CN105483363A - Method for co-production of activated calcium silicate by adopting copper tailings to produce iron ore concentrate - Google Patents
Method for co-production of activated calcium silicate by adopting copper tailings to produce iron ore concentrate Download PDFInfo
- Publication number
- CN105483363A CN105483363A CN201510915966.2A CN201510915966A CN105483363A CN 105483363 A CN105483363 A CN 105483363A CN 201510915966 A CN201510915966 A CN 201510915966A CN 105483363 A CN105483363 A CN 105483363A
- Authority
- CN
- China
- Prior art keywords
- calcium silicate
- copper tailings
- active calcium
- iron ore
- filtrate
- 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
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 title claims abstract description 115
- 229910052802 copper Inorganic materials 0.000 title claims abstract description 74
- 239000010949 copper Substances 0.000 title claims abstract description 74
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 title claims abstract description 73
- 229910052742 iron Inorganic materials 0.000 title claims abstract description 58
- OYACROKNLOSFPA-UHFFFAOYSA-N calcium;dioxido(oxo)silane Chemical class [Ca+2].[O-][Si]([O-])=O OYACROKNLOSFPA-UHFFFAOYSA-N 0.000 title claims abstract description 56
- 238000000034 method Methods 0.000 title claims abstract description 44
- 239000012141 concentrate Substances 0.000 title claims abstract description 34
- 238000004519 manufacturing process Methods 0.000 title description 15
- 239000000378 calcium silicate Substances 0.000 claims abstract description 55
- 229910052918 calcium silicate Inorganic materials 0.000 claims abstract description 55
- 239000000706 filtrate Substances 0.000 claims abstract description 28
- 229910052710 silicon Inorganic materials 0.000 claims abstract description 19
- 238000003723 Smelting Methods 0.000 claims abstract description 17
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 17
- 238000006243 chemical reaction Methods 0.000 claims abstract description 15
- 239000003513 alkali Substances 0.000 claims abstract description 12
- 238000011065 in-situ storage Methods 0.000 claims abstract description 7
- 238000002425 crystallisation Methods 0.000 claims abstract description 5
- 230000008025 crystallization Effects 0.000 claims abstract description 5
- 238000001914 filtration Methods 0.000 claims abstract description 3
- 238000001035 drying Methods 0.000 claims abstract 3
- 238000005406 washing Methods 0.000 claims abstract 3
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 30
- 230000008569 process Effects 0.000 claims description 22
- 239000007788 liquid Substances 0.000 claims description 16
- 239000010703 silicon Substances 0.000 claims description 13
- 239000003795 chemical substances by application Substances 0.000 claims description 9
- 239000011575 calcium Substances 0.000 claims description 8
- 230000035484 reaction time Effects 0.000 claims description 7
- 238000002386 leaching Methods 0.000 claims description 6
- 238000000605 extraction Methods 0.000 claims description 4
- 238000005188 flotation Methods 0.000 claims description 4
- 238000002844 melting Methods 0.000 claims description 4
- 230000008018 melting Effects 0.000 claims description 4
- 229910052760 oxygen Inorganic materials 0.000 claims description 4
- 239000002910 solid waste Substances 0.000 claims description 4
- 229910052708 sodium Inorganic materials 0.000 claims description 3
- 239000011734 sodium Substances 0.000 claims description 3
- 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 2
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims 4
- 235000011941 Tilia x europaea Nutrition 0.000 claims 4
- 239000004571 lime Substances 0.000 claims 4
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 claims 2
- 229910052791 calcium Inorganic materials 0.000 claims 2
- 239000000470 constituent Substances 0.000 claims 2
- 239000002253 acid Substances 0.000 claims 1
- 238000010790 dilution Methods 0.000 claims 1
- 239000012895 dilution Substances 0.000 claims 1
- 150000002148 esters Chemical class 0.000 claims 1
- 239000000047 product Substances 0.000 abstract description 16
- 238000000926 separation method Methods 0.000 abstract description 13
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 abstract description 9
- 239000000920 calcium hydroxide Substances 0.000 abstract description 9
- 235000011116 calcium hydroxide Nutrition 0.000 abstract description 9
- 229910001861 calcium hydroxide Inorganic materials 0.000 abstract description 9
- 238000004064 recycling Methods 0.000 abstract description 6
- 239000000463 material Substances 0.000 abstract description 5
- 238000002156 mixing Methods 0.000 abstract description 5
- 238000012986 modification Methods 0.000 abstract description 5
- 230000004048 modification Effects 0.000 abstract description 5
- 238000005265 energy consumption Methods 0.000 abstract description 4
- 239000003607 modifier Substances 0.000 abstract description 3
- 238000002360 preparation method Methods 0.000 abstract description 3
- 238000012545 processing Methods 0.000 abstract description 2
- 238000001704 evaporation Methods 0.000 abstract 1
- 230000008020 evaporation Effects 0.000 abstract 1
- XUIMIQQOPSSXEZ-UHFFFAOYSA-N Silicon Chemical compound [Si] XUIMIQQOPSSXEZ-UHFFFAOYSA-N 0.000 description 12
- 238000010521 absorption reaction Methods 0.000 description 10
- 230000000694 effects Effects 0.000 description 10
- 239000003921 oil Substances 0.000 description 10
- 239000000203 mixture Substances 0.000 description 9
- 239000002893 slag Substances 0.000 description 9
- 239000000292 calcium oxide Substances 0.000 description 7
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 7
- 238000011084 recovery Methods 0.000 description 7
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 6
- 239000004480 active ingredient Substances 0.000 description 5
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 4
- 239000004568 cement Substances 0.000 description 4
- 229910052840 fayalite Inorganic materials 0.000 description 4
- 238000002791 soaking Methods 0.000 description 4
- RYYKJJJTJZKILX-UHFFFAOYSA-M sodium octadecanoate Chemical compound [Na+].CCCCCCCCCCCCCCCCCC([O-])=O RYYKJJJTJZKILX-UHFFFAOYSA-M 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- 238000012360 testing method Methods 0.000 description 4
- OSMSIOKMMFKNIL-UHFFFAOYSA-N calcium;silicon Chemical compound [Ca]=[Si] OSMSIOKMMFKNIL-UHFFFAOYSA-N 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- 238000007654 immersion Methods 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 description 2
- 229910000519 Ferrosilicon Inorganic materials 0.000 description 2
- 229910004298 SiO 2 Inorganic materials 0.000 description 2
- 230000004913 activation Effects 0.000 description 2
- 229910052681 coesite Inorganic materials 0.000 description 2
- 239000004567 concrete Substances 0.000 description 2
- 229910052906 cristobalite Inorganic materials 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 239000006185 dispersion Substances 0.000 description 2
- 238000007885 magnetic separation Methods 0.000 description 2
- 230000007935 neutral effect Effects 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 230000009467 reduction Effects 0.000 description 2
- 239000000377 silicon dioxide Substances 0.000 description 2
- 235000012239 silicon dioxide Nutrition 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 229910052682 stishovite Inorganic materials 0.000 description 2
- 229910052905 tridymite Inorganic materials 0.000 description 2
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 229910003251 Na K Inorganic materials 0.000 description 1
- BPQQTUXANYXVAA-UHFFFAOYSA-N Orthosilicate Chemical compound [O-][Si]([O-])([O-])[O-] BPQQTUXANYXVAA-UHFFFAOYSA-N 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 239000002131 composite material Substances 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000010304 firing Methods 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- SZVJSHCCFOBDDC-UHFFFAOYSA-N iron(II,III) oxide Inorganic materials O=[Fe]O[Fe]O[Fe]=O SZVJSHCCFOBDDC-UHFFFAOYSA-N 0.000 description 1
- 229910052748 manganese Inorganic materials 0.000 description 1
- 238000005272 metallurgy Methods 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 230000003014 reinforcing effect Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 125000005372 silanol group Chemical group 0.000 description 1
- 125000004469 siloxy group Chemical group [SiH3]O* 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 229910052719 titanium Inorganic materials 0.000 description 1
- 239000011573 trace mineral Substances 0.000 description 1
- 235000013619 trace mineral Nutrition 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B1/00—Preliminary treatment of ores or scrap
- C22B1/005—Preliminary treatment of scrap
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B33/00—Silicon; Compounds thereof
- C01B33/20—Silicates
- C01B33/24—Alkaline-earth metal silicates
-
- 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
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Geochemistry & Mineralogy (AREA)
- Inorganic Chemistry (AREA)
- Manufacturing & Machinery (AREA)
- Materials Engineering (AREA)
- Mechanical Engineering (AREA)
- Metallurgy (AREA)
- Manufacture And Refinement Of Metals (AREA)
Abstract
本发明公开了一种铜尾渣生产铁精矿联产活性硅酸钙方法,包括以下步骤:(1)将铜尾渣与碱混合进行熔炼,熔炼完成后水浸、过滤,得到滤渣I和滤液I;所述滤渣I经洗涤、干燥得到富铁精矿;(2)在所述滤液I中加入熟石灰和表面改性剂进行原位改性,得到滤渣II和滤液II,所述滤渣II经洗涤干燥后得到活性硅酸钙,所述滤液II经蒸发结晶后返回步骤(1)中循环使用。本发明实现了铜尾渣中Fe、Si元素的定向分离、富集与相关高附加值产品的制备,解决了铜尾渣资源化利用率低,处理能耗高,反应辅料易造成二次污染等问题。
The invention discloses a method for co-producing active calcium silicate by producing iron concentrate from copper tailings, comprising the following steps: (1) mixing copper tailings with alkali for smelting, immersing in water and filtering after smelting to obtain filter residues I and Filtrate I; the filter residue I is washed and dried to obtain iron-rich concentrate; (2) adding slaked lime and a surface modifier to the filtrate I for in-situ modification to obtain filter residue II and filtrate II, and the filter residue II Active calcium silicate is obtained after washing and drying, and the filtrate II is returned to step (1) for recycling after evaporation and crystallization. The invention realizes the directional separation and enrichment of Fe and Si elements in copper tailings and the preparation of related high value-added products, and solves the problem of low resource utilization rate of copper tailings, high processing energy consumption, and secondary pollution easily caused by reaction auxiliary materials And other issues.
Description
技术领域technical field
本发明涉及冶金领域,尤其涉及一种铜冶炼尾渣生产铁精矿联产活性硅酸钙的方法。The invention relates to the field of metallurgy, in particular to a method for producing iron concentrate from copper smelting tailings and co-producing active calcium silicate.
背景技术Background technique
铜尾渣为冶炼产生的铜渣经破碎、筛分后,将粒度≤12mm的炉渣进行球磨之后进行两次浮选提取铜后的尾渣。通过之前阶段的处理后,铜尾渣的化学成分主要为铁橄榄石、SiO2和CaO,部分Fe3O4、Fe2O3、Al2O3和少量的MgO、K2O、Na2O等,此外还含有Mn、Zn、Cu、Ti等微量元素。渣中铁的品位一般在40%左右,远大于铁矿石的可开采品位(29.1%),渣中硅元素含量也高达20%,是理想的硅源。Copper tailing slag is the tailing slag after the copper slag produced by smelting is crushed and screened, and the slag with a particle size of ≤12 mm is ball milled and then subjected to two flotations to extract copper. After the previous stage of treatment, the chemical composition of copper tailings is mainly fayalite, SiO 2 and CaO, some Fe 3 O 4 , Fe 2 O 3 , Al 2 O 3 and a small amount of MgO, K 2 O, Na 2 O, etc., in addition, it also contains trace elements such as Mn, Zn, Cu, Ti, etc. The grade of iron in the slag is generally about 40%, which is much higher than the minable grade of iron ore (29.1%), and the silicon content in the slag is also as high as 20%, which is an ideal silicon source.
目前铜尾渣的处理方式除少部分用于水泥工业以外,大部分作堆弃处理。堆积的铜尾渣因其颗粒较小容易被风吹起造成空气污染,且在自然环境下铜尾渣浸出的有害重金属会污染水体、土壤,从而影响农业、渔业和林业的生产,并造成经济损失。在水泥混凝土工业中,铜尾渣主要集中于作为烧制水泥熟料的原料、作为矿化剂、作为水泥混凝土混合材等方面的制备。这些应用虽然实现了一定的经济价值,但对于铜尾渣的利用仅仅停留在其物理性能上,而渣中残留的铁、硅资源并没有得到充分的利用,资源化利用率极低。同时,对于铜尾渣的其他方面研究也比较有限。部分研究者对铜尾渣进行高温还原处理深度提铁,但过程中需要配入大量的焦粉和氧化钙,且还原温度高达1200~1300℃,能量与物料消耗巨大,同时铜尾渣中硅组分也未进行有效利用。也有部分学者将尾渣进行1300℃左右的高温焙烧,使用渣中铁组分转为磁铁矿相选择性富集,再经过磁选将部分铁进行回收。但该方法同样也面临着巨大的能耗与回收铁硅元素不充分等问题,其原因在于,铜尾渣中铁主要以铁橄榄石(2FeO·SiO2)、磁性氧化铁(Fe3O4)的物相存在于渣中,且弱磁性的铁橄榄石所占比例较大,因此磁选法分离硅铁无法实现。而铁橄榄石相因结构致密且熔点较高(1209℃),很难通过现行技术进行破坏,使其硅、铁相分离,资源化利用率极低。因此在我国现有资源紧缺及环境保护的严峻形势下,开发铜尾渣资源化综合利用技术,对促进循环经济和可持续发展具有重要的意义。At present, except for a small part of copper tailings being used in the cement industry, most of the copper tailings are disposed of in piles. The accumulated copper tailings are easily blown by the wind to cause air pollution because of their small particles, and in the natural environment, the harmful heavy metals leached from copper tailings will pollute water bodies and soil, thereby affecting the production of agriculture, fishery and forestry, and causing economic losses. loss. In the cement concrete industry, copper tailings are mainly used as raw materials for firing cement clinker, as mineralizers, and as cement and concrete mixtures. Although these applications have achieved a certain economic value, the utilization of copper tailings is only limited to its physical properties, while the iron and silicon resources remaining in the slag have not been fully utilized, and the utilization rate of resources is extremely low. At the same time, the research on other aspects of copper tailings is also relatively limited. Some researchers have carried out high-temperature reduction treatment on copper tailings to further improve iron, but a large amount of coke powder and calcium oxide need to be added in the process, and the reduction temperature is as high as 1200-1300 ° C, which consumes a lot of energy and materials. At the same time, silicon in copper tailings Components are also not efficiently utilized. Some scholars also roast the tailings at a high temperature of about 1300 °C, use the iron components in the slag to convert the magnetite phase into selective enrichment, and then recover part of the iron through magnetic separation. However, this method also faces problems such as huge energy consumption and insufficient recovery of iron and silicon elements. The reason is that iron in copper tailings mainly consists of fayalite (2FeO·SiO 2 ), magnetic iron oxide (Fe 3 O 4 ) The phase exists in the slag, and the proportion of weakly magnetic fayalite is relatively large, so the separation of ferrosilicon by magnetic separation cannot be realized. The fayalite phase has a dense structure and a high melting point (1209°C), so it is difficult to destroy it by the current technology, so that the silicon and iron phases are separated, and the utilization rate of resources is extremely low. Therefore, under the severe situation of resource shortage and environmental protection in our country, the development of comprehensive utilization technology of copper tailings is of great significance to promote circular economy and sustainable development.
发明内容Contents of the invention
本发明要解决的技术问题是克服现有技术的不足,提供一种铜尾渣生产铁精矿联产活性硅酸钙的方法。The technical problem to be solved by the present invention is to overcome the deficiencies of the prior art and provide a method for producing iron concentrate from copper tailings and co-producing active calcium silicate.
为解决上述技术问题,本发明提出的技术方案为:In order to solve the problems of the technologies described above, the technical solution proposed by the present invention is:
一种铜尾渣生产铁精矿联产活性硅酸钙方法,包括以下步骤:A method for coproducing active calcium silicate by producing iron concentrate from copper tailings, comprising the following steps:
(1)将铜尾渣与碱混合进行熔炼,熔炼完成后水浸、过滤,得到滤渣I和滤液I;所述滤渣I经洗涤、干燥得到富铁精矿;(1) mixing copper tailings with alkali for smelting, immersing in water and filtering after smelting to obtain filter residue I and filtrate I; said filter residue I is washed and dried to obtain iron-rich concentrate;
(2)在所述滤液I中加入熟石灰和表面改性剂进行原位改性,得到滤渣II和滤液II,所述滤渣II经洗涤干燥后得到活性硅酸钙,所述滤液II经蒸发结晶后返回步骤(1)中循环使用。所述活性硅酸钙又称高分散硅酸钙,表面存在硅氧基和硅醇基官能团,有很强的补强性能,对橡胶有良好的亲合性和高度的分散性,从而可提高制品的力学强度,显著地提高复合物性能和使用价值。活化指数表征硅酸钙的表面润属性,水合硅酸钙具有矫情的亲水性,活性硅酸钙表现为亲油性,活化指数越大,亲油性越好。活性硅酸钙的表面上形成了一层单分子膜,分体分散度提高,使得克力荐空隙减少,吸油值下降。吸油值越低,分散性越好。(2) Adding slaked lime and a surface modifier to the filtrate I for in-situ modification to obtain filter residue II and filtrate II, the filter residue II is washed and dried to obtain active calcium silicate, and the filtrate II is evaporated and crystallized Back to step (1) for recycling. The active calcium silicate, also known as highly dispersed calcium silicate, has siloxyl and silanol functional groups on the surface, has strong reinforcing properties, and has good affinity and high dispersibility to rubber, thereby improving The mechanical strength of the product can significantly improve the performance and use value of the composite. The activation index represents the surface wettability of calcium silicate. Hydrated calcium silicate has a hypocritical hydrophilicity, while active calcium silicate is lipophilic. The larger the activation index, the better the lipophilicity. A layer of monomolecular film is formed on the surface of the active calcium silicate, and the dispersion degree of the split body is improved, so that the voids of the creosinate are reduced, and the oil absorption value is reduced. The lower the oil absorption value, the better the dispersion.
上述的铜尾渣生产铁精矿联产活性硅酸钙方法,优选的,所述步骤(2)中,表面改性剂的加入量为滤液I中Si元素质量的1%~10%。In the above-mentioned method for producing iron concentrate from copper tailings and co-producing active calcium silicate, preferably, in the step (2), the amount of the surface modifier added is 1% to 10% of the Si element mass in the filtrate I.
上述的铜尾渣生产铁精矿联产活性硅酸钙方法,优选的,所述步骤(1)中,熔炼的时间为1.5~3.5小时,熔炼温度为500~700℃,铜尾渣与碱的质量比为1:1.0~3.0。The above method for producing iron concentrate from copper tailings and co-producing active calcium silicate, preferably, in the step (1), the smelting time is 1.5 to 3.5 hours, the smelting temperature is 500 to 700°C, and the copper tailings and alkali The mass ratio is 1:1.0~3.0.
上述的铜尾渣生产铁精矿联产活性硅酸钙方法,优选的,所述步骤(1)中,浸出温度为20~80℃,浸出时间为10~70min,浸出时固液质量比为1:10~25。The above-mentioned method for producing iron concentrate from copper tailings and co-producing active calcium silicate, preferably, in the step (1), the leaching temperature is 20-80°C, the leaching time is 10-70min, and the solid-liquid mass ratio during leaching is 1:10-25.
上述的铜尾渣生产铁精矿联产活性硅酸钙方法,优选的,所述步骤(2)中,熟石灰的加入量以钙元素计,滤渣I中的硅元素与熟石灰中钙元素摩尔比为1:1.0~2.0。Above-mentioned copper tailings production iron concentrate co-production active calcium silicate method, preferably, in described step (2), the add-on of slaked lime is calculated by calcium element, the silicon element in the filter residue 1 and calcium element mol ratio in the slaked lime It is 1:1.0~2.0.
上述的铜尾渣生产铁精矿联产活性硅酸钙方法,优选的,所述步骤(2)中,原位改性过程中控制反应温度为70~90℃,反应时间为60~120min。In the above-mentioned method for producing iron concentrate from copper tailings and co-producing active calcium silicate, preferably, in the step (2), during the in-situ modification process, the reaction temperature is controlled to be 70-90° C., and the reaction time is 60-120 minutes.
上述的铜尾渣生产铁精矿联产活性硅酸钙方法,优选的,所述铜尾渣为铜冶炼过程中经浮选贫化提铜后的固体废弃物,铜尾渣中主要元素为Fe、Si、O。In the above-mentioned method for producing iron concentrate with co-production of active calcium silicate from copper tailings, preferably, the copper tailings are solid wastes obtained by flotation depletion and extraction of copper during the copper smelting process, and the main elements in the copper tailings are Fe, Si, O.
上述的铜尾渣生产铁精矿联产活性硅酸钙方法,优选的,所述步骤(1)中,碱为氢氧化钠。In the above-mentioned method for producing iron concentrate from copper tailings and co-producing active calcium silicate, preferably, in the step (1), the alkali is sodium hydroxide.
上述的铜尾渣生产铁精矿联产活性硅酸钙方法,优选的,所述步骤(2)中,改性剂为硬酸酯钠,熟石灰中Ca(OH)2的质量分数不低于85%。Above-mentioned copper tailings production iron concentrate co-production active calcium silicate method, preferably, in described step (2), modifying agent is sodium hardate, and Ca (OH) in the slaked lime The mass fraction is not less than 85%.
本发明提出了以铜尾渣为原料采用低温碱性熔炼、水浸、原位改性制备铁精矿,并生产活性硅酸钙的方法处理铜尾渣。在熔炼阶段,由于碱性介质的加入可以有效破坏FeO与SiO2之间的化学键,并与SiO2结合生成硅酸盐,增加了FeO的活度从而降低反应体系温度;熔炼产物仅需要通过水浸即可分离其中的硅铁元素,避免了其他浸出剂的引入所带来的二次污染问题;浸出液(滤液)通过原位改性苛化反应制备活性硅酸钙,使活性硅酸钙的制备过程与改性过程同时进行,缩短了反应时间,同时降低了成本;制备活性硅酸钙的滤液可进行碱回用。The invention proposes the method of using copper tailings as raw material to prepare iron concentrate by low-temperature alkaline smelting, water immersion and in-situ modification, and producing active calcium silicate to process copper tailings. In the smelting stage, since the addition of alkaline medium can effectively break the chemical bond between FeO and SiO2 , and combine with SiO2 to form silicate, which increases the activity of FeO and reduces the temperature of the reaction system; the smelted product only needs to pass through water The ferrosilicon element in it can be separated by leaching, avoiding the secondary pollution caused by the introduction of other leaching agents; the leachate (filtrate) is prepared by in-situ modified causticization reaction to prepare active calcium silicate, so that the active calcium silicate The preparation process and the modification process are carried out simultaneously, which shortens the reaction time and reduces the cost; the filtrate for preparing the active calcium silicate can be reused by alkali.
与现有技术相比,本发明的优点在于:Compared with the prior art, the present invention has the advantages of:
(1)本发明的工艺实现了铜尾渣中Fe、Si元素的定向分离、富集与相关高附加值产品的制备,解决了铜尾渣资源化利用率低,处理能耗高,反应辅料易造成二次污染等问题。(1) The process of the present invention realizes the directional separation and enrichment of Fe and Si elements in copper tailings, the enrichment and the preparation of related high value-added products, and solves the problem of low resource utilization rate of copper tailings, high energy consumption for processing, and the need for reaction auxiliary materials It is easy to cause secondary pollution and other problems.
(2)本发明具有资源综合利用率高、反应能耗低、工艺流程短、辅料可循环使用、产品附加值高等特点:其中硅回收率≥85.5%,铁回收率高于97.7%。本发明所制备的富铁精矿铁品位最高达到62.29%,满足GB/T2593-2010二级标准,产品活性硅酸钙中有效成分CaO的含量均高达50%,符合市场标准。(2) The present invention has the characteristics of high resource comprehensive utilization rate, low reaction energy consumption, short process flow, recyclable auxiliary materials, and high product added value: wherein the recovery rate of silicon is ≥ 85.5%, and the recovery rate of iron is higher than 97.7%. The highest iron grade of the iron-rich concentrate prepared by the invention reaches 62.29%, which meets the secondary standard of GB/T2593-2010, and the content of active ingredient CaO in the product active calcium silicate is as high as 50%, which meets the market standard.
(3)本发明的工艺过程无固体废弃物产生,工艺全过程中反应辅料均可实现循环利用,经济效果显著。本发明工艺过程产生的水可以循环使用,无废水排放。(3) The technical process of the present invention does not generate solid waste, and the auxiliary materials in the process can be recycled, and the economic effect is remarkable. The water produced in the technical process of the invention can be recycled without waste water discharge.
附图说明Description of drawings
图1为本发明的铜尾渣生产铁精矿联产活性硅酸钙的工艺流程图。Fig. 1 is a process flow chart of the present invention for producing iron concentrate from copper tailings and co-producing active calcium silicate.
具体实施方式detailed description
为了便于理解本发明,下文将结合较佳的实施例对本发明作更全面、细致地描述,但本发明的保护范围并不限于以下具体的实施例。In order to facilitate the understanding of the present invention, the following will describe the present invention more fully and in detail in combination with preferred embodiments, but the protection scope of the present invention is not limited to the following specific embodiments.
除非另有定义,下文中所使用的所有专业术语与本领域技术人员通常理解的含义相同。本文中所使用的专业术语只是为了描述具体实施例的目的,并不是旨在限制本发明的保护范围。Unless otherwise defined, all technical terms used hereinafter have the same meanings as commonly understood by those skilled in the art. The terminology used herein is only for the purpose of describing specific embodiments, and is not intended to limit the protection scope of the present invention.
除有特别说明,本发明中用到的各种试剂、原料均为可以从市场上购买的商品或者可以通过公知的方法制得的产品。Unless otherwise specified, the various reagents and raw materials used in the present invention are commercially available products or products that can be prepared by known methods.
以下实施例所采用的原料铜尾渣为铜冶炼过程中经浮选贫化提铜后的固体废弃物,主要元素为Fe、Si、O,其化学组成见表1所示。The raw copper tailings used in the following examples are solid wastes obtained by flotation depletion and copper extraction in the copper smelting process. The main elements are Fe, Si, and O. The chemical composition is shown in Table 1.
表1铜尾渣化学组成(%)Table 1 Copper tailings chemical composition (%)
实施例1:Example 1:
一种本发明的铜尾渣生产铁精矿联产活性硅酸钙方法,其工艺流程如图1所示,包括以下步骤:A kind of copper tailings of the present invention produces iron concentrate and co-produces active calcium silicate method, and its technological process as shown in Figure 1, comprises the following steps:
(1)将铜尾渣磨碎至200目以下,称取100g铜尾渣与150gNaOH(渣碱质量比1:1.5)混合均匀,置于马弗炉中加热至500℃,恒温1.5小时进行熔炼。熔炼产物空冷后经磨碎后水浸20min,水浸温度40℃,固液质量比为1:15,水浸完成后固液分离,所得滤渣洗涤至中性后进行烘干得到富铁精矿产品,铁品位达到52.11%。(1) Grind copper tailings to below 200 mesh, weigh 100g copper tailings and 150g NaOH (slag-alkali mass ratio 1:1.5) and mix evenly, place in a muffle furnace and heat to 500°C, keep the temperature for 1.5 hours for smelting . The smelted product is air-cooled, ground, and then soaked in water for 20 minutes. The water soaking temperature is 40°C, and the solid-liquid mass ratio is 1:15. After the water soaking is completed, the solid-liquid separation is carried out. The obtained filter residue is washed to neutral and then dried to obtain iron-rich concentrate Products, the iron grade reaches 52.11%.
(2)在步骤固液分离得到的滤液中加入滤液中Si元素质量5%的硬酸酯钠混合均匀后,按照硅钙摩尔比1:1.0加入熟石灰(Ca(OH)2的质量分数为90%)均匀后,控制反应温度为75℃,反应时间为90min,反应结束后,固液分离得到的滤渣至中性后再进行分散洗涤,烘干得成品活性硅酸钙;滤液蒸发结晶后制得NaOH返回步骤(1)中循环利用。全过程中铁、硅回收率分别达到97.1%与90.25%,活性硅酸钙中有效成分CaO的含量达到51.6%。(2) Add sodium stearate of 5% Si element quality in the filtrate to the filtrate obtained in the step of solid-liquid separation and mix evenly, then add slaked lime (Ca(OH) 2 with a mass fraction of 90 %) after being uniform, control the reaction temperature to be 75°C, and the reaction time is 90min. After the reaction is over, the filter residue obtained from solid-liquid separation is neutralized and then dispersed and washed, and dried to obtain the finished active calcium silicate; the filtrate is evaporated and crystallized to produce Get NaOH and return to step (1) for recycling. During the whole process, the recovery rates of iron and silicon reach 97.1% and 90.25% respectively, and the content of active ingredient CaO in the active calcium silicate reaches 51.6%.
测试本实施得到的活性硅酸钙的活性指数为85%,吸油值为75ml/(100g);而未加入改性剂时,硅酸钙的活性指数为0%,吸油值为85ml/(100g)。Test the activity index of the active calcium silicate that this implementation obtains is 85%, and oil absorption value is 75ml/(100g); And when not adding modifying agent, the activity index of calcium silicate is 0%, and oil absorption value is 85ml/(100g) ).
实施例2:Example 2:
一种本发明的铜尾渣生产铁精矿联产活性硅酸钙方法,其工艺流程如图1所示,包括以下步骤:A kind of copper tailings of the present invention produces iron concentrate and co-produces active calcium silicate method, and its technological process as shown in Figure 1, comprises the following steps:
(1)将铜尾渣磨碎至200目以下,称取200g铜尾渣与400gNaOH(渣碱质量比1:2)混合均匀,置于马弗炉中加热至550℃,恒温2小时进行熔炼。熔炼产物空冷后经磨碎后水浸40min,水浸温度50℃,固液质量比为1:10水浸完成后固液分离,所得滤渣洗涤至中性后进行烘干得到富铁精矿产品,铁品位达到56.11%。(1) Grind the copper tailings to below 200 mesh, weigh 200g copper tailings and 400g NaOH (slag-alkali mass ratio 1:2) and mix evenly, place in a muffle furnace and heat to 550°C, keep the temperature for 2 hours for smelting . After the smelted product is air-cooled, it is ground and soaked in water for 40 minutes. The water immersion temperature is 50°C and the mass ratio of solid to liquid is 1:10. , the iron grade reaches 56.11%.
(2)在步骤(1)固液分离得到的滤液中加入滤液中Si元素质量8%的硬酸酯钠混合均匀后,按照硅钙摩尔比1:1.5加入熟石灰(Ca(OH)2的质量分数为85%)均匀后,控制反应温度为80℃,反应时间为70min,反应结束后,固液分离得到的滤渣至中性后再进行分散洗涤,烘干得成品活性硅酸钙,滤液蒸发结晶后制得NaOH返回步骤(1)中循环利用。全过程中铁、硅回收率分别达到98.1%与87.69%,活性硅酸钙中有效成分CaO的含量达到53.1%。(2) in the filtrate that step (1) solid-liquid separation obtains, add the sodium stearate of Si element mass 8% in the filtrate after mixing uniformly, add slaked lime (Ca(OH) according to the silicon-calcium molar ratio 1 :1.5 The quality of After the fraction is 85%), the reaction temperature is controlled to be 80°C, and the reaction time is 70min. After the reaction is over, the filter residue obtained by solid-liquid separation is neutralized and then dispersed and washed, dried to obtain the finished active calcium silicate, and the filtrate is evaporated The NaOH obtained after crystallization is returned to step (1) for recycling. In the whole process, the recovery rates of iron and silicon reach 98.1% and 87.69% respectively, and the content of active ingredient CaO in the active calcium silicate reaches 53.1%.
测试本实施例得到的活性硅酸钙的活性指数为87%,吸油值为74ml/(100g);未加入改性剂时,硅酸钙的活性指数为0%,吸油值为83ml/(100g)。The activity index of the active calcium silicate obtained by testing the present embodiment is 87%, and the oil absorption value is 74ml/(100g); When no modifying agent is added, the activity index of calcium silicate is 0%, and the oil absorption value is 83ml/(100g) ).
实施例3:Example 3:
一种本发明的铜尾渣生产铁精矿联产活性硅酸钙方法,其工艺流程如图1所示,包括以下步骤:A kind of copper tailings of the present invention produces iron concentrate and co-produces active calcium silicate method, and its technological process as shown in Figure 1, comprises the following steps:
(1)将铜尾渣磨碎至200目以下,称取100g铜尾渣与250gNaOH(渣碱质量比1:2.5)混合均匀,置于马弗炉中加热至600℃,恒温2.5小时进行熔炼。熔炼产物空冷后经磨碎后水浸50min,水浸温度60℃,固液质量比为1:25,水浸完成后固液分离,所得滤渣洗涤至中性后进行烘干得到富铁精矿产品,铁品位达到59.26%。(1) Grind the copper tailings to below 200 mesh, weigh 100g copper tailings and 250g NaOH (slag-alkali mass ratio 1:2.5) and mix evenly, place in a muffle furnace and heat to 600°C, keep the temperature for 2.5 hours for smelting . The smelted product is air-cooled, ground, and then soaked in water for 50 minutes. The water soaking temperature is 60°C, and the solid-liquid mass ratio is 1:25. After the water soaking is completed, the solid-liquid separation is carried out. The resulting filter residue is washed to neutral and then dried to obtain iron-rich concentrate. Products, the iron grade reaches 59.26%.
(2)在步骤(1)固液分离得到的滤液中加入滤液中Si元素质量10%的硬酸酯钠混合均匀后,按照硅钙摩尔比1:2.0加入熟石灰(Ca(OH)2的质量分数为88%)均匀后,控制反应温度为90℃,反应时间为100min,反应结束后,固液分离得到的滤渣至中性后再进行分散洗涤,烘干得成品活性硅酸钙;滤液蒸发结晶后制得NaOH返回步骤(1)中循环利用。全过程中铁、硅回收率分别达到98.2%与91.5%,活性硅酸钙中有效成分CaO的含量达到56.4%。(2) In the filtrate that step (1) solid-liquid separation obtains, add the sodium stearate of Si element quality 10% in the filtrate after mixing uniformly, add slaked lime (Ca(OH) according to the silicon-calcium molar ratio 1: 2.0 The quality of After the fraction is 88%), the reaction temperature is controlled to be 90°C and the reaction time is 100min. After the reaction is over, the filter residue obtained by solid-liquid separation is neutralized and then dispersed and washed, and dried to obtain the finished active calcium silicate; the filtrate is evaporated The NaOH obtained after crystallization is returned to step (1) for recycling. In the whole process, the recovery rates of iron and silicon reach 98.2% and 91.5% respectively, and the content of active ingredient CaO in the active calcium silicate reaches 56.4%.
测试本实施例得到的活性硅酸钙的活性指数为83%,吸油值为78ml/(100g);而未加入改性剂时,获得的硅酸钙的活性指数为0%,吸油值为86ml/(100g)。The activity index of the active calcium silicate obtained by testing the present embodiment is 83%, and the oil absorption value is 78ml/(100g); When no modifying agent is added, the activity index of the calcium silicate obtained is 0%, and the oil absorption value is 86ml / (100g).
实施例4:Example 4:
一种本发明的铜尾渣生产铁精矿联产活性硅酸钙方法,其工艺流程如图1所示,包括以下步骤:A kind of copper tailings of the present invention produces iron concentrate and co-produces active calcium silicate method, its technological process as shown in Figure 1, comprises the following steps:
(1)将铜尾渣磨碎至200目以下,称取100g铜尾渣与300gNaOH(渣碱质量比1:3.0)混合均匀,置于马弗炉中加热至600℃,恒温3小时进行熔炼。熔炼产物空冷后经磨碎后水浸80min,水浸温度70℃,固液质量比为1:20,水浸完成后固液分离,所得滤渣洗涤至中性后进行烘干得到富铁精矿产品,铁品位达到62.29%。(1) Grind the copper tailings to below 200 mesh, weigh 100g copper tailings and 300g NaOH (slag-alkali mass ratio 1:3.0) and mix evenly, place in a muffle furnace and heat to 600°C, keep the temperature for 3 hours for smelting . The smelted product is air-cooled, ground and then immersed in water for 80 minutes. The temperature of water immersion is 70°C, and the mass ratio of solid to liquid is 1:20. Products, the iron grade reaches 62.29%.
(2)在步骤(1)固液分离得到的滤液中加入滤液中Si元素质量6%的硬酸酯钠混合均匀后,按照硅钙摩尔比1:2.0加入熟石灰(Ca(OH)2的质量分数为92%)均匀后,控制反应温度为90℃,反应时间为80min,反应结束后,固液分离得到的滤渣至中性后再进行分散洗涤,烘干得成品活性硅酸钙,滤液蒸发结晶后制得NaOH返回步骤(1)中循环利用。全过程中铁、硅回收率分别达到99.3%与86.5%,活性硅酸钙中有效成分CaO的含量达到53.4%。(2) in the filtrate that step (1) solid-liquid separation obtains, add the sodium stearate of Si element quality 6% in the filtrate after mixing uniformly, add slaked lime (Ca(OH) according to the silicon-calcium molar ratio 1: 2.0 The quality of After the fraction is 92%), the reaction temperature is controlled to be 90°C and the reaction time is 80min. After the reaction is over, the filter residue obtained by solid-liquid separation is neutralized and then dispersed and washed, dried to obtain the finished active calcium silicate, and the filtrate is evaporated The NaOH obtained after crystallization is returned to step (1) for recycling. In the whole process, the recovery rates of iron and silicon reach 99.3% and 86.5% respectively, and the content of active ingredient CaO in the active calcium silicate reaches 53.4%.
测试本实施例得到的活性硅酸钙的活性指数为84%,吸油值为74ml/(100g);而未加入改性剂时,产物活性指数为0%,吸油值为88ml/(100g)。The activity index of the active calcium silicate that the test present embodiment obtains is 84%, and oil absorption value is 74ml/(100g); When not adding modifying agent, product activity index is 0%, and oil absorption value is 88ml/(100g).
Claims (9)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510915966.2A CN105483363A (en) | 2015-12-10 | 2015-12-10 | Method for co-production of activated calcium silicate by adopting copper tailings to produce iron ore concentrate |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510915966.2A CN105483363A (en) | 2015-12-10 | 2015-12-10 | Method for co-production of activated calcium silicate by adopting copper tailings to produce iron ore concentrate |
Publications (1)
Publication Number | Publication Date |
---|---|
CN105483363A true CN105483363A (en) | 2016-04-13 |
Family
ID=55670634
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201510915966.2A Pending CN105483363A (en) | 2015-12-10 | 2015-12-10 | Method for co-production of activated calcium silicate by adopting copper tailings to produce iron ore concentrate |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN105483363A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN116022792A (en) * | 2023-02-08 | 2023-04-28 | 湖南愿景新材料科技有限公司 | A method for co-producing calcium silicate hydrate by alkali dissolution and purification of silica sand |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101525143A (en) * | 2009-01-09 | 2009-09-09 | 东北大学 | Method for preparing magnesia, silicon dioxide and nickel oxide products from lateritic nickel ore |
CN101886179A (en) * | 2010-07-12 | 2010-11-17 | 昆明理工大学 | Method for separating iron, copper and silicon components from copper smelting slag |
CN101941725A (en) * | 2009-07-10 | 2011-01-12 | 同方环境股份有限公司 | Method for extracting aluminum oxide from coal gangue and co-producing active calcium silicate |
CN102336426A (en) * | 2010-07-16 | 2012-02-01 | 中国科学院合肥物质科学研究院 | Preparation method of hydrophobic nanoscale calcium carbonate |
CN104229892A (en) * | 2014-09-15 | 2014-12-24 | 中国科学院过程工程研究所 | Method for efficiently extracting, separating and recovering chromium and silicon from vanadium extraction tailings |
-
2015
- 2015-12-10 CN CN201510915966.2A patent/CN105483363A/en active Pending
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101525143A (en) * | 2009-01-09 | 2009-09-09 | 东北大学 | Method for preparing magnesia, silicon dioxide and nickel oxide products from lateritic nickel ore |
CN101941725A (en) * | 2009-07-10 | 2011-01-12 | 同方环境股份有限公司 | Method for extracting aluminum oxide from coal gangue and co-producing active calcium silicate |
CN101886179A (en) * | 2010-07-12 | 2010-11-17 | 昆明理工大学 | Method for separating iron, copper and silicon components from copper smelting slag |
CN102336426A (en) * | 2010-07-16 | 2012-02-01 | 中国科学院合肥物质科学研究院 | Preparation method of hydrophobic nanoscale calcium carbonate |
CN104229892A (en) * | 2014-09-15 | 2014-12-24 | 中国科学院过程工程研究所 | Method for efficiently extracting, separating and recovering chromium and silicon from vanadium extraction tailings |
Non-Patent Citations (1)
Title |
---|
胡继林 等: ""表面改性超细硅酸钙的制备及其性能表征"", 《无机盐工业》 * |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN116022792A (en) * | 2023-02-08 | 2023-04-28 | 湖南愿景新材料科技有限公司 | A method for co-producing calcium silicate hydrate by alkali dissolution and purification of silica sand |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN103614547B (en) | A method for separating iron, aluminum and silicon from diaspore type bauxite | |
CN110284004B (en) | Method for synergistically recycling copper slag and sodium sulfate waste slag | |
JP5944522B2 (en) | Method of separating and recovering iron from waste nonferrous slag discharged from nonferrous metal smelting process | |
CN102924113A (en) | Copper mine tailing slag porous ceramic material and preparation method thereof | |
CN105039728A (en) | Method for treating copper slag | |
CN101775507B (en) | Extraction method for extracting vanadium pentoxide from low grade oxidized type navajoite | |
CN106824543A (en) | A kind of method that copper smelting slag reclaims copper | |
CN102851489B (en) | Method for comprehensively recovering valuable metals in limonite type laterite-nickel ore | |
CN103611624A (en) | Floatation and acid pickling combined process for processing low-grade mixed copper ore | |
CN110106347B (en) | A kind of treatment method of copper smelting waste residue applied to sintering | |
CN106315517A (en) | Method for recycling sulphur from sulphur-containing residue | |
CN111411217A (en) | Method for preparing ferronickel product by reducing high-magnesium type laterite-nickel ore | |
CN107971123A (en) | A kind of flotation and metallurgy method of irony coated mixed copper ore | |
CN108456153B (en) | Phenylpropenyl hydroxamic acid and its preparation method and its application in the flotation of tungsten ore | |
CN101481754A (en) | Method for separating molybdenum and nickel in molybdenum- and nickel-containing black shale | |
Liu et al. | New progress in the development and utilization of ferromanganese ore | |
CN107473710A (en) | A kind of electroplating sludge that blends prepares the method that clay brick process improves heavy metals immobilization effect | |
CN105483363A (en) | Method for co-production of activated calcium silicate by adopting copper tailings to produce iron ore concentrate | |
CN105506297A (en) | Resource utilization method for copper smelting slag | |
CN105316479A (en) | Red mud vanadium extracting and ore-blending sintering method | |
CN102936650A (en) | Method for comprehensively utilizing red mud and high-phosphorus iron ore | |
CN103966436B (en) | Utilize the method that alkali soaks, v-ti magnetite concentrate is selected in desliming again | |
CN108796236B (en) | Method for comprehensively recycling valuable components in copper slag | |
CN102268539A (en) | Method for removing phosphorus from high-phosphorus iron ore through two-step acid leaching | |
CN110330360A (en) | A kind of novel light aggregate foaming agent and preparation method thereof |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20160413 |