑。Step 4.2. The dried white mud is further preheated to 600°C, and CaCO 3 begins to decompose; then the white mud is heated to 825° C. At this time, CaCO 3 begins to decompose rapidly, that is, it enters the calcination section to generate recyclable CaO. The reaction is: CaCO 3 =CaO+CO 2 ↑.
本发明的有益效果是,一种制浆废液综合回收利用的方法,从制浆蒸煮液中提取出稀黑液,经过除渣、氧化、除硅等预处理阶段,之后通过板式降膜蒸发器蒸发浓缩,并进行除皂回收塔罗油,然后送入喷射炉进行燃烧,最后经过绿液苛化回收烧碱,并且回收利用苛化阶段所用的消石灰,从而完成对造纸废液黑液的回收利用。本发明提供的回收与利用制浆废液的优化工艺具有流程更加精细,通过优化工艺有效地消除了传统造纸废液在处理以及回收利用中污染重、回收效率低、安全系数低等缺陷,达到降低生产成本、循环利用化学药品的目的。The beneficial effect of the present invention is that, in a method for comprehensive recycling and utilization of pulping waste liquor, dilute black liquor is extracted from pulping and cooking liquor, undergoes pretreatment stages such as slag removal, oxidation, and silicon removal, and then passes through plate type falling film evaporation. It is evaporated and concentrated in the device, and the soap is removed to recover the tall oil, and then sent to the jet furnace for combustion. Finally, the caustic soda is recovered through the causticization of the green liquor, and the slaked lime used in the causticization stage is recycled, so as to complete the recovery of the black liquor of the papermaking waste liquor. use. The optimized process for recycling and utilizing pulping waste liquid provided by the present invention has a more refined process, and through the optimized process, the defects such as heavy pollution, low recovery efficiency and low safety factor of traditional papermaking waste liquid in the treatment and recycling are effectively eliminated, and the The purpose of reducing production costs and recycling chemicals.
附图说明Description of drawings
图1是本发明一种制浆废液综合回收利用的方法的流程图。Fig. 1 is a flow chart of a method for comprehensive recycling and utilization of pulping waste liquid according to the present invention.
具体实施方式Detailed ways
下面结合附图和具体实施方式对本发明进行详细说明。The present invention will be described in detail below with reference to the accompanying drawings and specific embodiments.
本发明一种制浆废液综合回收利用的方法,流程图如图1所示,具体按照以下步骤实施:A method for comprehensive recycling and utilization of pulping waste liquid of the present invention, the flowchart is shown in Figure 1, and is specifically implemented according to the following steps:
步骤1、从制浆蒸煮液中提取出稀黑液,然后对稀黑液预处理,最后采用混流式间接蒸发法对经预处理后的稀黑液蒸发浓缩;Step 1. Extract the dilute black liquor from the pulping and cooking liquor, then pretreat the dilute black liquor, and finally adopt the mixed-flow indirect evaporation method to evaporate and concentrate the pretreated dilute black liquor;
步骤1中提取出的稀黑液成分为70%可燃烧的有机物质,30%无机物,无机物包括蒸煮废液中残余的化学药品,如NaOH,Na2S,以及和制浆原料中的有机物化合的金属盐基、制浆原料本身带来的无机成分。The dilute black liquor extracted in step 1 is composed of 70% combustible organic matter and 30% inorganic matter. The inorganic matter includes the residual chemicals in the cooking waste liquor, such as NaOH, Na 2 S, and the raw materials for pulping. The metal salt base of organic compounds and the inorganic components brought by the pulping raw material itself.
步骤1中对稀黑液预处理包括除渣、氧化、除硅,除渣即对黑液中含有的细小纤维和各种残渣进行去除;氧化即将黑液中的Na2S氧化为稳定的Na2SO4和Na2S2O3,具体反应为:2Na2S+2O2+H2O=Na2S2O3+2NaOH,Na2S+2O2=Na2SO4;除硅即采用铝土矿除硅法,将适量的铝土矿,在燃烧前加入到黑液中,在燃烧过程中形成的铝酸钠,绿液中与硅酸钠反应生成硅铝酸钠复合体沉淀而被除去。In step 1, the pretreatment of the dilute black liquor includes slag removal, oxidation and silicon removal. The slag removal is to remove the fine fibers and various residues contained in the black liquor; the oxidation is to oxidize Na 2 S in the black liquor to stable Na 2 SO 4 and Na 2 S 2 O 3 , the specific reaction is: 2Na 2 S+2O 2 +H 2 O=Na 2 S 2 O 3 +2NaOH, Na 2 S+2O 2 =Na 2 SO 4 ; Using the bauxite desilicon method, an appropriate amount of bauxite is added to the black liquor before combustion, and the sodium aluminate formed during the combustion process reacts with sodium silicate in the green liquor to form a sodium aluminosilicate complex precipitate. and removed.
步骤1中对经预处理后的稀黑液蒸发浓缩,具体为:首先采用混流式加热,加热过程中水分汽化逸出浓度浓缩到45%~48%,再使用烟气余热加热浓缩至浓度值为50%~65%。In step 1, the pretreated dilute black liquor is evaporated and concentrated, specifically: firstly adopting mixed-flow heating, during the heating process, the concentration of water vaporization escapes is concentrated to 45% to 48%, and then the waste heat of flue gas is used to heat and concentrate to the concentration value 50% to 65%.
步骤2、对经步骤1浓缩后的黑液采用喷射炉燃烧,黑液中的有机物燃烧后产生的高温烟气在炉内上升,无机物熔融从燃烧炉下方的溜槽流入溶解槽中,且溶解于稀白液或水中形成绿液,绿液成分包括Na2CO3、Na2S;Step 2. The black liquor concentrated in step 1 is burned in a jet furnace. The high-temperature flue gas generated by the combustion of the organic matter in the black liquor rises in the furnace, and the inorganic matter melts from the chute below the combustion furnace into the dissolving tank, and dissolves. Form green liquor in dilute white liquor or water, and the components of green liquor include Na 2 CO 3 and Na 2 S;
步骤2具体按照以下步骤实施:Step 2 is implemented according to the following steps:
步骤2.1、第一阶段:入炉黑液在热炉气的作用下进一步干燥至浓度为85%时,形成黑灰,烟气中所含的SO2、SO3以及CO2与黑液中的活性碱及有机结合钠起化学反应;黑液中的游离NaOH和大部分的Na2S均转变为Na2CO3、Na2SO3、Na2SO4和Na2S2O3;Step 2.1, the first stage: when the black liquor entering the furnace is further dried to a concentration of 85% under the action of the hot furnace gas, black ash is formed, and the SO 2 , SO 3 and CO 2 contained in the flue gas and the black liquor The active alkali and organically bound sodium react chemically; the free NaOH and most of Na 2 S in the black liquor are transformed into Na 2 CO 3 , Na 2 SO 3 , Na 2 SO 4 and Na 2 S 2 O 3 ;
步骤2.2、第二阶段:黑灰最后剩下的水分逐渐被蒸发掉,温度迅速升高到350℃~450℃时,有机物快速分解为CH3OH、CH3COOH、CH3SH、H2S、酚、低分子的醛酸以及结构复杂的烷基硫化物有机气体,并与进入炉膛的二次风和三次风混合后发生气相燃烧,生成SO2、SO3、CO、H2O、H2S气体;还有一部分有机物发生碳化作用,变成元素碳,供芒硝还原用;另外,与有机物结合生成的钠化合物也发生分解反应,生成Na2CO3;Step 2.2, the second stage: the last remaining water of the black ash is gradually evaporated. When the temperature rises rapidly to 350℃~450℃, the organic matter is rapidly decomposed into CH 3 OH, CH 3 COOH, CH 3 SH, H 2 S , phenol, low molecular aldehyde acid and complex structure of alkyl sulfide organic gas, and mixed with the secondary air and tertiary air entering the furnace, gas-phase combustion occurs to generate SO 2 , SO 3 , CO, H 2 O, H 2 S gas; a part of the organic matter is carbonized and becomes elemental carbon for the reduction of mirabilite; in addition, the sodium compound formed by combining with the organic matter also undergoes a decomposition reaction to generate Na 2 CO 3 ;
为使黑灰在还原条件下充分燃烧,入炉空气需预先加热到140~150℃,一次风在燃烧炉的还原区加入,二次风在还原区的上方及黑液喷射入口附近加入,三次风在黑液喷枪上方加入,一、二、三次风的风量分配比大致为50:20:30,一次风压力为0.8~1.2KPa、二、三次风压力为1.5~3KPa。In order to fully burn the black ash under reducing conditions, the air entering the furnace needs to be preheated to 140-150 °C, the primary air is added in the reduction area of the combustion furnace, and the secondary air is added above the reduction area and near the injection inlet of the black liquor, three times. The air is added above the black liquor spray gun. The air volume distribution ratio of the primary, secondary and tertiary air is roughly 50:20:30, the primary air pressure is 0.8~1.2KPa, and the secondary and tertiary air pressure is 1.5~3KPa.
步骤2.3、第三阶段:使无机物在高温下熔融,同时补加芒硝。Step 2.3, the third stage: the inorganic matter is melted at high temperature, and then mirabilite is added at the same time.
步骤3、对溶解于稀白液或水中的无机熔融物所形成的绿液进行苛化反应;Step 3, causticizing the green liquor formed by the inorganic melt dissolved in dilute white liquor or water;
步骤3具体按照以下步骤实施:Step 3 is implemented according to the following steps:
步骤3.1、将溶解槽中的绿液进行澄清,除去不溶性的杂质绿泥,然后将剩余的粗绿泥进行洗涤、沉淀处理以回收绿泥中夹带的绿液;Step 3.1, clarify the green liquor in the dissolving tank, remove the insoluble impurity green mud, then wash and precipitate the remaining crude green mud to recover the green liquor entrained in the green mud;
步骤3.2、将澄清后的绿液和绿泥中夹带的绿液进行消化反应,具体反应为CaO+H2O=Ca(OH)2,加料时间控制在60~130min,为了进一步提高苛化效率,需要将CaO进行研磨,将粒径控制为3~4μm;Step 3.2, the clarified green liquor and the green liquor entrained in the green mud are digested, the specific reaction is CaO+H 2 O=Ca(OH) 2 , and the feeding time is controlled at 60-130min, in order to further improve the causticizing efficiency , CaO needs to be ground, and the particle size is controlled to 3-4 μm;
步骤3.3、石灰消化后形成的初始苛化乳液进入分离器,将未消化的石灰渣料除去后,送到连续苛化器系统苛化,具体反应为Ca(OH)2+Na2CO3=CaCO3↓+2NaOH;Step 3.3. The initial causticized emulsion formed after lime digestion enters the separator, and after removing the undigested lime residue, it is sent to the continuous causticizer system for causticization. The specific reaction is Ca(OH) 2 +Na 2 CO 3 = CaCO 3 ↓+2NaOH;
步骤3.4、从连续苛化器系统出来的浓白液送到白液澄清器中,以除去白液中的白泥;Step 3.4, the concentrated white liquor from the continuous causticizer system is sent to the white liquor clarifier to remove the white mud in the white liquor;
步骤3.5、澄清的白液经过进一步的过滤处理后送入浓白液槽,然后送到蒸煮工段,从白液过滤设备来的白泥送到白泥洗涤器经热水稀释、洗涤、混合均匀后得到稀白液和白泥乳液;Step 3.5. After further filtration treatment, the clarified white liquor is sent to the concentrated white liquor tank, and then sent to the cooking section. The white mud from the white liquor filtration equipment is sent to the white mud scrubber for dilution, washing and mixing with hot water. Afterwards, dilute white liquor and white mud emulsion are obtained;
步骤3.6、将稀白液和白泥乳液送入离心机系统进行处理,再次回收部分稀白液,而白泥送入白泥处理系统。In step 3.6, the dilute white liquor and white mud emulsion are sent to the centrifuge system for processing, part of the dilute white liquor is recovered again, and the white mud is sent to the white mud treatment system.
步骤4、对绿液苛化反应产生的产物进行回收利用,具体按照以下步骤实施:Step 4. Recycling the product produced by the green liquor causticization reaction is implemented according to the following steps:
步骤4.1、将所述步骤3苛化工段出来的白泥送入煅烧炉后,在高温炉气的作用下蒸发干燥并形成颗粒状白泥;Step 4.1, after the lime mud from the causticization section of the step 3 is sent into the calciner, evaporate and dry under the effect of high temperature furnace gas and form granular white mud;
步骤4.2、干燥后的白泥进一步预热到600℃,CaCO3开始分解;然后将白泥加热至825℃,此时CaCO3开始迅速分解,即进入煅烧段,生成可循环利用的CaO,具体反应为:CaCO3=CaO+CO2↑。Step 4.2. The dried white mud is further preheated to 600°C, and CaCO 3 begins to decompose; then the white mud is heated to 825° C. At this time, CaCO 3 begins to decompose rapidly, that is, it enters the calcination section to generate recyclable CaO. The reaction is: CaCO 3 =CaO+CO 2 ↑.
实施例1Example 1
本发明一种制浆废液综合回收利用的方法,流程图如图1所示,具体按照以下步骤实施:A method for comprehensive recycling and utilization of pulping waste liquid of the present invention, the flowchart is shown in Figure 1, and is specifically implemented according to the following steps:
步骤1、从制浆蒸煮液中提取出稀黑液,然后对稀黑液预处理,最后采用混流式间接蒸发法对经预处理后的稀黑液蒸发浓缩;Step 1. Extract the dilute black liquor from the pulping and cooking liquor, then pretreat the dilute black liquor, and finally adopt the mixed-flow indirect evaporation method to evaporate and concentrate the pretreated dilute black liquor;
步骤1中提取出的稀黑液成分为70%可燃烧的有机物质,30%无机物,无机物包括蒸煮废液中残余的化学药品,如NaOH,Na2S,以及和制浆原料中的有机物化合的金属盐基、制浆原料本身带来的无机成分。The dilute black liquor extracted in step 1 is composed of 70% combustible organic matter and 30% inorganic matter. The inorganic matter includes the residual chemicals in the cooking waste liquor, such as NaOH, Na 2 S, and the raw materials for pulping. The metal salt base of organic compounds and the inorganic components brought by the pulping raw material itself.
步骤1中对稀黑液预处理包括除渣、氧化、除硅,除渣即对黑液中含有的细小纤维和各种残渣进行去除;氧化即将黑液中的Na2S氧化为稳定的Na2SO4和Na2S2O3,具体反应为:2Na2S+2O2+H2O=Na2S2O3+2NaOH,Na2S+2O2=Na2SO4;除硅即采用铝土矿除硅法,将适量的铝土矿,在燃烧前加入到黑液中,在燃烧过程中形成的铝酸钠,绿液中与硅酸钠反应生成硅铝酸钠复合体沉淀而被除去。In step 1, the pretreatment of the dilute black liquor includes slag removal, oxidation and silicon removal. The slag removal is to remove the fine fibers and various residues contained in the black liquor; the oxidation is to oxidize Na 2 S in the black liquor to stable Na 2 SO 4 and Na 2 S 2 O 3 , the specific reaction is: 2Na 2 S+2O 2 +H 2 O=Na 2 S 2 O 3 +2NaOH, Na 2 S+2O 2 =Na 2 SO 4 ; Using the bauxite desilicon method, an appropriate amount of bauxite is added to the black liquor before combustion, and the sodium aluminate formed during the combustion process reacts with sodium silicate in the green liquor to form a sodium aluminosilicate complex precipitate. and removed.
步骤1中对经预处理后的稀黑液蒸发浓缩,具体为:首先采用混流式加热,加热过程中水分汽化逸出浓度浓缩到45%,再使用烟气余热加热浓缩至浓度值为50%。In step 1, the pretreated dilute black liquor is evaporated and concentrated, specifically: firstly adopting mixed-flow heating, during the heating process, the concentration of water vaporization escapes is concentrated to 45%, and then the residual heat of flue gas is used to heat and concentrate to the concentration value of 50% .
步骤2、对经步骤1浓缩后的黑液采用喷射炉燃烧,黑液中的有机物燃烧后产生的高温烟气在炉内上升,无机物熔融从燃烧炉下方的溜槽流入溶解槽中,且溶解于稀白液或水中形成绿液,绿液成分包括Na2CO3、Na2S;Step 2. The black liquor concentrated in step 1 is burned in a jet furnace. The high-temperature flue gas generated by the combustion of the organic matter in the black liquor rises in the furnace, and the inorganic matter melts from the chute below the combustion furnace into the dissolving tank, and dissolves. Form green liquor in dilute white liquor or water, and the components of green liquor include Na 2 CO 3 and Na 2 S;
步骤2具体按照以下步骤实施:Step 2 is implemented according to the following steps:
步骤2.1、第一阶段:入炉黑液在热炉气的作用下进一步干燥至浓度为85%时,形成黑灰,烟气中所含的SO2、SO3以及CO2与黑液中的活性碱及有机结合钠起化学反应;黑液中的游离NaOH和大部分的Na2S均转变为Na2CO3、Na2SO3、Na2SO4和Na2S2O3;Step 2.1, the first stage: when the black liquor entering the furnace is further dried to a concentration of 85% under the action of the hot furnace gas, black ash is formed, and the SO 2 , SO 3 and CO 2 contained in the flue gas and the black liquor The active alkali and organically bound sodium react chemically; the free NaOH and most of Na 2 S in the black liquor are transformed into Na 2 CO 3 , Na 2 SO 3 , Na 2 SO 4 and Na 2 S 2 O 3 ;
步骤2.2、第二阶段:黑灰最后剩下的水分逐渐被蒸发掉,温度迅速升高到350℃~450℃时,有机物快速分解为CH3OH、CH3COOH、CH3SH、H2S、酚、低分子的醛酸以及结构复杂的烷基硫化物有机气体,并与进入炉膛的二次风和三次风混合后发生气相燃烧,生成SO2、SO3、CO、H2O、H2S气体;还有一部分有机物发生碳化作用,变成元素碳,供芒硝还原用;另外,与有机物结合生成的钠化合物也发生分解反应,生成Na2CO3;Step 2.2, the second stage: the last remaining water of the black ash is gradually evaporated. When the temperature rises rapidly to 350℃~450℃, the organic matter is rapidly decomposed into CH 3 OH, CH 3 COOH, CH 3 SH, H 2 S , phenol, low molecular aldehyde acid and complex structure of alkyl sulfide organic gas, and mixed with the secondary air and tertiary air entering the furnace, gas-phase combustion occurs to generate SO 2 , SO 3 , CO, H 2 O, H 2 S gas; a part of the organic matter is carbonized and becomes elemental carbon for the reduction of mirabilite; in addition, the sodium compound formed by combining with the organic matter also undergoes a decomposition reaction to generate Na 2 CO 3 ;
为使黑灰在还原条件下充分燃烧,入炉空气需预先加热到140℃,一次风在燃烧炉的还原区加入,二次风在还原区的上方及黑液喷射入口附近加入,三次风在黑液喷枪上方加入,一、二、三次风的风量分配比大致为50:20:30,一次风压力为0.8KPa、二、三次风压力为1.5KPa。In order to fully burn the black ash under reducing conditions, the air entering the furnace should be preheated to 140°C. Add above the black liquor spray gun, the air volume distribution ratio of the primary, secondary and tertiary air is roughly 50:20:30, the primary air pressure is 0.8KPa, and the secondary and tertiary air pressure is 1.5KPa.
步骤2.3、第三阶段:使无机物在高温下熔融,同时补加芒硝。Step 2.3, the third stage: the inorganic matter is melted at high temperature, and then mirabilite is added at the same time.
步骤3、对溶解于稀白液或水中的无机熔融物所形成的绿液进行苛化反应;Step 3, causticizing the green liquor formed by the inorganic melt dissolved in dilute white liquor or water;
步骤3具体按照以下步骤实施:Step 3 is implemented according to the following steps:
步骤3.1、将溶解槽中的绿液进行澄清,除去不溶性的杂质绿泥,然后将剩余的粗绿泥进行洗涤、沉淀处理以回收绿泥中夹带的绿液;Step 3.1, clarify the green liquor in the dissolving tank, remove the insoluble impurity green mud, then wash and precipitate the remaining crude green mud to recover the green liquor entrained in the green mud;
步骤3.2、将澄清后的绿液和绿泥中夹带的绿液进行消化反应,具体反应为CaO+H2O=Ca(OH)2,加料时间控制在60min,为了进一步提高苛化效率,需要将CaO进行研磨,将粒径控制为3μm;Step 3.2. Digest the clarified green liquor and the green liquor entrained in the green mud, the specific reaction is CaO+H 2 O=Ca(OH) 2 , and the feeding time is controlled at 60min. In order to further improve the causticizing efficiency, it is necessary to The CaO is ground, and the particle size is controlled to 3 μm;
步骤3.3、石灰消化后形成的初始苛化乳液进入分离器,将未消化的石灰渣料除去后,送到连续苛化器系统苛化,具体反应为Ca(OH)2+Na2CO3=CaCO3↓+2NaOH;Step 3.3. The initial causticized emulsion formed after lime digestion enters the separator, and after removing the undigested lime residue, it is sent to the continuous causticizer system for causticization. The specific reaction is Ca(OH) 2 +Na 2 CO 3 = CaCO 3 ↓+2NaOH;
步骤3.4、从连续苛化器系统出来的浓白液送到白液澄清器中,以除去白液中的白泥;Step 3.4, the concentrated white liquor from the continuous causticizer system is sent to the white liquor clarifier to remove the white mud in the white liquor;
步骤3.5、澄清的白液经过进一步的过滤处理后送入浓白液槽,然后送到蒸煮工段,从白液过滤设备来的白泥送到白泥洗涤器经热水稀释、洗涤、混合均匀后得到稀白液和白泥乳液;Step 3.5. After further filtration treatment, the clarified white liquor is sent to the concentrated white liquor tank, and then sent to the cooking section. The white mud from the white liquor filtration equipment is sent to the white mud scrubber for dilution, washing and mixing with hot water. Afterwards, dilute white liquor and white mud emulsion are obtained;
步骤3.6、将稀白液和白泥乳液送入离心机系统进行处理,再次回收部分稀白液,而白泥送入白泥处理系统。In step 3.6, the dilute white liquor and white mud emulsion are sent to the centrifuge system for processing, part of the dilute white liquor is recovered again, and the white mud is sent to the white mud treatment system.
步骤4、对绿液苛化反应产生的产物进行回收利用,具体按照以下步骤实施:Step 4. Recycling the product produced by the green liquor causticization reaction is implemented according to the following steps:
步骤4.1、将所述步骤3苛化工段出来的白泥送入煅烧炉后,在高温炉气的作用下蒸发干燥并形成颗粒状白泥;Step 4.1, after the lime mud from the causticization section of the step 3 is sent into the calciner, evaporate and dry under the effect of high temperature furnace gas and form granular white mud;
步骤4.2、干燥后的白泥进一步预热到600℃,CaCO3开始分解;然后将白泥加热至825℃,此时CaCO3开始迅速分解,即进入煅烧段,生成可循环利用的CaO,具体反应为:CaCO3=CaO+CO2↑。Step 4.2. The dried white mud is further preheated to 600°C, and CaCO 3 begins to decompose; then the white mud is heated to 825° C. At this time, CaCO 3 begins to decompose rapidly, that is, it enters the calcination section to generate recyclable CaO. The reaction is: CaCO 3 =CaO+CO 2 ↑.
实施例2Example 2
本发明一种制浆废液综合回收利用的方法,流程图如图1所示,具体按照以下步骤实施:A method for comprehensive recycling and utilization of pulping waste liquid of the present invention, the flowchart is shown in Figure 1, and is specifically implemented according to the following steps:
步骤1、从制浆蒸煮液中提取出稀黑液,然后对稀黑液预处理,最后采用混流式间接蒸发法对经预处理后的稀黑液蒸发浓缩;Step 1. Extract the dilute black liquor from the pulping and cooking liquor, then pretreat the dilute black liquor, and finally adopt the mixed-flow indirect evaporation method to evaporate and concentrate the pretreated dilute black liquor;
步骤1中提取出的稀黑液成分为70%可燃烧的有机物质,30%无机物,无机物包括蒸煮废液中残余的化学药品,如NaOH,Na2S,以及和制浆原料中的有机物化合的金属盐基、制浆原料本身带来的无机成分。The dilute black liquor extracted in step 1 is composed of 70% combustible organic matter and 30% inorganic matter. The inorganic matter includes the residual chemicals in the cooking waste liquor, such as NaOH, Na 2 S, and the raw materials for pulping. The metal salt base of organic compounds and the inorganic components brought by the pulping raw material itself.
步骤1中对稀黑液预处理包括除渣、氧化、除硅,除渣即对黑液中含有的细小纤维和各种残渣进行去除;氧化即将黑液中的Na2S氧化为稳定的Na2SO4和Na2S2O3,具体反应为:2Na2S+2O2+H2O=Na2S2O3+2NaOH,Na2S+2O2=Na2SO4;除硅即采用铝土矿除硅法,将适量的铝土矿,在燃烧前加入到黑液中,在燃烧过程中形成的铝酸钠,绿液中与硅酸钠反应生成硅铝酸钠复合体沉淀而被除去。In step 1, the pretreatment of the dilute black liquor includes slag removal, oxidation and silicon removal. The slag removal is to remove the fine fibers and various residues contained in the black liquor; the oxidation is to oxidize Na 2 S in the black liquor to stable Na 2 SO 4 and Na 2 S 2 O 3 , the specific reaction is: 2Na 2 S+2O 2 +H 2 O=Na 2 S 2 O 3 +2NaOH, Na 2 S+2O 2 =Na 2 SO 4 ; Using the bauxite desilicon method, an appropriate amount of bauxite is added to the black liquor before combustion, and the sodium aluminate formed during the combustion process reacts with sodium silicate in the green liquor to form a sodium aluminosilicate complex precipitate. and removed.
步骤1中对经预处理后的稀黑液蒸发浓缩,具体为:首先采用混流式加热,加热过程中水分汽化逸出浓度浓缩到45%~48%,再使用烟气余热加热浓缩至浓度值为65%。In step 1, the pretreated dilute black liquor is evaporated and concentrated, specifically: firstly adopting mixed-flow heating, during the heating process, the concentration of water vaporization escapes is concentrated to 45% to 48%, and then the waste heat of flue gas is used to heat and concentrate to the concentration value is 65%.
步骤2、对经步骤1浓缩后的黑液采用喷射炉燃烧,黑液中的有机物燃烧后产生的高温烟气在炉内上升,无机物熔融从燃烧炉下方的溜槽流入溶解槽中,且溶解于稀白液或水中形成绿液,绿液成分包括Na2CO3、Na2S;Step 2. The black liquor concentrated in step 1 is burned in a jet furnace. The high-temperature flue gas generated by the combustion of the organic matter in the black liquor rises in the furnace, and the inorganic matter melts from the chute below the combustion furnace into the dissolving tank, and dissolves. Form green liquor in dilute white liquor or water, and the components of green liquor include Na 2 CO 3 and Na 2 S;
步骤2具体按照以下步骤实施:Step 2 is implemented according to the following steps:
步骤2.1、第一阶段:入炉黑液在热炉气的作用下进一步干燥至浓度为85%时,形成黑灰,烟气中所含的SO2、SO3以及CO2与黑液中的活性碱及有机结合钠起化学反应;黑液中的游离NaOH和大部分的Na2S均转变为Na2CO3、Na2SO3、Na2SO4和Na2S2O3;Step 2.1, the first stage: when the black liquor entering the furnace is further dried to a concentration of 85% under the action of the hot furnace gas, black ash is formed, and the SO 2 , SO 3 and CO 2 contained in the flue gas and the black liquor The active alkali and organically bound sodium react chemically; the free NaOH and most of Na 2 S in the black liquor are transformed into Na 2 CO 3 , Na 2 SO 3 , Na 2 SO 4 and Na 2 S 2 O 3 ;
步骤2.2、第二阶段:黑灰最后剩下的水分逐渐被蒸发掉,温度迅速升高到350℃~450℃时,有机物快速分解为CH3OH、CH3COOH、CH3SH、H2S、酚、低分子的醛酸以及结构复杂的烷基硫化物有机气体,并与进入炉膛的二次风和三次风混合后发生气相燃烧,生成SO2、SO3、CO、H2O、H2S气体;还有一部分有机物发生碳化作用,变成元素碳,供芒硝还原用;另外,与有机物结合生成的钠化合物也发生分解反应,生成Na2CO3;Step 2.2, the second stage: the last remaining water of the black ash is gradually evaporated. When the temperature rises rapidly to 350℃~450℃, the organic matter is rapidly decomposed into CH 3 OH, CH 3 COOH, CH 3 SH, H 2 S , phenol, low molecular aldehyde acid and complex structure of alkyl sulfide organic gas, and mixed with the secondary air and tertiary air entering the furnace, gas-phase combustion occurs to generate SO 2 , SO 3 , CO, H 2 O, H 2 S gas; a part of the organic matter is carbonized and becomes elemental carbon for the reduction of mirabilite; in addition, the sodium compound formed by combining with the organic matter also undergoes a decomposition reaction to generate Na 2 CO 3 ;
为使黑灰在还原条件下充分燃烧,入炉空气需预先加热到140~150℃,一次风在燃烧炉的还原区加入,二次风在还原区的上方及黑液喷射入口附近加入,三次风在黑液喷枪上方加入,一、二、三次风的风量分配比大致为50:20:30,一次风压力为0.8~1.2KPa、二、三次风压力为3KPa。In order to fully burn the black ash under reducing conditions, the air entering the furnace needs to be preheated to 140-150 °C, the primary air is added in the reduction area of the combustion furnace, and the secondary air is added above the reduction area and near the injection inlet of the black liquor, three times. The air is added above the black liquor spray gun. The air volume distribution ratio of the primary, secondary and tertiary air is roughly 50:20:30, the primary air pressure is 0.8-1.2KPa, and the secondary and tertiary air pressure is 3KPa.
步骤2.3、第三阶段:使无机物在高温下熔融,同时补加芒硝。Step 2.3, the third stage: the inorganic matter is melted at high temperature, and then mirabilite is added at the same time.
步骤3、对溶解于稀白液或水中的无机熔融物所形成的绿液进行苛化反应;Step 3, causticizing the green liquor formed by the inorganic melt dissolved in dilute white liquor or water;
步骤3具体按照以下步骤实施:Step 3 is implemented according to the following steps:
步骤3.1、将溶解槽中的绿液进行澄清,除去不溶性的杂质绿泥,然后将剩余的粗绿泥进行洗涤、沉淀处理以回收绿泥中夹带的绿液;Step 3.1, clarify the green liquor in the dissolving tank, remove the insoluble impurity green mud, then wash and precipitate the remaining crude green mud to recover the green liquor entrained in the green mud;
步骤3.2、将澄清后的绿液和绿泥中夹带的绿液进行消化反应,具体反应为CaO+H2O=Ca(OH)2,加料时间控制在130min,为了进一步提高苛化效率,需要将CaO进行研磨,将粒径控制为4μm;Step 3.2. Digest the clarified green liquor and the green liquor entrained in the green mud, the specific reaction is CaO+H 2 O=Ca(OH) 2 , and the feeding time is controlled at 130min. In order to further improve the causticizing efficiency, it is necessary to The CaO is ground, and the particle size is controlled to 4 μm;
步骤3.3、石灰消化后形成的初始苛化乳液进入分离器,将未消化的石灰渣料除去后,送到连续苛化器系统苛化,具体反应为Ca(OH)2+Na2CO3=CaCO3↓+2NaOH;Step 3.3. The initial causticized emulsion formed after lime digestion enters the separator, and after removing the undigested lime residue, it is sent to the continuous causticizer system for causticization. The specific reaction is Ca(OH) 2 +Na 2 CO 3 = CaCO 3 ↓+2NaOH;
步骤3.4、从连续苛化器系统出来的浓白液送到白液澄清器中,以除去白液中的白泥;Step 3.4, the concentrated white liquor from the continuous causticizer system is sent to the white liquor clarifier to remove the white mud in the white liquor;
步骤3.5、澄清的白液经过进一步的过滤处理后送入浓白液槽,然后送到蒸煮工段,从白液过滤设备来的白泥送到白泥洗涤器经热水稀释、洗涤、混合均匀后得到稀白液和白泥乳液;Step 3.5. After further filtration treatment, the clarified white liquor is sent to the concentrated white liquor tank, and then sent to the cooking section. The white mud from the white liquor filtration equipment is sent to the white mud scrubber for dilution, washing and mixing with hot water. Afterwards, dilute white liquor and white mud emulsion are obtained;
步骤3.6、将稀白液和白泥乳液送入离心机系统进行处理,再次回收部分稀白液,而白泥送入白泥处理系统。In step 3.6, the dilute white liquor and white mud emulsion are sent to the centrifuge system for processing, part of the dilute white liquor is recovered again, and the white mud is sent to the white mud treatment system.
步骤4、对绿液苛化反应产生的产物进行回收利用,具体按照以下步骤实施:Step 4. Recycling the product produced by the green liquor causticization reaction is implemented according to the following steps:
步骤4.1、将所述步骤3苛化工段出来的白泥送入煅烧炉后,在高温炉气的作用下蒸发干燥并形成颗粒状白泥;Step 4.1, after the lime mud from the causticization section of the step 3 is sent into the calciner, evaporate and dry under the effect of high temperature furnace gas and form granular white mud;
步骤4.2、干燥后的白泥进一步预热到600℃,CaCO3开始分解;然后将白泥加热至825℃,此时CaCO3开始迅速分解,即进入煅烧段,生成可循环利用的CaO,具体反应为:CaCO3=CaO+CO2↑。Step 4.2. The dried white mud is further preheated to 600°C, and CaCO 3 begins to decompose; then the white mud is heated to 825° C. At this time, CaCO 3 begins to decompose rapidly, that is, it enters the calcination section to generate recyclable CaO. The reaction is: CaCO 3 =CaO+CO 2 ↑.
实施例3Example 3
本发明一种制浆废液综合回收利用的方法,流程图如图1所示,具体按照以下步骤实施:A method for comprehensive recycling and utilization of pulping waste liquid of the present invention, the flowchart is shown in Figure 1, and is specifically implemented according to the following steps:
步骤1、从制浆蒸煮液中提取出稀黑液,然后对稀黑液预处理,最后采用混流式间接蒸发法对经预处理后的稀黑液蒸发浓缩;Step 1. Extract the dilute black liquor from the pulping and cooking liquor, then pretreat the dilute black liquor, and finally adopt the mixed-flow indirect evaporation method to evaporate and concentrate the pretreated dilute black liquor;
步骤1中提取出的稀黑液成分为70%可燃烧的有机物质,30%无机物,无机物包括蒸煮废液中残余的化学药品,如NaOH,Na2S,以及和制浆原料中的有机物化合的金属盐基、制浆原料本身带来的无机成分。The dilute black liquor extracted in step 1 is composed of 70% combustible organic matter and 30% inorganic matter. The inorganic matter includes the residual chemicals in the cooking waste liquor, such as NaOH, Na 2 S, and the raw materials for pulping. The metal salt base of organic compounds and the inorganic components brought by the pulping raw material itself.
步骤1中对稀黑液预处理包括除渣、氧化、除硅,除渣即对黑液中含有的细小纤维和各种残渣进行去除;氧化即将黑液中的Na2S氧化为稳定的Na2SO4和Na2S2O3,具体反应为:2Na2S+2O2+H2O=Na2S2O3+2NaOH,Na2S+2O2=Na2SO4;除硅即采用铝土矿除硅法,将适量的铝土矿,在燃烧前加入到黑液中,在燃烧过程中形成的铝酸钠,绿液中与硅酸钠反应生成硅铝酸钠复合体沉淀而被除去。In step 1, the pretreatment of the dilute black liquor includes slag removal, oxidation and silicon removal. The slag removal is to remove the fine fibers and various residues contained in the black liquor; the oxidation is to oxidize Na 2 S in the black liquor to stable Na 2 SO 4 and Na 2 S 2 O 3 , the specific reaction is: 2Na 2 S+2O 2 +H 2 O=Na 2 S 2 O 3 +2NaOH, Na 2 S+2O 2 =Na 2 SO 4 ; Using the bauxite desilicon method, an appropriate amount of bauxite is added to the black liquor before combustion, and the sodium aluminate formed during the combustion process reacts with sodium silicate in the green liquor to form a sodium aluminosilicate complex precipitate. and removed.
步骤1中对经预处理后的稀黑液蒸发浓缩,具体为:首先采用混流式加热,加热过程中水分汽化逸出浓度浓缩到46%,再使用烟气余热加热浓缩至浓度值为60%。In step 1, the pretreated dilute black liquor is evaporated and concentrated, specifically: first, mixed-flow heating is adopted, and the concentration of water vaporized during the heating process is concentrated to 46%, and then the residual heat of flue gas is used to heat and concentrate to a concentration value of 60%. .
步骤2、对经步骤1浓缩后的黑液采用喷射炉燃烧,黑液中的有机物燃烧后产生的高温烟气在炉内上升,无机物熔融从燃烧炉下方的溜槽流入溶解槽中,且溶解于稀白液或水中形成绿液,绿液成分包括Na2CO3、Na2S;Step 2. The black liquor concentrated in step 1 is burned in a jet furnace. The high-temperature flue gas generated by the combustion of the organic matter in the black liquor rises in the furnace, and the inorganic matter melts from the chute below the combustion furnace into the dissolving tank, and dissolves. Form green liquor in dilute white liquor or water, and the components of green liquor include Na 2 CO 3 and Na 2 S;
步骤2具体按照以下步骤实施:Step 2 is implemented according to the following steps:
步骤2.1、第一阶段:入炉黑液在热炉气的作用下进一步干燥至浓度为85%时,形成黑灰,烟气中所含的SO2、SO3以及CO2与黑液中的活性碱及有机结合钠起化学反应;黑液中的游离NaOH和大部分的Na2S均转变为Na2CO3、Na2SO3、Na2SO4和Na2S2O3;Step 2.1, the first stage: when the black liquor entering the furnace is further dried to a concentration of 85% under the action of the hot furnace gas, black ash is formed, and the SO 2 , SO 3 and CO 2 contained in the flue gas and the black liquor The active alkali and organically bound sodium react chemically; the free NaOH and most of Na 2 S in the black liquor are transformed into Na 2 CO 3 , Na 2 SO 3 , Na 2 SO 4 and Na 2 S 2 O 3 ;
步骤2.2、第二阶段:黑灰最后剩下的水分逐渐被蒸发掉,温度迅速升高到350℃~450℃时,有机物快速分解为CH3OH、CH3COOH、CH3SH、H2S、酚、低分子的醛酸以及结构复杂的烷基硫化物有机气体,并与进入炉膛的二次风和三次风混合后发生气相燃烧,生成SO2、SO3、CO、H2O、H2S气体;还有一部分有机物发生碳化作用,变成元素碳,供芒硝还原用;另外,与有机物结合生成的钠化合物也发生分解反应,生成Na2CO3;Step 2.2, the second stage: the last remaining water of the black ash is gradually evaporated. When the temperature rises rapidly to 350℃~450℃, the organic matter is rapidly decomposed into CH 3 OH, CH 3 COOH, CH 3 SH, H 2 S , phenol, low molecular aldehyde acid and complex structure of alkyl sulfide organic gas, and mixed with the secondary air and tertiary air entering the furnace, gas-phase combustion occurs to generate SO 2 , SO 3 , CO, H 2 O, H 2 S gas; a part of the organic matter is carbonized and becomes elemental carbon for the reduction of mirabilite; in addition, the sodium compound formed by combining with the organic matter also undergoes a decomposition reaction to generate Na 2 CO 3 ;
为使黑灰在还原条件下充分燃烧,入炉空气需预先加热到140~150℃,一次风在燃烧炉的还原区加入,二次风在还原区的上方及黑液喷射入口附近加入,三次风在黑液喷枪上方加入,一、二、三次风的风量分配比大致为50:20:30,一次风压力为1.0KPa、二、三次风压力为2.2KPa。In order to fully burn the black ash under reducing conditions, the air entering the furnace needs to be preheated to 140-150 °C, the primary air is added in the reduction area of the combustion furnace, and the secondary air is added above the reduction area and near the injection inlet of the black liquor, three times. The air is added above the black liquor spray gun. The air volume distribution ratio of the primary, secondary and tertiary air is roughly 50:20:30, the primary air pressure is 1.0KPa, and the secondary and tertiary air pressure is 2.2KPa.
步骤2.3、第三阶段:使无机物在高温下熔融,同时补加芒硝。Step 2.3, the third stage: the inorganic matter is melted at high temperature, and then mirabilite is added at the same time.
步骤3、对溶解于稀白液或水中的无机熔融物所形成的绿液进行苛化反应;Step 3, causticizing the green liquor formed by the inorganic melt dissolved in dilute white liquor or water;
步骤3具体按照以下步骤实施:Step 3 is implemented according to the following steps:
步骤3.1、将溶解槽中的绿液进行澄清,除去不溶性的杂质绿泥,然后将剩余的粗绿泥进行洗涤、沉淀处理以回收绿泥中夹带的绿液;Step 3.1, clarify the green liquor in the dissolving tank, remove the insoluble impurity green mud, then wash and precipitate the remaining crude green mud to recover the green liquor entrained in the green mud;
步骤3.2、将澄清后的绿液和绿泥中夹带的绿液进行消化反应,具体反应为CaO+H2O=Ca(OH)2,加料时间控制在60~130min,为了进一步提高苛化效率,需要将CaO进行研磨,将粒径控制为3.5μm;Step 3.2, the clarified green liquor and the green liquor entrained in the green mud are digested, the specific reaction is CaO+H 2 O=Ca(OH) 2 , and the feeding time is controlled at 60-130min, in order to further improve the causticizing efficiency , CaO needs to be ground, and the particle size is controlled to 3.5 μm;
步骤3.3、石灰消化后形成的初始苛化乳液进入分离器,将未消化的石灰渣料除去后,送到连续苛化器系统苛化,具体反应为Ca(OH)2+Na2CO3=CaCO3↓+2NaOH;Step 3.3. The initial causticized emulsion formed after lime digestion enters the separator, and after removing the undigested lime residue, it is sent to the continuous causticizer system for causticization. The specific reaction is Ca(OH) 2 +Na 2 CO 3 = CaCO 3 ↓+2NaOH;
步骤3.4、从连续苛化器系统出来的浓白液送到白液澄清器中,以除去白液中的白泥;Step 3.4, the concentrated white liquor from the continuous causticizer system is sent to the white liquor clarifier to remove the white mud in the white liquor;
步骤3.5、澄清的白液经过进一步的过滤处理后送入浓白液槽,然后送到蒸煮工段,从白液过滤设备来的白泥送到白泥洗涤器经热水稀释、洗涤、混合均匀后得到稀白液和白泥乳液;Step 3.5. After further filtration treatment, the clarified white liquor is sent to the concentrated white liquor tank, and then sent to the cooking section. The white mud from the white liquor filtration equipment is sent to the white mud scrubber for dilution, washing and mixing with hot water. Afterwards, dilute white liquor and white mud emulsion are obtained;
步骤3.6、将稀白液和白泥乳液送入离心机系统进行处理,再次回收部分稀白液,而白泥送入白泥处理系统。In step 3.6, the dilute white liquor and white mud emulsion are sent to the centrifuge system for processing, part of the dilute white liquor is recovered again, and the white mud is sent to the white mud treatment system.
步骤4、对绿液苛化反应产生的产物进行回收利用,具体按照以下步骤实施:Step 4. Recycling the product produced by the green liquor causticization reaction is implemented according to the following steps:
步骤4.1、将所述步骤3苛化工段出来的白泥送入煅烧炉后,在高温炉气的作用下蒸发干燥并形成颗粒状白泥;Step 4.1, after the lime mud from the causticization section of the step 3 is sent into the calciner, evaporate and dry under the effect of high temperature furnace gas and form granular white mud;
步骤4.2、干燥后的白泥进一步预热到600℃,CaCO3开始分解;然后将白泥加热至825℃,此时CaCO3开始迅速分解,即进入煅烧段,生成可循环利用的CaO,具体反应为:CaCO3=CaO+CO2↑。Step 4.2. The dried white mud is further preheated to 600°C, and CaCO 3 begins to decompose; then the white mud is heated to 825° C. At this time, CaCO 3 begins to decompose rapidly, that is, it enters the calcination section to generate recyclable CaO. The reaction is: CaCO 3 =CaO+CO 2 ↑.
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