WO2016019774A1 - Procédé de préparation d'un mélange de résidus alcalins d'élimination de chlore par utilisation de résidus alcalins par le biais d'un processus ammoniac-soude et son application - Google Patents
Procédé de préparation d'un mélange de résidus alcalins d'élimination de chlore par utilisation de résidus alcalins par le biais d'un processus ammoniac-soude et son application Download PDFInfo
- Publication number
- WO2016019774A1 WO2016019774A1 PCT/CN2015/083350 CN2015083350W WO2016019774A1 WO 2016019774 A1 WO2016019774 A1 WO 2016019774A1 CN 2015083350 W CN2015083350 W CN 2015083350W WO 2016019774 A1 WO2016019774 A1 WO 2016019774A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- alkali
- powder
- mixture
- returned
- sand
- Prior art date
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/50—Improvements relating to the production of bulk chemicals
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P40/00—Technologies relating to the processing of minerals
- Y02P40/10—Production of cement, e.g. improving or optimising the production methods; Cement grinding
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
Definitions
- the invention belongs to the field of industrial solid waste treatment, and particularly relates to an alkali alkali residue and a sand returning stone treatment method and an application method thereof.
- soda ash As a basic chemical raw material, soda ash is mainly used in construction materials, chemicals, chemical pesticides, non-ferrous metals, textiles and other industries. It plays an important role in the national economy and is known as the “mother of chemical industry”. At present, the production of soda ash mainly includes the trona method, the ammonia-alkali method and the combined alkali method. The production of soda ash in China is mainly based on the ammonia-alkali method.
- Alkali slag is an industrial waste residue produced during the process of producing soda ash by the ammonia-base method.
- the main components of the alkali slag are calcium carbonate, calcium sulfate and oxides such as aluminum, iron and silicon, and contain a large amount of chloride.
- the annual production of alkali slag in China exceeds 300. Ten thousand tons.
- Alkali slag is a worldwide problem due to its high alkalinity and high chloride ion content.
- the main methods of its use are to prepare engineering soil for land preparation, dam construction, roadbed and pavement base layer, etc.
- soil improver and smoke are prepared by using alkali residue.
- how to effectively reduce the chloride ion content in the alkali residue has not been broken, and the excessive chloride ion content in the alkali residue after treatment also affects its application in various fields.
- the most effective method for dechlorination of alkali residue is water washing and dechlorination, but the washing efficiency is low, multiple washings are required, and a large amount of water is consumed, which also seriously affects its application.
- the higher chloride ion content can be controlled.
- the chloride ion content of the alkali residue is controlled at 1.5% after one water washing and pressure filtration. Left and right.
- the high-efficiency dechlorination method of alkali slag has become a major problem that restricts the sustainable development of the soda ash industry.
- the solid waste of the soda ash plant also has a returning sand returning stone, which is generated for each ton of soda ash produced.
- the object of the present invention is to provide a chlorine removal alkali slag mixture by using an alkali-base alkali residue for good chlorine removal effect.
- a method for preparing a mixture of chlor-alkali residues by using an alkali-base alkali residue comprising the steps of:
- Step 1 First, returning the sand to the stone and crushing it into a sand returning powder;
- Step 2 Soak the returning stone powder in water 0.5 to 14 After dissolving the calcined calcium oxide, the digested returning stone powder, alkali residue and water are mixed, and the ratio of the dry mass of the returned sand powder and the alkali residue after digestion is 2:8. To 5 : 5, the total mass of water is 1.5 to 8 times the total dry mass of the returned sand returning powder and alkali residue after digestion;
- Step 3 Perform a pressure filtration treatment to obtain a dechlorination alkali residue mixture having a chloride ion content of 0.30% lower than the total mass of the solid in the mixture.
- intermittent agitation is also performed during the step 2 in which the returning sand powder is immersed.
- One or more of fly ash, limestone powder, slag powder, slag powder, steel slag powder and stone powder may be used to replace the returning sand powder of less than or equal to 50%.
- the first method further comprises the steps of separately separating and recovering calcium hydroxide in the re-returned stone powder after digestion, and using it for soda ash production.
- Another object of the present invention is to provide an application of the above-described chlorine-removing alkali residue mixture, the scheme being as follows:
- the chlorine-removing alkali residue mixture can be used as a mixed material of cement, mineral admixture of concrete and mortar, engineering soil, filler, flue gas desulfurizer, soil treatment agent , adsorbents and carriers.
- the chlorinated alkali residue mixture is used as a mixed material of cement, a mineral admixture of concrete and mortar, a filler, a flue gas desulfurizer, a soil treatment agent, an adsorbent and a carrier, and is first dried, crushed, and ground. The mixture was treated to obtain a powdery chlorinated alkali residue mixture.
- the dechlorination alkali residue mixture can replace 30% or less of the cementitious material.
- the alkali slag particles are small, the particle size is between several micrometers and several tens of micrometers, and contains a large amount of pores, so the moisture content and chloride ion content of the alkali slag after pressure filtration are high.
- the chloride ion in the alkali residue is mainly present in water, and the particle grading adjustment material may be added to reduce the porosity, thereby reducing the chloride ion content in the alkali residue after pressure filtration.
- the returning sand powder after water digestion is selected as the particle grading adjustment material. Due to the dissolution of calcium oxide, the surface of the returned sand powder after water digestion is rough, which can reduce the chloride ion content more effectively.
- the present invention has the following advantages:
- the dechlorination effect of the invention is good, and the chlorine ion content (calculated as the total mass of the solid) can be made less than 0.30% by using a single water washing and pressure filtration treatment, which greatly reduces the chloride ion content compared with the conventional primary water washing pressure filtration.
- a method for preparing a mixture of chlor-alkali residues by using an alkali-base alkali residue comprising the steps of:
- Step 1 First, returning the sand to the stone and crushing it into a sand returning powder;
- Step 2 Soak the returning stone powder in water 0.5 Days dissolve the burned calcium oxide, and intermittently stir when returning the sand to the stone powder, and then mix the returned sand returning powder, alkali residue and water after the digestion, based on the mass percentage of the material, the back-returned stone powder after digestion and The ratio of alkali residue is 2 : 8, the total mass of water is 8 times the total mass of returning stone powder and alkali residue after digestion;
- Step 3 Perform a pressure filtration treatment to obtain a chlorinated alkali residue mixture having a chloride ion content of 0.28% of the total solid mass in the mixture.
- one or more of fly ash, limestone powder, slag powder, slag powder, steel slag powder and stone powder may be replaced by no more than 50%. Returning sand to stone powder.
- the calcium hydroxide in the re-returned stone powder after digestion is first separated and recovered, and used for soda ash production.
- a method for preparing a mixture of chlor-alkali residues by using an alkali-base alkali residue comprising the steps of:
- Step 1 First, returning the sand to the stone and crushing it into a sand returning powder;
- Step 2 Soak the returning sand powder in water 3 Days dissolve the burned calcium oxide, and intermittently stir when returning the sand to the stone powder, and then mix the returned sand returning powder, alkali residue and water after the digestion, based on the mass percentage of the material, the back-returned stone powder after digestion and The ratio of alkali residue is 3 :7, the total mass of water is 7 times of the total mass of returning stone powder and alkali residue after digestion;
- Step 3 Perform a pressure filtration treatment to obtain a chlorinated alkali residue mixture having a chloride ion content of 0.08% of the total solid mass in the mixture.
- one or more of fly ash, limestone powder, slag powder, slag powder, steel slag powder and stone powder may be replaced by no more than 50%. Returning sand to stone powder.
- the calcium hydroxide in the re-returned stone powder after digestion is first separated and recovered, and used for soda ash production.
- a method for preparing a mixture of chlor-alkali residues by using an alkali-base alkali residue comprising the steps of:
- Step 1 First, returning the sand to the stone and crushing it into a sand returning powder;
- Step 2 Soak the returning stone powder in water 7 Days dissolve the burned calcium oxide, and intermittently stir when returning the sand to the stone powder, and then mix the returned sand returning powder, alkali residue and water after the digestion, based on the mass percentage of the material, the back-returned stone powder after digestion and The ratio of alkali residue is 5 : 5, the total mass of water is 3 times the total mass of returning stone powder and alkali residue after digestion;
- Step 3 Perform a pressure filtration treatment to obtain a chlorinated alkali residue mixture having a chloride ion content of 0.05% of the total solid mass in the mixture.
- one or more of fly ash, limestone powder, slag powder, slag powder, steel slag powder and stone powder may be replaced by no more than 50%. Returning sand to stone powder.
- the calcium hydroxide in the re-returned stone powder after digestion is first separated and recovered, and used for soda ash production.
- a method for preparing a mixture of chlor-alkali residues by using an alkali-base alkali residue comprising the steps of:
- Step 1 First, returning the sand to the stone and crushing it into a sand returning powder;
- Step 2 soak in water 14 Days dissolve the burned calcium oxide, and intermittently stir when returning the sand to the stone powder, and then mix the returned sand returning powder, alkali residue and water after the digestion, based on the mass percentage of the material, the back-returned stone powder after digestion and The ratio of alkali residue is 5 : 5, the total mass of water is 1.5 times the total mass of returning stone powder and alkali residue after digestion;
- Step 3 Perform a pressure filtration treatment to obtain a chlorinated alkali residue mixture having a chloride ion content of 0.09% of the total solid mass in the mixture.
- one or more of fly ash, limestone powder, slag powder, slag powder, steel slag powder and stone powder may be replaced by no more than 50%. Returning sand to stone powder.
- the calcium hydroxide in the re-returned stone powder after digestion is first separated and recovered, and used for soda ash production.
- a method for preparing a mixture of chlor-alkali residues by using an alkali-base alkali residue comprising the steps of:
- Step 1 First, returning the sand to the stone and crushing it into a sand returning powder;
- Step 2 Soak the returned sand powder, alkali residue and water, and soak 0.5
- the calcined calcium oxide is dissolved in days, and the ratio of the mass of the returned sand powder to the alkali residue is 2:8, and the total mass of the water is 8 times the total dry mass of the returned sand powder and the alkali residue;
- Step 3 Perform a pressure filtration treatment to obtain a chlorinated alkali residue mixture having a chloride ion content of 0.28% of the total solid mass in the mixture.
- one or more of fly ash, limestone powder, slag powder, slag powder, steel slag powder and stone powder may be replaced by no more than 50%. Returning sand to stone powder.
- a method for preparing a mixture of chlor-alkali residues by using an alkali-base alkali residue comprising the steps of:
- Step 1 First, returning the sand to the stone and crushing it into a sand returning powder;
- Step 2 Soak the returned sand powder, alkali residue and water, and soak 3
- the calcined calcium oxide is dissolved in days, and the ratio of the mass of the returned sand powder to the alkali residue is 3:7, and the total mass of the water is 7 times the total dry mass of the returned sand powder and the alkali residue;
- Step 3 Perform a pressure filtration treatment to obtain a chlorinated alkali residue mixture having a chloride ion content of 0.08% of the total solid mass in the mixture.
- one or more of fly ash, limestone powder, slag powder, slag powder, steel slag powder and stone powder may be replaced by no more than 50%. Returning sand to stone powder.
- the chlor-alkali residue mixture is used as a mineral admixture for concrete, and the chlor-alkali residue is formulated to have a water content of 250%.
- the suspension is used to replace 10% of the cement with chlor-alkali slag (dry basis).
- the concrete strength is basically unchanged and does not cause corrosion of the steel in the structure.
- the powdered dechlorination alkali residue mixture after drying and crushing and grinding the dechlorination alkali residue mixture is used as a mixed material of cement, wherein the powdery dechlorination alkali residue mixture has a particle size of 80
- the micron sieve residue is less than 5%, the amount is 30%, the amount of slag powder is 22%, the amount of cement clinker is 45%, and the amount of gypsum is 3%.
- Cement performance meets masonry cement 12.5 Grade requirements, and high water retention, water retention rate of 96.5%.
- the powdered dechlorination alkali residue mixture after drying and crushing and grinding the dechlorination alkali residue mixture is classified according to different particle sizes, wherein less than 3 Micron powdered chlorinated alkali residue mixture used as rubber filler, greater than or equal to 3 A micron powdered chlor-alkali residue mixture is used as a flue gas desulfurizer.
- the porosity of the mixture of dechlorination alkali slag is utilized to improve the mechanical properties of the rubber and the efficiency of the flue gas desulfurizer. When used as a flue gas desulfurizer, it can replace the limestone powder originally used, saving energy and environmental protection.
- the chlor-alkali residue mixture When used in engineering soil, it can be directly used for earthwork filling, and the chlorine ion content is low, and it will not cause harm to the environment.
Abstract
L'invention concerne un procédé de préparation d'un mélange de résidus alcalins d'élimination de chlore par utilisation de résidus alcalins par le biais d'un processus ammoniac-soude. Ce procédé comprend les étapes suivantes : étape 1, broyer du sable de rebut et des pierres de rebut pour obtenir de la poudre de sable de rebut et de pierres de rebut; étape 2, faire tremper la poudre de sable de rebut et de pierres de rebut dans l'eau pendant 0,5 à 14 jours, mettre en digestion de l'oxyde de calcium brûlé, puis mélanger la poudre de sable de rebut et de pierres de rebut digérée, des résidus alcalins et de l'eau, le rapport entre la masse sèche de cette poudre digérée et les résidus alcalins représentant de 2/8 à 5/5 du pourcentage massique des matériaux, et la masse totale de l'eau est de 1,5 à 8 fois égale à la masse totale sèche de ladite poudre de sable de rebut et de pierres de rebut digérée et des résidus alcalins; ou bien mélanger la poudre de sable de rebut et de pierres de rebut, les résidus alcalins et l'eau, puis faire tremper ce mélange pendant 0,5 à 14 jours, et mettre en digestion l'oxyde de calcium calciné; étape 3, exécuter un traitement de pressage-filtrage, puis obtenir le mélange de résidus alcalins d'élimination de chlore dont le contenu en ions chlore est inférieur à 0,30 % de la masse totale des solides dans le mélange. L'invention concerne également une application du mélange de résidus alcalins d'élimination de chlore. Ce procédé possède de bons effets d'élimination du chlore, est simple à mettre en œuvre, efficace du point de vue énergétique et sans danger pour l'environnement.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2016568449A JP6404948B2 (ja) | 2014-08-06 | 2015-07-06 | アンモニアソーダ法による苛性スラッジから脱塩素苛性スラッジ混合物を調製する方法及びその応用 |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201410383247.6A CN104190690B (zh) | 2014-08-06 | 2014-08-06 | 一种利用氨碱法碱渣制备除氯碱渣混合物的方法及应用 |
CN201410383247.6 | 2014-08-06 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO2016019774A1 true WO2016019774A1 (fr) | 2016-02-11 |
Family
ID=52076137
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/CN2015/083350 WO2016019774A1 (fr) | 2014-08-06 | 2015-07-06 | Procédé de préparation d'un mélange de résidus alcalins d'élimination de chlore par utilisation de résidus alcalins par le biais d'un processus ammoniac-soude et son application |
Country Status (3)
Country | Link |
---|---|
JP (1) | JP6404948B2 (fr) |
CN (1) | CN104190690B (fr) |
WO (1) | WO2016019774A1 (fr) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN112723842A (zh) * | 2021-01-07 | 2021-04-30 | 广州大学 | 一种蒸压加气混凝土砌块及其制备方法 |
CN113082846A (zh) * | 2021-03-26 | 2021-07-09 | 路德环境科技股份有限公司 | 氨碱厂碱渣的除杂净化工艺和净化装置 |
CN114768603A (zh) * | 2022-05-27 | 2022-07-22 | 路德环境科技股份有限公司 | 应用于碱渣处理工艺的黄土化浆系统 |
CN116119999A (zh) * | 2022-10-12 | 2023-05-16 | 东南大学 | 一种碱渣轻质土及其制备方法与应用 |
Families Citing this family (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104190690B (zh) * | 2014-08-06 | 2016-05-04 | 华南理工大学 | 一种利用氨碱法碱渣制备除氯碱渣混合物的方法及应用 |
CN105060828A (zh) * | 2015-07-16 | 2015-11-18 | 浙江大学宁波理工学院 | 道路工程用脱氯碱渣固化土 |
CN105330488B (zh) * | 2015-12-08 | 2019-01-18 | 华北理工大学 | 一种含腐植酸复合土壤调理剂及其制备方法和应用 |
CN106186767A (zh) * | 2016-07-15 | 2016-12-07 | 华南理工大学 | 一种无机粉体保水剂及其制备方法与应用 |
CN106220018B (zh) * | 2016-07-15 | 2018-09-14 | 华南理工大学 | 一种无机粉体保水剂的回转烘干制备方法与应用 |
CN106186769B (zh) * | 2016-07-15 | 2019-01-15 | 华南理工大学 | 一种碱渣保水剂及其回转烘干制备方法与应用 |
CN106167362B (zh) * | 2016-07-15 | 2019-01-18 | 华南理工大学 | 一种碱渣保水剂及其制备方法与应用 |
CN108863118A (zh) * | 2018-08-15 | 2018-11-23 | 淮安市水泥厂有限公司 | 一种碱渣水泥超细粉及其制备方法 |
CN111454003A (zh) * | 2020-04-29 | 2020-07-28 | 山东海天生物化工有限公司 | 纯碱生产中返砂的回收利用方法 |
CN111848034B (zh) * | 2020-07-16 | 2022-05-10 | 广州大学 | 一种湿拌砂浆及制备工艺 |
CN112573553B (zh) * | 2020-10-26 | 2023-02-03 | 山东海天生物化工有限公司 | 一种纯碱生产时返砂回收利用的方法 |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2004033893A (ja) * | 2002-07-02 | 2004-02-05 | Taiheiyo Cement Corp | 廃棄物の再資源化処理方法 |
CN101966999A (zh) * | 2010-11-11 | 2011-02-09 | 中国地质大学(北京) | 高铝粉煤灰两步碱溶法提取氧化铝和白炭黑的方法 |
CN103664242A (zh) * | 2013-09-18 | 2014-03-26 | 薛彦辉 | 碱渣的处理方法 |
CN103769407A (zh) * | 2012-10-26 | 2014-05-07 | 中国石油化工股份有限公司 | 一种含硫碱渣的再生方法 |
CN104190690A (zh) * | 2014-08-06 | 2014-12-10 | 华南理工大学 | 一种利用氨碱法碱渣制备除氯碱渣混合物的方法及应用 |
Family Cites Families (15)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB1545789A (en) * | 1975-06-04 | 1979-05-16 | Ici Ltd | Manufacture of calcium carbonate magnesium bicarbonate magnesium carbonate and calcium sulphate |
FR2459210A1 (fr) * | 1979-06-19 | 1981-01-09 | Solvay | Procede de fabrication d'un mortier hydraulique, materiau d'isolation thermique a structure cellulaire a liant hydraulique et procede de fabrication d'un tel materiau |
JPS5645824A (en) * | 1979-09-19 | 1981-04-25 | Central Glass Co Ltd | Treatment of ammonia soda process waste |
CN1182646A (zh) * | 1996-11-14 | 1998-05-27 | 乔希海 | 硅化碱渣土的制造方法 |
CN1141270C (zh) * | 1996-11-29 | 2004-03-10 | 天津渤海化工有限责任公司天津碱厂 | 碱渣土的制造方法 |
JP3304300B2 (ja) * | 1997-07-14 | 2002-07-22 | 太平洋セメント株式会社 | セメント原料化処理方法 |
JP4118495B2 (ja) * | 2000-08-23 | 2008-07-16 | 株式会社トクヤマ | 泥漿の再利用方法 |
JP4358014B2 (ja) * | 2004-03-29 | 2009-11-04 | 株式会社荏原製作所 | 焼却灰及びセメントキルンダストの水洗方法並びに装置 |
JP2007069185A (ja) * | 2005-09-09 | 2007-03-22 | Unitika Ltd | 無機物の洗浄方法 |
CN101780464B (zh) * | 2010-02-02 | 2012-02-01 | 山东海化集团有限公司 | 一种脱除氨碱法纯碱废渣氯离子的方法 |
JP5716892B2 (ja) * | 2010-11-30 | 2015-05-13 | 三菱マテリアル株式会社 | 汚泥の洗浄方法 |
CN102070287B (zh) * | 2010-12-03 | 2013-07-03 | 广州市天益三和能源环保有限公司 | 一种降低氨碱厂白泥中氯离子的工艺 |
JP5954863B2 (ja) * | 2012-02-29 | 2016-07-20 | 太平洋セメント株式会社 | ごみ焼却灰の処理方法及び処理装置 |
CN103157652B (zh) * | 2013-04-09 | 2015-03-11 | 东莞市嘉汇环保科技有限公司 | 一种纯碱厂工业中产生的固体废弃物制造脱硫剂的方法 |
CN104192881A (zh) * | 2014-08-06 | 2014-12-10 | 华南理工大学 | 一种利用返砂返石制备多用途固体废渣的方法及应用 |
-
2014
- 2014-08-06 CN CN201410383247.6A patent/CN104190690B/zh active Active
-
2015
- 2015-07-06 JP JP2016568449A patent/JP6404948B2/ja not_active Expired - Fee Related
- 2015-07-06 WO PCT/CN2015/083350 patent/WO2016019774A1/fr active Application Filing
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2004033893A (ja) * | 2002-07-02 | 2004-02-05 | Taiheiyo Cement Corp | 廃棄物の再資源化処理方法 |
CN101966999A (zh) * | 2010-11-11 | 2011-02-09 | 中国地质大学(北京) | 高铝粉煤灰两步碱溶法提取氧化铝和白炭黑的方法 |
CN103769407A (zh) * | 2012-10-26 | 2014-05-07 | 中国石油化工股份有限公司 | 一种含硫碱渣的再生方法 |
CN103664242A (zh) * | 2013-09-18 | 2014-03-26 | 薛彦辉 | 碱渣的处理方法 |
CN104190690A (zh) * | 2014-08-06 | 2014-12-10 | 华南理工大学 | 一种利用氨碱法碱渣制备除氯碱渣混合物的方法及应用 |
Non-Patent Citations (1)
Title |
---|
YAO, WEICHONG ET AL.: "DISCUSSION ABOUT PRODUCING GEL BUILDING MATERIALS (ALINITE CEMENT) BY WET PROCESS FROM WASTE RESIDUE GENERATED IN SODA PRODUCTION BY AMMONIA-SODA PROCESS", SODA INDUSTRY, no. 01, 28 February 1997 (1997-02-28), pages 27 - 31 * |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN112723842A (zh) * | 2021-01-07 | 2021-04-30 | 广州大学 | 一种蒸压加气混凝土砌块及其制备方法 |
CN113082846A (zh) * | 2021-03-26 | 2021-07-09 | 路德环境科技股份有限公司 | 氨碱厂碱渣的除杂净化工艺和净化装置 |
CN114768603A (zh) * | 2022-05-27 | 2022-07-22 | 路德环境科技股份有限公司 | 应用于碱渣处理工艺的黄土化浆系统 |
CN116119999A (zh) * | 2022-10-12 | 2023-05-16 | 东南大学 | 一种碱渣轻质土及其制备方法与应用 |
Also Published As
Publication number | Publication date |
---|---|
CN104190690B (zh) | 2016-05-04 |
JP2017520391A (ja) | 2017-07-27 |
JP6404948B2 (ja) | 2018-10-17 |
CN104190690A (zh) | 2014-12-10 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
WO2016019774A1 (fr) | Procédé de préparation d'un mélange de résidus alcalins d'élimination de chlore par utilisation de résidus alcalins par le biais d'un processus ammoniac-soude et son application | |
Ismail et al. | Engineering properties of treated recycled concrete aggregate (RCA) for structural applications | |
KR100464666B1 (ko) | 굴패각을 이용한 지반개량형 고화재 제조방법 | |
Juan et al. | Re-use of ceramic wastes in construction | |
CN109516707B (zh) | 一种抑制碱-骨料反应的再生骨料的制备方法 | |
JP6325837B2 (ja) | 初期ひび割れの発生が少ない改質フライアッシュ含有舗装用コンクリート、および初期ひび割れの発生が少ない改質フライアッシュ含有舗装用コンクリートの製造方法 | |
Fang et al. | Fast enhancement of recycled fine aggregates properties by wet carbonation | |
JP2015514662A (ja) | 補助セメント質材料(SCMs)の製造方法 | |
CN112456946A (zh) | 一种纳米微膨胀无机注浆材料及其制备方法 | |
CN104192881A (zh) | 一种利用返砂返石制备多用途固体废渣的方法及应用 | |
CN113149564A (zh) | 一种再生混凝土的制备方法 | |
CN113549463A (zh) | 一种修复重金属污染土的固化剂及其应用 | |
CN107021703B (zh) | 复合高效超微细粉灌浆材料 | |
KR100836598B1 (ko) | 폐 콘크리트를 활용한 콘크리트 모르타르 조성물 | |
CN104310811A (zh) | 水泥及制备方法 | |
CN110627466A (zh) | 一种钛石膏废渣抹灰砂浆及其制备方法 | |
CN103553545A (zh) | 一种高效固化剂 | |
CN111635206A (zh) | 一种抗渗和抗碳化固废混凝土及其制备方法 | |
JP2007314393A (ja) | コンクリートのアルカリシリカ反応抑制方法 | |
CN112250392B (zh) | 一种用于道路建设的人工碎石及其制备方法 | |
Premkumar et al. | Performance of fly ash based geopolymer concrete with partial replacement of fine aggregate by steel mill slag | |
CN110240438B (zh) | 一种用于水泥基材料密实增强剂及其制备方法 | |
TWI711595B (zh) | 砂漿組成物、砂漿及砂漿硬固物 | |
CN113336463A (zh) | 一种利用铝灰制备水泥、混凝土膨胀剂的方法 | |
Kibriya | Crushed limestone waste as supplementary cementing material for high strength concrete |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
121 | Ep: the epo has been informed by wipo that ep was designated in this application |
Ref document number: 15829869 Country of ref document: EP Kind code of ref document: A1 |
|
ENP | Entry into the national phase |
Ref document number: 2016568449 Country of ref document: JP Kind code of ref document: A |
|
NENP | Non-entry into the national phase |
Ref country code: DE |
|
122 | Ep: pct application non-entry in european phase |
Ref document number: 15829869 Country of ref document: EP Kind code of ref document: A1 |