CN115838233A - A method for comprehensive utilization of red mud - Google Patents
A method for comprehensive utilization of red mud Download PDFInfo
- Publication number
- CN115838233A CN115838233A CN202211246443.XA CN202211246443A CN115838233A CN 115838233 A CN115838233 A CN 115838233A CN 202211246443 A CN202211246443 A CN 202211246443A CN 115838233 A CN115838233 A CN 115838233A
- Authority
- CN
- China
- Prior art keywords
- red mud
- metal
- acid
- waste
- solid
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 238000000034 method Methods 0.000 title claims abstract description 19
- 229910052751 metal Inorganic materials 0.000 claims abstract description 29
- 239000002184 metal Substances 0.000 claims abstract description 29
- 239000002699 waste material Substances 0.000 claims abstract description 29
- 239000002253 acid Substances 0.000 claims abstract description 24
- 229910052755 nonmetal Inorganic materials 0.000 claims abstract description 21
- 238000006243 chemical reaction Methods 0.000 claims abstract description 18
- 239000007788 liquid Substances 0.000 claims abstract description 16
- 238000000197 pyrolysis Methods 0.000 claims abstract description 15
- 239000007787 solid Substances 0.000 claims abstract description 11
- 238000000926 separation method Methods 0.000 claims abstract description 9
- 238000006386 neutralization reaction Methods 0.000 claims abstract description 8
- 230000002378 acidificating effect Effects 0.000 claims abstract description 7
- 230000003213 activating effect Effects 0.000 claims abstract description 4
- 239000008213 purified water Substances 0.000 claims abstract description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 4
- 230000004913 activation Effects 0.000 claims description 10
- 239000007789 gas Substances 0.000 claims description 10
- 239000007769 metal material Substances 0.000 claims description 9
- 239000002912 waste gas Substances 0.000 claims description 5
- 238000003763 carbonization Methods 0.000 claims description 4
- 230000004048 modification Effects 0.000 claims description 4
- 238000012986 modification Methods 0.000 claims description 4
- 239000002910 solid waste Substances 0.000 claims description 4
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 3
- 239000011230 binding agent Substances 0.000 claims description 3
- 230000005484 gravity Effects 0.000 claims description 3
- 229910052739 hydrogen Inorganic materials 0.000 claims description 3
- 239000001257 hydrogen Substances 0.000 claims description 3
- 229910052760 oxygen Inorganic materials 0.000 claims description 3
- 239000001301 oxygen Substances 0.000 claims description 3
- 230000035484 reaction time Effects 0.000 claims description 3
- 150000002739 metals Chemical class 0.000 claims description 2
- 150000002843 nonmetals Chemical class 0.000 claims description 2
- 238000007781 pre-processing Methods 0.000 abstract 1
- 239000000126 substance Substances 0.000 description 7
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 6
- 239000004576 sand Substances 0.000 description 6
- 239000000853 adhesive Substances 0.000 description 5
- 230000001070 adhesive effect Effects 0.000 description 5
- 229910052782 aluminium Inorganic materials 0.000 description 5
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 5
- 239000008204 material by function Substances 0.000 description 5
- 239000002585 base Substances 0.000 description 4
- 239000011449 brick Substances 0.000 description 4
- 239000003513 alkali Substances 0.000 description 3
- 230000006872 improvement Effects 0.000 description 3
- 229910052742 iron Inorganic materials 0.000 description 3
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- 239000004826 Synthetic adhesive Substances 0.000 description 2
- 239000000654 additive Substances 0.000 description 2
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 2
- 239000000227 bioadhesive Substances 0.000 description 2
- 239000004566 building material Substances 0.000 description 2
- 239000003054 catalyst Substances 0.000 description 2
- 239000004568 cement Substances 0.000 description 2
- 239000000919 ceramic Substances 0.000 description 2
- 239000003245 coal Substances 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000003292 glue Substances 0.000 description 2
- 230000008676 import Effects 0.000 description 2
- 229910021645 metal ion Inorganic materials 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 229910052761 rare earth metal Inorganic materials 0.000 description 2
- 150000002910 rare earth metals Chemical class 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 159000000000 sodium salts Chemical class 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- -1 sulfur ions Chemical class 0.000 description 2
- RSWGJHLUYNHPMX-UHFFFAOYSA-N Abietic-Saeure Natural products C12CCC(C(C)C)=CC2=CCC2C1(C)CCCC2(C)C(O)=O RSWGJHLUYNHPMX-UHFFFAOYSA-N 0.000 description 1
- 239000002028 Biomass Substances 0.000 description 1
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 229920001353 Dextrin Polymers 0.000 description 1
- 239000004375 Dextrin Substances 0.000 description 1
- 229910002651 NO3 Inorganic materials 0.000 description 1
- KHPCPRHQVVSZAH-HUOMCSJISA-N Rosin Natural products O(C/C=C/c1ccccc1)[C@H]1[C@H](O)[C@@H](O)[C@@H](O)[C@@H](CO)O1 KHPCPRHQVVSZAH-HUOMCSJISA-N 0.000 description 1
- 229920001800 Shellac Polymers 0.000 description 1
- 229920002472 Starch Polymers 0.000 description 1
- 239000010426 asphalt Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 235000019425 dextrin Nutrition 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000000284 extract Substances 0.000 description 1
- 238000009313 farming Methods 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 238000002309 gasification Methods 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 238000005984 hydrogenation reaction Methods 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 239000010806 kitchen waste Substances 0.000 description 1
- 235000021190 leftovers Nutrition 0.000 description 1
- 244000144972 livestock Species 0.000 description 1
- 239000010871 livestock manure Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 238000005065 mining Methods 0.000 description 1
- 239000004058 oil shale Substances 0.000 description 1
- 150000002894 organic compounds Chemical class 0.000 description 1
- 239000010815 organic waste Substances 0.000 description 1
- 239000003209 petroleum derivative Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 235000019353 potassium silicate Nutrition 0.000 description 1
- 244000144977 poultry Species 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 235000018102 proteins Nutrition 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 238000012827 research and development Methods 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000004208 shellac Substances 0.000 description 1
- ZLGIYFNHBLSMPS-ATJNOEHPSA-N shellac Chemical compound OCCCCCC(O)C(O)CCCCCCCC(O)=O.C1C23[C@H](C(O)=O)CCC2[C@](C)(CO)[C@@H]1C(C(O)=O)=C[C@@H]3O ZLGIYFNHBLSMPS-ATJNOEHPSA-N 0.000 description 1
- 229940113147 shellac Drugs 0.000 description 1
- 235000013874 shellac Nutrition 0.000 description 1
- 238000005245 sintering Methods 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- NTHWMYGWWRZVTN-UHFFFAOYSA-N sodium silicate Chemical compound [Na+].[Na+].[O-][Si]([O-])=O NTHWMYGWWRZVTN-UHFFFAOYSA-N 0.000 description 1
- 235000019698 starch Nutrition 0.000 description 1
- 239000008107 starch Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
- 229920003051 synthetic elastomer Polymers 0.000 description 1
- 229920003002 synthetic resin Polymers 0.000 description 1
- 239000000057 synthetic resin Substances 0.000 description 1
- 239000005061 synthetic rubber Substances 0.000 description 1
- KHPCPRHQVVSZAH-UHFFFAOYSA-N trans-cinnamyl beta-D-glucopyranoside Natural products OC1C(O)C(O)C(CO)OC1OCC=CC1=CC=CC=C1 KHPCPRHQVVSZAH-UHFFFAOYSA-N 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Landscapes
- Treatment Of Sludge (AREA)
Abstract
Description
技术领域technical field
本发明涉及煤气化灰渣处理技术领域,尤其涉及一种赤泥综合利用的方法。The invention relates to the technical field of coal gasification ash treatment, in particular to a method for comprehensive utilization of red mud.
背景技术Background technique
赤泥是铝工业提取氧化铝时排除的污染性废渣。一般平均每生产1吨氧化铝,附带生产1.0~2.0吨的赤泥。Red mud is the polluting waste that is removed when the aluminum industry extracts alumina. Generally, for every 1 ton of alumina produced, 1.0 to 2.0 tons of red mud is incidentally produced.
国内外多家研究机构都在积极地开展对赤泥综合利用的研发,并且也取得了一些成果,但至今却无一项成果能真正地实现大规模的产业化应用,更没有哪些成果对赤泥的利用超过30%。其中的一个主要原因就是赤泥的含碱量太高。现有技术中有3种处理赤泥的方法,分别为拜尔法、烧结法和烧结-拜尔联合法,三种处理方法都是向赤泥中添加碱,因此在赤泥处理过程中产生的Na2O含量(质量分数)高达9~11%,属高危污染物。所以高碱量是赤泥开发利用的瓶颈。Many research institutions at home and abroad are actively carrying out research and development on the comprehensive utilization of red mud, and have also achieved some results, but so far none of the results can truly achieve large-scale industrial application, let alone any results that are beneficial to red mud. The utilization of mud exceeds 30%. One of the main reasons is that the alkali content of red mud is too high. There are three methods of processing red mud in the prior art, namely Bayer method, sintering method and sintering-Bayer combined method. The three processing methods are to add alkali to red mud, so during the red mud treatment process produces The Na 2 O content (mass fraction) is as high as 9-11%, which is a high-risk pollutant. So high alkalinity is the bottleneck of red mud development and utilization.
发明内容Contents of the invention
本发明的目的就在于提供一种赤泥综合利用的方法,具有能充分处理赤泥,并利用多相态酸性废物达到已废治废、解决赤泥处理高效,对环境友好节约资源的优点。The purpose of the present invention is to provide a method for comprehensive utilization of red mud, which has the advantages of being able to fully treat red mud, and utilizing multi-phase acidic waste to achieve waste treatment, solving the problem of efficient treatment of red mud, being friendly to the environment and saving resources.
为了实现上述目的,本发明采用的技术方案是:一种赤泥综合利用的方法,包括以下步骤:In order to achieve the above object, the technical solution adopted in the present invention is: a method for comprehensive utilization of red mud, comprising the following steps:
S1、预处理,对赤泥进行脱碱改性,将多相态酸性废物与赤泥进行酸碱中和反应;S1, pretreatment, carry out dealkalization modification on red mud, and carry out acid-base neutralization reaction between multiphase acidic waste and red mud;
S2、初级分离,将赤泥与多相态酸性废物酸碱中和反应后产物进行固液气分离;S2, primary separation, the solid-liquid-gas separation of the product after the acid-base neutralization reaction between the red mud and the multi-phase acidic waste;
S3、将步骤S2中分离出的固体和液体分别通过电磁分离器与重选器进行二次分离,并将固体分离为金属物和非金属物,将液体分为金属物、非金属和净化水;S3. The solid and liquid separated in step S2 are separated twice through the electromagnetic separator and re-selector, and the solid is separated into metal and non-metal, and the liquid is divided into metal, non-metal and purified water. ;
S4、对金属物和非金属物分别进行热解反应;S4, performing pyrolysis reactions on metals and non-metals respectively;
S5、对热解反应后的金属物通过电磁分离器与重选器进行精分离,将金属物中的金属成分与非金属成分分离;S5. Finely separate the metal objects after the pyrolysis reaction through an electromagnetic separator and a gravity separator, and separate the metal components and non-metal components in the metal objects;
S6、将步骤S4热解反应后的非金属物和步骤S5中的非金属成分进行活化处理。S6, performing activation treatment on the non-metallic substance after the pyrolysis reaction in step S4 and the non-metallic component in step S5.
所述步骤S1中的多相态酸性废物为酸性废气、酸性废液和酸性固体废物。The multiphase acid waste in the step S1 is acid waste gas, acid waste liquid and acid solid waste.
所述步骤S4中热解反应的温度为400-1200摄氏度,反应时间为40-240分钟。The temperature of the pyrolysis reaction in the step S4 is 400-1200 degrees Celsius, and the reaction time is 40-240 minutes.
步骤S6中的活化处理为活化-石化,将非金属物活化后,添加粘合剂使得活化后的非金属凝结成矿石体。The activation treatment in step S6 is activation-petrochemical. After activating the non-metal, a binder is added to make the activated non-metal coagulate into an ore body.
步骤S6中的活化处理为活化-碳化,将非金属物活化后,进行高温绝氧,使得非金属物中的氧元素和氢元素析出。The activation treatment in step S6 is activation-carbonization. After the non-metallic substance is activated, high-temperature anaerobic treatment is performed, so that oxygen and hydrogen elements in the non-metallic substance are precipitated.
与现有技术相比,本发明的优点在于:将金属物部分采用电磁协同超重力技术,分选回收铁、铝、钠盐、稀土等金属成分,回收率大于90%;采用活化石化技术制成水泥、陶瓷及添加剂,砖及透水砖,人工砂石等规模化绿色建材和路基产业化应用,其中,人工砂石的规模化应用意义重大,还可扭转我国花大量外汇进口沙石的被动局面。Compared with the prior art, the present invention has the advantages of: adopting the electromagnetism synergistic supergravity technology to separate and recover metal components such as iron, aluminum, sodium salt, rare earth, etc., with a recovery rate greater than 90%; Large-scale green building materials and roadbed industrial applications such as cement, ceramics and additives, bricks and permeable bricks, artificial sand and gravel. Among them, the large-scale application of artificial sand and gravel is of great significance, and it can also reverse the passive situation of my country spending a large amount of foreign exchange to import sand and gravel. situation.
具体实施方式Detailed ways
下面将对本发明作进一步说明。The present invention will be further described below.
实施例:一种赤泥综合利用的方法,包括以下步骤:Embodiment: a method for comprehensive utilization of red mud, comprising the following steps:
S1、预处理,对赤泥进行脱碱改性,将赤泥到入反应池中,并向反应池中到入多相态酸性废物,使得赤泥与多相态酸性废物发生酸碱中和反应;所述多相态酸性废物为酸性废气、酸性废液和酸性固体废物,其中,酸性废气可以是化工行业未经净化处理的酸性废气、排放的二氧化碳等,例如燃煤电站、燃煤高炉、燃煤锅炉等未经除尘、脱硫、脱硝的废气,同时由于赤泥多孔,能够将废气中的灰尘、硫离子、硝离子等吸附,极大的降低化工行业的处理废气的成本,另一方面利用废气中CO2对化工行业的碳减排具有重大的意义。S1, pretreatment, carry out dealkalization modification on the red mud, put the red mud into the reaction tank, and put the multi-phase acid waste into the reaction tank, so that the red mud and the multi-phase acid waste undergo acid-base neutralization reaction; the multiphase acid waste is acid waste gas, acid waste liquid and acid solid waste, wherein the acid waste gas can be unpurified acid waste gas in the chemical industry, carbon dioxide discharged, etc., such as coal-fired power stations, coal-fired blast furnaces , coal-fired boilers and other exhaust gases that have not been dedusted, desulfurized, and denitrated. At the same time, due to the porous red mud, it can absorb dust, sulfur ions, and nitrate ions in the exhaust gas, which greatly reduces the cost of treating exhaust gas in the chemical industry. Another On the one hand, the use of CO 2 in exhaust gas is of great significance to the carbon emission reduction of the chemical industry.
酸性废液可以是各个行业产生的废酸液,酸性废水等;酸性固体废物可以是化工、矿业等行业未经净化处理的酸性废渣,酸渣等;通过合理利用多相态酸性废物来实现赤泥的大规模低成本的脱碱改性处理,并实现以废治废降低了赤泥和工业废物的处理成本。Acid waste liquid can be waste acid liquid and acid waste water produced by various industries; acid solid waste can be unpurified acid waste residue and acid slag in chemical industry, mining and other industries; through rational use of multiphase acid waste to realize Large-scale and low-cost dealkalization modification treatment of mud, and realize waste treatment by waste treatment, which reduces the treatment cost of red mud and industrial waste.
S2、初级分离,对酸碱中和反应后产物进行固液气分离,分离成固、液、气三种物质,分离出的气体收集并通过气体净化装置净化后排放。S2. Primary separation. The product after the acid-base neutralization reaction is separated into solid, liquid and gas, and separated into three substances: solid, liquid and gas. The separated gas is collected and purified by a gas purification device before being discharged.
S3、将步骤S2中分离出的固体和液体分别通过电磁分离器与重选器进行二次分离,并将固体分离为金属物和非金属物,将液体分为金属物、非金属和净化水,其中金属物主要含有铁、铝等金属离子,金属物和非金属物均为固体状。S3. The solid and liquid separated in step S2 are separated twice through the electromagnetic separator and re-selector, and the solid is separated into metal and non-metal, and the liquid is divided into metal, non-metal and purified water. , in which metal objects mainly contain metal ions such as iron and aluminum, and both metal objects and non-metal objects are solid.
S4、对金属物和非金属物分别进行热解反应,热解反应的温度为400-1200 摄氏度,反应时间为40-240分钟。S4. Carry out pyrolysis reaction on the metal object and the non-metal object respectively, the temperature of the pyrolysis reaction is 400-1200 degrees Celsius, and the reaction time is 40-240 minutes.
S5、对热解反应后的金属物通过电磁分离器与重选器进行精分离,将金属物中的金属成分与非金属成分分离;金属成分为铁、铝、钠盐、稀土等并将金属成分进行分选回收,回收率大于90%,剩余的非金属成分残渣转入非金属物进行下一步处理。S5. Finely separate the metal objects after the pyrolysis reaction through an electromagnetic separator and a gravity separator, and separate the metal components in the metal objects from the non-metal components; the metal components are iron, aluminum, sodium salt, rare earth, etc. and the metal The components are sorted and recovered, and the recovery rate is greater than 90%, and the remaining non-metallic component residues are transferred to non-metallic substances for further processing.
S6、将步骤S4热解反应后的非金属物和步骤S5中的非金属成分进行活化处理。其中活化处理分为活化-石化和活化-碳化;活化-石化是通过粘合剂将复杂组分粉体物、液体物在不加热的条件下自然凝结成高强度矿石体的技术,将分离完高价值成分后(如铝、钙等金属离子)的非金属物制成水泥、陶瓷及添加剂、砖及透水砖、人工砂石等规模化绿色建材和路基产业化应用,其中,人工砂石的规模化应用意义重大,还可扭转我国花大量外汇进口沙石的被动局面;所述粘合剂,包括天然粘合剂和合成粘合剂,其中天然粘合剂取自于自然界中的物质。包括淀粉、蛋白质、糊精、动物胶、虫胶、皮胶、松香等生物粘合剂;也包括沥青等矿物粘合剂;合成粘合剂指人工合成的物质,包括水玻璃等无机粘合剂,以及合成树脂、合成橡胶等有机粘合剂。S6, performing activation treatment on the non-metallic substance after the pyrolysis reaction in step S4 and the non-metallic component in step S5. Among them, the activation treatment is divided into activation-petrochemical and activation-carbonization; activation-petrochemical is a technology that uses binders to naturally condense complex component powders and liquids into high-strength ore bodies without heating. High-value components (such as aluminum, calcium and other metal ions) are made into cement, ceramics and additives, bricks and permeable bricks, artificial sand and other large-scale green building materials and roadbed industrial applications. Among them, artificial sand Large-scale application is of great significance, and it can also reverse the passive situation that my country spends a large amount of foreign exchange to import sand and gravel; the adhesive includes natural adhesives and synthetic adhesives, wherein natural adhesives are derived from substances in nature. Including starch, protein, dextrin, animal glue, shellac, hide glue, rosin and other biological adhesives; also including asphalt and other mineral adhesives; synthetic adhesives refer to artificially synthesized substances, including inorganic adhesives such as water glass agent, and organic adhesives such as synthetic resin and synthetic rubber.
活化-碳化是将非金属物活化后,进行高温绝氧,使得非金属物中的氧元素和氢元素析出,从而将非金属物制成功能材料,包括环保功能材料和催化剂功能材料,其中环保功能材料,大量用于三废治理及土壤修复与改良,催化剂功能材料,用于煤、生物质、油页岩、某些有机化合物和石油渣油的加氢饱和反应。在另一个实施例中,还可以对非金属物进行温度大于80摄氏度的高温活化处理,非金属物在高温活化无害化后直接做建设用地土地的土壤,同时还可以在非金属物中加入桔杆、畜禽粪便等种养殖废物,餐厨垃圾,污水厂污泥,食品生产下脚料及废渣等有机质废物,经高温活化用于赤泥等废渣堆场等地的土地修复和复耕,或土地改良,或盐碱地、荒漠化地的复耕土壤。Activation-carbonization is to activate the non-metallic substance and perform high-temperature anaerobic, so that the oxygen and hydrogen elements in the non-metallic substance are precipitated, so that the non-metallic substance is made into functional materials, including environmentally friendly functional materials and catalyst functional materials, among which environmental protection Functional materials are widely used in the treatment of three wastes and soil restoration and improvement. Catalyst functional materials are used in the hydrogenation saturation reaction of coal, biomass, oil shale, certain organic compounds and petroleum residue. In another embodiment, non-metallic objects can also be subjected to high-temperature activation treatment with a temperature greater than 80 degrees Celsius. After the non-metallic objects are activated and harmless at high temperature, they can be directly used as soil for construction land. Farming waste such as orange stalks, livestock and poultry manure, kitchen waste, sewage plant sludge, food production leftovers and waste residues and other organic wastes, after high temperature activation, they can be used for land restoration and reclamation in red mud and other waste residue dumps, or Land improvement, or recultivation of saline-alkali land and desertification land.
本文中应用了具体个例对本发明的原理及实施方式进行了阐述,以上实施例的说明只是用于帮助理解本发明的方法及其核心思想;同时,对于本领域的一般技术人员,依据本发明的思想,在具体实施方式及应用范围上均会有改变之处,对本发明的变更和改进将是可能的,而不会超出附加权利要求所规定的构思和范围,综上所述,本说明书内容不应理解为对本发明的限制。In this paper, specific examples have been used to illustrate the principle and implementation of the present invention. The description of the above embodiments is only used to help understand the method of the present invention and its core idea; meanwhile, for those of ordinary skill in the art, according to the present invention Thoughts, there will be changes in the specific implementation and scope of application, and changes and improvements to the present invention will be possible without going beyond the concept and scope specified in the appended claims. In summary, this specification The content should not be construed as a limitation of the invention.
Claims (5)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202211246443.XA CN115838233A (en) | 2022-10-12 | 2022-10-12 | A method for comprehensive utilization of red mud |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202211246443.XA CN115838233A (en) | 2022-10-12 | 2022-10-12 | A method for comprehensive utilization of red mud |
Publications (1)
Publication Number | Publication Date |
---|---|
CN115838233A true CN115838233A (en) | 2023-03-24 |
Family
ID=85575602
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202211246443.XA Pending CN115838233A (en) | 2022-10-12 | 2022-10-12 | A method for comprehensive utilization of red mud |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN115838233A (en) |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101927255A (en) * | 2009-09-03 | 2010-12-29 | 昆明理工大学 | Method for carbon dioxide suspension dealkalization of red mud in alumina plant |
CN102500592A (en) * | 2011-09-16 | 2012-06-20 | 茌平县信发盛吉赤泥处理有限公司 | Method for comprehensively utilizing alumina red mud |
CN103073066A (en) * | 2012-11-01 | 2013-05-01 | 吕富华 | Innocent treatment and resource utilization method for red mud |
US20200299806A1 (en) * | 2016-03-25 | 2020-09-24 | Fakon Vállalkozási Kft. | Process for processing red mud and producing rare-earth metal salts |
US20200299145A1 (en) * | 2019-03-22 | 2020-09-24 | Kunming University Of Science And Technology | Method for aluminum-enhanced dealkalization of red mud and separation and recovery of aluminum and iron |
CN113800792A (en) * | 2021-09-13 | 2021-12-17 | 河南理工大学 | Method for activating sintering-process red mud by in-situ wet carbonization at room temperature, activated red mud and application thereof |
-
2022
- 2022-10-12 CN CN202211246443.XA patent/CN115838233A/en active Pending
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101927255A (en) * | 2009-09-03 | 2010-12-29 | 昆明理工大学 | Method for carbon dioxide suspension dealkalization of red mud in alumina plant |
CN102500592A (en) * | 2011-09-16 | 2012-06-20 | 茌平县信发盛吉赤泥处理有限公司 | Method for comprehensively utilizing alumina red mud |
CN103073066A (en) * | 2012-11-01 | 2013-05-01 | 吕富华 | Innocent treatment and resource utilization method for red mud |
US20200299806A1 (en) * | 2016-03-25 | 2020-09-24 | Fakon Vállalkozási Kft. | Process for processing red mud and producing rare-earth metal salts |
US20200299145A1 (en) * | 2019-03-22 | 2020-09-24 | Kunming University Of Science And Technology | Method for aluminum-enhanced dealkalization of red mud and separation and recovery of aluminum and iron |
CN113800792A (en) * | 2021-09-13 | 2021-12-17 | 河南理工大学 | Method for activating sintering-process red mud by in-situ wet carbonization at room temperature, activated red mud and application thereof |
Non-Patent Citations (2)
Title |
---|
刘武军等: "《生物质废弃物污染控制与清洁转化》", 31 March 2022, 合肥:中国科学技术大学出版社, pages: 19 - 21 * |
陈益民等: "《高性能水泥基础研究 973项目研究进展》", 30 November 2004, 北京:中国纺织出版社, pages: 187 - 190 * |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Sutar et al. | Progress of red mud utilization: An overview | |
Rai et al. | Neutralization and utilization of red mud for its better waste management | |
Pappu et al. | Solid wastes generation in India and their recycling potential in building materials | |
Bernal et al. | Management and valorisation of wastes through use in producing alkali‐activated cement materials | |
CN104529196B (en) | Method for extracting ammonium and modifying electrolytic manganese residue | |
Trushko et al. | Topicality and possibilities for complete processing of red mud of aluminous production | |
CN109111208B (en) | A kind of iron tailings sintered brick and preparation method thereof | |
Prabhakar et al. | Incinerated sewage sludge bottom ash-chemical processing, leaching patterns and toxicity testing | |
CN105800973A (en) | Method for preparing cement from municipal solid waste incineration furnace slag | |
CN104445844A (en) | Method for dealkalizing red mud by uniting smoke and basic material | |
CN103060547B (en) | Method for restoring, roasting, purifying, and extracting manganese and iron by utilizing electrolytic manganese slag rotary kiln | |
Xiong et al. | Overview of hazardous waste treatment and stabilization/solidification technology | |
Gao et al. | A short review of the sustainable utilization of coal gangue in environmental applications | |
Nayak et al. | Red mud: Characteristics, utilization, and environmental remediation strategies in the aluminium industry | |
Fini et al. | Perspectives on innovative non-fertilizer applications of sewage sludge for mitigating environmental and health hazards | |
Xue et al. | Progress of solid waste red mud in the field of ecology and environment | |
Obenaus-Emler et al. | Geopolymers from mining tailings for more sustainable raw material supply | |
CN115838233A (en) | A method for comprehensive utilization of red mud | |
CN118515444A (en) | A low-carbon full-component synergistic process for the utilization of high-iron red mud and coal gangue industrial solid waste | |
CN109081353B (en) | Topezite prepared by activating incinerator bottom ash with humic acid and application thereof | |
Mikulionok | A state of art and prospects of red mud management | |
Alam et al. | Characterization and an overview of utilization and neutralization for efficient management of Bauxite residue for sustainable environment | |
Li et al. | The large-scale sustainable utilization status of bauxite residue (red mud): challenges and perspectives for China | |
CN108856248A (en) | Method for solidifying and cementing polycyclic aromatic hydrocarbon-containing industrial organic waste by using cocklebur flavum | |
CN115818999A (en) | Method for producing sandstone aggregate from red mud |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination |