CN102134649B - Comprehensive utilization method for vanadium slag - Google Patents
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- LEONUFNNVUYDNQ-UHFFFAOYSA-N vanadium atom Chemical compound [V] LEONUFNNVUYDNQ-UHFFFAOYSA-N 0.000 title claims abstract description 170
- 229910052720 vanadium Inorganic materials 0.000 title claims abstract description 168
- 239000002893 slag Substances 0.000 title claims abstract description 64
- 238000000034 method Methods 0.000 title claims abstract description 33
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims abstract description 145
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 claims abstract description 88
- 229910052742 iron Inorganic materials 0.000 claims abstract description 72
- GNTDGMZSJNCJKK-UHFFFAOYSA-N divanadium pentaoxide Chemical compound O=[V](=O)O[V](=O)=O GNTDGMZSJNCJKK-UHFFFAOYSA-N 0.000 claims abstract description 66
- 238000001556 precipitation Methods 0.000 claims abstract description 23
- 238000002844 melting Methods 0.000 claims abstract description 13
- 230000008018 melting Effects 0.000 claims abstract description 13
- 238000002156 mixing Methods 0.000 claims abstract description 12
- 238000001914 filtration Methods 0.000 claims abstract description 10
- 238000000227 grinding Methods 0.000 claims abstract description 10
- 238000002360 preparation method Methods 0.000 claims abstract description 9
- 239000000706 filtrate Substances 0.000 claims description 48
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 27
- NCEFRBSXBILZPP-UHFFFAOYSA-M azanium;potassium;sulfate Chemical compound [NH4+].[K+].[O-]S([O-])(=O)=O NCEFRBSXBILZPP-UHFFFAOYSA-M 0.000 claims description 26
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 claims description 25
- 229910052921 ammonium sulfate Inorganic materials 0.000 claims description 25
- 235000011130 ammonium sulphate Nutrition 0.000 claims description 25
- 239000000843 powder Substances 0.000 claims description 25
- 239000007787 solid Substances 0.000 claims description 22
- KCXVZYZYPLLWCC-UHFFFAOYSA-N EDTA Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O KCXVZYZYPLLWCC-UHFFFAOYSA-N 0.000 claims description 21
- 239000000203 mixture Substances 0.000 claims description 17
- 239000012452 mother liquor Substances 0.000 claims description 17
- 239000000126 substance Substances 0.000 claims description 11
- 239000007864 aqueous solution Substances 0.000 claims description 10
- 239000000463 material Substances 0.000 claims description 10
- 239000004568 cement Substances 0.000 claims description 9
- 239000013078 crystal Substances 0.000 claims description 9
- 238000006243 chemical reaction Methods 0.000 claims description 8
- 229910021529 ammonia Inorganic materials 0.000 claims 3
- 238000001354 calcination Methods 0.000 claims 3
- NDLPOXTZKUMGOV-UHFFFAOYSA-N oxo(oxoferriooxy)iron hydrate Chemical compound O.O=[Fe]O[Fe]=O NDLPOXTZKUMGOV-UHFFFAOYSA-N 0.000 claims 3
- 230000015572 biosynthetic process Effects 0.000 claims 1
- 238000001816 cooling Methods 0.000 claims 1
- 238000013467 fragmentation Methods 0.000 claims 1
- 238000006062 fragmentation reaction Methods 0.000 claims 1
- 239000002105 nanoparticle Substances 0.000 claims 1
- 230000001105 regulatory effect Effects 0.000 claims 1
- 238000010792 warming Methods 0.000 claims 1
- 239000000047 product Substances 0.000 abstract description 14
- 239000002994 raw material Substances 0.000 abstract description 12
- 230000008901 benefit Effects 0.000 abstract description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 3
- 239000013067 intermediate product Substances 0.000 abstract description 2
- 238000004064 recycling Methods 0.000 abstract description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N sulfuric acid Substances OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 9
- 238000000605 extraction Methods 0.000 description 7
- 238000000926 separation method Methods 0.000 description 6
- 239000011734 sodium Substances 0.000 description 5
- 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 description 4
- 150000003863 ammonium salts Chemical class 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 239000002244 precipitate Substances 0.000 description 4
- 229910052708 sodium Inorganic materials 0.000 description 4
- 239000002699 waste material Substances 0.000 description 4
- UNTBPXHCXVWYOI-UHFFFAOYSA-O azanium;oxido(dioxo)vanadium Chemical compound [NH4+].[O-][V](=O)=O UNTBPXHCXVWYOI-UHFFFAOYSA-O 0.000 description 3
- 238000002425 crystallisation Methods 0.000 description 3
- 230000008025 crystallization Effects 0.000 description 3
- 239000012535 impurity Substances 0.000 description 3
- 238000002386 leaching Methods 0.000 description 3
- 239000000243 solution Substances 0.000 description 3
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 2
- 239000000654 additive Substances 0.000 description 2
- 239000003513 alkali Substances 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 238000004090 dissolution Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 235000010755 mineral Nutrition 0.000 description 2
- 159000000000 sodium salts Chemical class 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- QXNVGIXVLWOKEQ-UHFFFAOYSA-N Disodium Chemical class [Na][Na] QXNVGIXVLWOKEQ-UHFFFAOYSA-N 0.000 description 1
- 238000003723 Smelting Methods 0.000 description 1
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 1
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- GJPIVNTZJFSDCX-UHFFFAOYSA-N [V].[Ca] Chemical compound [V].[Ca] GJPIVNTZJFSDCX-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 230000000996 additive effect Effects 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 230000002308 calcification Effects 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 239000013522 chelant Substances 0.000 description 1
- 230000009920 chelation Effects 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010949 copper Substances 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- -1 ferrous metals Chemical class 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 238000009776 industrial production Methods 0.000 description 1
- 239000011133 lead Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 238000005272 metallurgy Methods 0.000 description 1
- 231100000572 poisoning Toxicity 0.000 description 1
- 230000000607 poisoning effect Effects 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 235000002639 sodium chloride Nutrition 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 239000002341 toxic gas Substances 0.000 description 1
- 229910001935 vanadium oxide Inorganic materials 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
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- 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
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Abstract
本发明提供一种钒渣的综合利用方法,其特征在于按以下步骤进行:⑴破碎和粉磨、⑵混料、⑶熔融、⑷溶解和过滤、⑸钒的沉淀、⑹氧化铁的制备。本发明的原料来源广泛,一次性整体利用钒渣,并实现中间产物循环利用,降低了原材料和水的消耗,无二次污染,工艺简单,操作条件温和,成本低,产品附加值高,经济效益高。既解决了生产高纯度五氧化二钒的过程中有效去除铁的问题,又合理利用了钒和铁等资源,为钒渣提供了综合利用的新途径。
The invention provides a comprehensive utilization method of vanadium slag, which is characterized in that the following steps are carried out: (1) crushing and grinding, (2) mixing, (3) melting, (4) dissolving and filtering, (5) precipitation of vanadium, (6) preparation of iron oxide. The present invention has a wide range of sources of raw materials, uses vanadium slag as a whole at one time, and realizes the recycling of intermediate products, reduces the consumption of raw materials and water, has no secondary pollution, has simple process, mild operating conditions, low cost, high added value of products, and is economical. High benefit. It not only solves the problem of effectively removing iron in the process of producing high-purity vanadium pentoxide, but also rationally utilizes resources such as vanadium and iron, and provides a new way for comprehensive utilization of vanadium slag.
Description
技术领域 technical field
本发明涉及一种钒渣的综合利用方法,属于冶金技术领域。 The invention relates to a comprehensive utilization method of vanadium slag, which belongs to the technical field of metallurgy.
背景技术 Background technique
南非、俄罗斯和中国是世界产钒大国和出口大国,欧盟、日本和美国是主要进口国。据预测,在未来10年间全球可提供钒(折合五氧化二钒)10万吨/年的市场空间。预计从2011年到2020年间,世界钒需求量将保持持续增长趋势,年增长率4.3%左右。钒通常以含钒矿物或类质同相的形式存在,这使钒不能象铜铅锌等有色金属那样,通过机械选矿的方法得到钒精矿,故现有的提钒工艺中,处理的矿石和/或废渣品位都较低,因此找到一条适合对低品位钒矿石和/或废渣的处理工艺更具有现实意义。 South Africa, Russia and China are major vanadium producers and exporters in the world, while the European Union, Japan and the United States are major importers. It is predicted that in the next 10 years, the world can provide a market space of 100,000 tons of vanadium (equivalent to vanadium pentoxide) per year. It is estimated that from 2011 to 2020, the demand for vanadium in the world will maintain a continuous growth trend, with an annual growth rate of about 4.3%. Vanadium usually exists in the form of vanadium-containing minerals or similar substances, which prevents vanadium from obtaining vanadium concentrate through mechanical beneficiation like copper, lead, zinc and other non-ferrous metals. Therefore, in the existing vanadium extraction process, the processed ore and /Or the grade of waste residue is low, so it is more practical to find a treatment process suitable for low-grade vanadium ore and/or waste residue.
四川攀枝花、河北承德及安徽马鞍山等地都有大量的废弃钒渣,每年排放近120万吨,这些钒渣中钒含量普遍较低,一般为 2%左右,大部分存在于钒钛酸钙中,是提钒的主要对象,由于含有近40%的CaO而较其它钒矿难以提取。 Panzhihua in Sichuan, Chengde in Hebei and Ma'anshan in Anhui have a large amount of waste vanadium slag, which discharges nearly 1.2 million tons per year. The vanadium content in these vanadium slags is generally low, generally about 2%, and most of them exist in vanadium calcium titanate , is the main object of vanadium extraction, because it contains nearly 40% CaO, it is more difficult to extract than other vanadium ores.
专利申请号为200710202445.8的技术采用钙化焙烧—硫酸浸出工艺,以CaCO3作为钙源添加剂,对钒渣进行焙烧,并以硫酸浸出焙烧后产物中的钒。但该工艺存在如下缺点:⑴有新的废弃与新的污染,造成了部分矿物资源的流失;⑵浸出时间长,且耗酸量较大,每产出1t五氧化二钒要消耗81t硫酸,目前尚无法回收利用;⑶工艺过程中有二氧化硫挥发,会产生较严重的空气污染及操作人员中毒等问题;⑷加热条件下硫酸具有强腐蚀性,对设备腐蚀严重,生产上不安全。 The technology with the patent application number 200710202445.8 adopts the calcification roasting-sulfuric acid leaching process, uses CaCO 3 as the calcium source additive, roasts the vanadium slag, and leaches the vanadium in the roasted product with sulfuric acid. However, this process has the following disadvantages: (1) there is new waste and new pollution, resulting in the loss of some mineral resources; (2) the leaching time is long, and the acid consumption is relatively large, and 81t of sulfuric acid is consumed for every 1t of vanadium pentoxide produced. At present, it cannot be recycled; (3) sulfur dioxide volatilizes in the process, which will cause serious air pollution and operator poisoning; (4) sulfuric acid is highly corrosive under heating conditions, which seriously corrodes equipment and is unsafe in production.
钠化焙烧提钒是含钒原料提钒应用较多的工艺,其基本原理是:以食盐或苏打等钠盐为添加剂,通过焙烧将多价态的钒转化为水溶性五价钒的钠盐: 4NaCl+2V2O5+O2=4NaVO3+Cl2 Vanadium extraction by sodium roasting is a process that is widely used for extracting vanadium from vanadium-containing raw materials. Its basic principle is: using sodium salts such as table salt or soda as additives, and converting multivalent vanadium into water-soluble sodium salt of pentavalent vanadium by roasting : 4NaCl+2V 2 O 5 +O 2 =4NaVO 3 +Cl 2
再对钠化焙烧产物直接水浸,可得到含钒及少量铝杂质的浸取液,后加入铵盐(酸性铵盐沉淀法)制得偏钒酸铵沉淀,经焙烧得到粗五氧化二钒。再经碱溶、除杂并用铵盐二次沉钒得偏钒酸铵,焙烧后可得到纯度大于98%的V2O5。也可用硫酸浸渍焙烧产物: Then directly immerse the sodium roasted product in water to obtain a leaching solution containing vanadium and a small amount of aluminum impurities, and then add ammonium salt (acidic ammonium salt precipitation method) to obtain ammonium metavanadate precipitation, and obtain crude vanadium pentoxide after roasting . After alkali dissolution, impurity removal and second vanadium precipitation with ammonium salt, ammonium metavanadate can be obtained. After roasting, V 2 O 5 with a purity greater than 98% can be obtained. Sulfuric acid can also be used to impregnate roasted products:
2NaVO3+H2SO4=Na2SO4+H2O+ V2O5 2NaVO 3 +H 2 SO 4 =Na 2 SO 4 +H 2 O+V 2 O 5
分离得到粗V2O5,后经碱溶、除杂并用铵盐二次沉钒得偏钒酸铵,经焙烧可得高纯五氧化二钒。钠化焙烧提钒法工艺相对成熟、操作简单,早期投入小,因对钒选择性强、回收率高,一直是我国从原矿中提钒的主要方法。但由于钠化焙烧时产生大量Cl2、HCl及SO2等有毒气体,随着全球对环境的保护和提高资源有效利用的重视,寻找新的低污染、高效率的提钒工艺已成为全球钒冶炼工业中一个亟待解决的问题。 Crude V 2 O 5 is obtained by separation, and after alkali dissolution, impurity removal, and second vanadium precipitation with ammonium salt, ammonium metavanadate is obtained, and high-purity vanadium pentoxide can be obtained through roasting. Sodium roasting vanadium extraction method is relatively mature, simple operation, small initial investment, strong selectivity to vanadium, high recovery rate, has been the main method of extracting vanadium from raw ore in my country. However, due to the production of a large amount of toxic gases such as Cl 2 , HCl and SO 2 during sodium roasting, with the global emphasis on environmental protection and effective utilization of resources, it has become a global trend to find new low-pollution, high-efficiency vanadium extraction processes. An urgent problem to be solved in the smelting industry.
发明内容 Contents of the invention
发明目的:本发明提供一种钒渣的综合利用方法,其目的是解决以往利用钒渣提钒方法中所存在的高污染、低效率和不安全的问题;本发明从钒渣中获取五氧化二钒和氧化铁。 Purpose of the invention: the present invention provides a method for comprehensive utilization of vanadium slag, the purpose of which is to solve the problems of high pollution, low efficiency and unsafety in previous methods for extracting vanadium from vanadium slag; the present invention obtains pentoxide from vanadium slag Vanadium and iron oxide.
技术方案:本发明是通过以下技术方案来实现的: Technical solution: the present invention is achieved through the following technical solutions:
一种钒渣的综合利用方法,其特征在于按以下步骤进行: A comprehensive utilization method of vanadium slag is characterized in that it is carried out according to the following steps:
⑴破碎和粉磨:将钒渣经破碎和粉磨得到直径70~170μm的粉末; (1) Crushing and grinding: the vanadium slag is crushed and ground to obtain a powder with a diameter of 70-170 μm;
⑵混料:将钒渣粉末与硫酸铵和硫酸铵钾混合均匀,物料混合按重量百分比为钒渣粉末:硫酸铵:硫酸铵钾=1:5~12:2~5; (2) Mixing: Mix the vanadium slag powder with ammonium sulfate and ammonium potassium sulfate evenly, and mix the materials into vanadium slag powder by weight percentage: ammonium sulfate: potassium ammonium sulfate=1:5~12:2~5;
⑶熔融:将上述混匀的物料升温至270~440℃并保温10~45min,得到块状固体和氨气; (3) Melting: raise the temperature of the above mixed material to 270-440°C and keep it warm for 10-45 minutes to obtain massive solid and ammonia gas;
⑷溶解和过滤:将上述所获块状固体置于浓度为0.1~0.3mol/L的EDTA的水溶液中溶解,使块状固体中的铁与EDTA发生螯合反应,形成稳定的螯合物,且EDTA与块状固体中的铁的摩尔比为0.5~1.1:1,然后过滤得到滤液和残渣,残渣为铁水泥; (4) Dissolving and filtering: dissolving the above-mentioned block solid in an aqueous solution of EDTA with a concentration of 0.1 to 0.3 mol/L, so that iron in the block solid and EDTA undergo a chelation reaction to form a stable chelate. And the molar ratio of EDTA to the iron in the massive solid is 0.5~1.1:1, then filter to obtain the filtrate and residue, the residue is iron cement;
⑸钒的沉淀:向上述的滤液中通入步骤⑶得到的氨气,并控制pH为1.3~2.7,温度为40~80℃,使滤液中的钒沉淀,并在220~360℃灼烧30~150min,得到五氧化二钒; (5) Precipitation of vanadium: pass the ammonia gas obtained in step (3) into the above-mentioned filtrate, and control the pH to 1.3-2.7, and the temperature is 40-80°C to precipitate the vanadium in the filtrate, and burn it at 220-360°C for 30 ~150min, get vanadium pentoxide;
⑹氧化铁的制备:向钒沉淀的母液中通入步骤⑶得到的氨气,调节pH为6.8~7.5,并将母液在400~520℃灼烧30~60min,获取氧化铁;将灼烧过程中产生的气态物质冷却,得到硫酸铵和硫酸铵钾混合物,该混合物循环到步骤⑵进行再利用。 (6) Preparation of iron oxide: pass the ammonia gas obtained in step (3) into the mother liquor of vanadium precipitation, adjust the pH to 6.8-7.5, and burn the mother liquor at 400-520°C for 30-60 minutes to obtain iron oxide; The gaseous substance produced in the process is cooled to obtain a mixture of ammonium sulfate and potassium ammonium sulfate, which is recycled to step (2) for reuse.
“⑴”步骤中所述的钒渣,铁的重量百分比为20%~30%,钒的重量百分比为0.8%~3.0%。 For the vanadium slag described in the step "⑴", the weight percentage of iron is 20%-30%, and the weight percentage of vanadium is 0.8%-3.0%.
所述的步骤⑷的滤液中,水溶性钒占钒渣中钒的总重量的百分比≥93%,水溶性铁占钒渣中铁的总重量的百分比≤30%。 In the filtrate of the step (4), the percentage of water-soluble vanadium to the total weight of vanadium in the vanadium slag is ≥93%, and the percentage of water-soluble iron to the total weight of iron in the vanadium slag is ≤30%.
所述的步骤⑸中以五氧化二钒形式沉淀的钒占滤液中钒总重量的百分比≥99%;以氧化铁形式沉淀的铁占滤液中铁总重量的百分比≤0.0005%。 In the step (5), the vanadium precipitated in the form of vanadium pentoxide accounts for ≥99% of the total weight of vanadium in the filtrate; the percentage of iron precipitated in the form of iron oxide accounts for ≤0.0005% of the total weight of iron in the filtrate.
所述的产物五氧化二钒重量纯度≥98%;氧化铁重量纯度≥99%,其晶型为纳米氧化铁。 The product vanadium pentoxide has a weight purity of ≥98%; iron oxide has a weight purity of ≥99%, and its crystal form is nanometer iron oxide.
优点及效果: Advantages and effects:
与现有技术相比,本发明的特点及其有益效果是: Compared with prior art, feature of the present invention and beneficial effect thereof are:
将钒渣粉末与硫酸铵、硫酸铵钾混合均匀,是利用了硫酸铵钾特殊的化学性质,使熔融反应更具选择性:使更多的钒通过化学反应转化为水溶性钒,而使更少的铁转化为水溶性铁,进行铁和钒的初步分离(通常情况下,熔融反应不具选择性,如专利申请号为201010576256.9的技术)。水溶性钒占钒渣中钒的总重量的百分比≥93%,说明其转化率高,是现有技术无法实现的。 Mixing vanadium slag powder with ammonium sulfate and potassium ammonium sulfate evenly uses the special chemical properties of potassium ammonium sulfate to make the melting reaction more selective: more vanadium is converted into water-soluble vanadium through chemical reactions, and more A small amount of iron is converted into water-soluble iron for preliminary separation of iron and vanadium (usually, the melting reaction is not selective, such as the technology of patent application number 201010576256.9). The water-soluble vanadium accounts for more than 93% of the total weight of vanadium in the vanadium slag, indicating that the conversion rate is high, which cannot be realized by the prior art.
将熔融反应所获块状固体直接置于EDTA的水溶液中溶解,并在钒的沉淀过程中控制pH和温度,选择性地使钒沉淀,而铁不沉淀,因而产物五氧化二钒和氧化铁纯度高,实现了钒渣中钒和铁的彻底分离,是现有技术无法实现的。同时,熔融反应所获块状固体经溶解和过滤产生的残渣用作铁水泥——新型高性能特种水泥。 The massive solid obtained from the melting reaction is directly dissolved in the aqueous solution of EDTA, and the pH and temperature are controlled during the precipitation of vanadium to selectively precipitate the vanadium, but the iron does not precipitate, so the products are vanadium pentoxide and iron oxide The purity is high, and the complete separation of vanadium and iron in the vanadium slag is realized, which cannot be realized by the prior art. At the same time, the residue produced by dissolving and filtering the massive solid obtained from the melting reaction is used as iron cement—a new type of high-performance special cement.
将含Fe母液在400~520℃灼烧30~60min后获取的氧化铁,其晶型为纳米氧化铁,不同于普通氧化铁,故具有特殊的物理化学性质和用途,大大提高了产品的附加值,是现有技术无法实现的。 The iron oxide obtained by burning the Fe-containing mother liquor at 400-520°C for 30-60 minutes has a crystal form of nano-iron oxide, which is different from ordinary iron oxide, so it has special physical and chemical properties and uses, which greatly improves the additional value of the product. value, which cannot be achieved by existing technologies.
将钒的沉淀物在220~360℃灼烧30~150min,得到的五氧化二钒具有较高的晶化程度。一般认为,从水溶液中得到的沉淀物晶化程度低,甚至为非晶,但本发明通过灼烧,大大提高了五氧化二钒的晶化程度。 Burn the vanadium precipitate at 220-360° C. for 30-150 minutes, and the obtained vanadium pentoxide has a higher degree of crystallization. It is generally believed that the crystallization degree of the precipitate obtained from the aqueous solution is low, even amorphous, but the present invention greatly improves the crystallization degree of vanadium pentoxide by burning.
对铁和钒的分离而言,铁的百分含量越高,其分离的难度越大。因此,对铁的重量百分比为20%~30%的原料,如钒渣的铁和钒的分离工艺一直是研究的空白,本发明很好的实现了钒渣中钒和铁的彻底分离,是技术上显著的进步。 For the separation of iron and vanadium, the higher the percentage of iron, the more difficult the separation. Therefore, the iron and vanadium separation process of vanadium slag has always been a research blank for raw materials with a weight percentage of 20% to 30% of iron. Significant advances in technology.
综上所述,本发明的原料来源广泛,一次性整体利用钒渣,并实现中间产物循环利用,降低了原材料和水的消耗,无二次污染,工艺简单,操作条件温和,成本低,产品附加值高,经济效益高。既解决了生产高纯度五氧化二钒的过程中有效去除铁的问题,又合理利用了钒和铁等资源,为钒渣提供了综合利用的新途径,且本发明方法易于实现工业化生产,具有可观的环境效益、社会效益和经济效益。 In summary, the present invention has a wide range of sources of raw materials, one-time overall utilization of vanadium slag, and the recycling of intermediate products, reducing the consumption of raw materials and water, no secondary pollution, simple process, mild operating conditions, low cost, and products High added value and high economic benefit. It not only solves the problem of effectively removing iron in the process of producing high-purity vanadium pentoxide, but also rationally utilizes resources such as vanadium and iron, and provides a new way for comprehensive utilization of vanadium slag, and the method of the invention is easy to realize industrial production, and has the advantages of Considerable environmental benefits, social benefits and economic benefits.
附图说明:Description of drawings:
图1为本发明的工艺流程框图。 Fig. 1 is a process flow block diagram of the present invention.
具体实施方式:下面结合附图对本发明做进一步的说明: The specific embodiment: the present invention will be further described below in conjunction with accompanying drawing:
下面结合实施例对本发明作详细说明,但本发明的保护范围不仅限于下述的实施例。 The present invention will be described in detail below in conjunction with the examples, but the protection scope of the present invention is not limited to the following examples.
实施例1: Example 1:
⑴破碎和粉磨:将含铁的重量百分比为29%,钒的重量百分比为1.0%的钒渣经破碎和粉磨得到直径80μm的粉末; (1) Crushing and grinding: the vanadium slag containing 29% by weight of iron and 1.0% by weight of vanadium is crushed and ground to obtain a powder with a diameter of 80 μm;
⑵混料:按重量比钒渣粉末:硫酸铵:硫酸铵钾=1:7:3称取原料,将钒渣粉末与硫酸铵、硫酸铵钾混合均匀; (2) Mixing: According to the weight ratio of vanadium slag powder: ammonium sulfate: potassium ammonium sulfate = 1:7:3, weigh the raw materials, and mix the vanadium slag powder with ammonium sulfate and potassium ammonium sulfate evenly;
⑶熔融:将上述混匀的物料升温至300℃并保温15min,得到块状固体和氨气; (3) Melting: raise the temperature of the above-mentioned mixed material to 300°C and keep it warm for 15 minutes to obtain massive solid and ammonia gas;
⑷溶解和过滤:将上述所获块状固体置于浓度为0.15mol/L的EDTA的水溶液中溶解,且EDTA与铁的摩尔比为0.6:1,然后过滤得到滤液和残渣,残渣为铁水泥,滤液水溶性钒占钒渣中钒的总重量的百分比为94%,水溶性铁占钒渣中铁的总重量的百分比为27%; (4) Dissolving and filtering: the block solid obtained above is dissolved in an aqueous solution of EDTA with a concentration of 0.15mol/L, and the molar ratio of EDTA to iron is 0.6:1, and then filtered to obtain the filtrate and residue, the residue is iron cement , the percentage of filtrate water-soluble vanadium accounting for the total weight of vanadium in the vanadium slag is 94%, and the percentage of water-soluble iron accounting for the total weight of iron in the vanadium slag is 27%;
⑸钒的沉淀:向上述的滤液中通入步骤⑶得到的氨气,并控制pH为1.5,温度为45℃,使滤液中的钒沉淀,并在240℃灼烧50min,得到五氧化二钒;该步骤中以五氧化二钒形式沉淀的钒占滤液中钒总重量的百分比99.2%;以氧化铁形式沉淀的铁占滤液中铁总重量的百分比0.0004%。 (5) Precipitation of vanadium: pass the ammonia gas obtained in step (3) into the above-mentioned filtrate, and control the pH to 1.5 and the temperature to 45°C to precipitate the vanadium in the filtrate, and burn at 240°C for 50min to obtain vanadium pentoxide In this step, the vanadium precipitated in the form of vanadium pentoxide accounts for 99.2% of the total weight of vanadium in the filtrate; the iron precipitated in the form of iron oxide accounts for 0.0004% of the total weight of iron in the filtrate.
⑹氧化铁的制备:向钒沉淀的母液中通入步骤⑶得到的氨气,调节pH为7.0,并将母液在500℃灼烧60min,获取氧化铁;将灼烧过程中产生的气态物质冷却,得到硫酸铵和硫酸铵钾混合物,该混合物循环到步骤⑵进行再利用。 (6) Preparation of iron oxide: pass the ammonia gas obtained in step (3) into the mother liquor of vanadium precipitation, adjust the pH to 7.0, and burn the mother liquor at 500°C for 60 minutes to obtain iron oxide; cool the gaseous substance produced during the burning process , to obtain ammonium sulfate and potassium ammonium sulfate mixture, which is recycled to step (2) for reuse.
经检测,所述的产物五氧化二钒重量纯度99.2%;氧化铁重量纯度99.3%,其晶型为纳米氧化铁。 After testing, the product vanadium pentoxide has a weight purity of 99.2%; iron oxide has a weight purity of 99.3%, and its crystal form is nanometer iron oxide.
实施例2: Example 2:
⑴破碎和粉磨:将含铁的重量百分比为20%,钒的重量百分比为3.0%的钒渣经破碎和粉磨得到直径70μm的粉末; (1) Crushing and grinding: the vanadium slag containing 20% by weight of iron and 3.0% by weight of vanadium is crushed and ground to obtain a powder with a diameter of 70 μm;
⑵混料:按重量比钒渣粉末:硫酸铵:硫酸铵钾=1:5:5称取原料,将钒渣粉末与硫酸铵、硫酸铵钾混合均匀; (2) Mixing: According to the weight ratio of vanadium slag powder: ammonium sulfate: ammonium potassium sulfate=1:5:5, weigh the raw materials, and mix the vanadium slag powder with ammonium sulfate and ammonium potassium sulfate evenly;
⑶熔融:将上述混匀的物料升温至270℃并保温30min,得到块状固体和氨气; (3) Melting: raise the temperature of the above-mentioned mixed material to 270°C and keep it warm for 30 minutes to obtain massive solid and ammonia gas;
⑷溶解和过滤:将上述所获块状固体置于浓度为0.18mol/L的EDTA的水溶液中溶解,且EDTA与铁的摩尔比为1.1:1,然后过滤得到滤液和残渣,残渣为铁水泥,滤液水溶性钒占钒渣中钒的总重量的百分比为96%,水溶性铁占钒渣中铁的总重量的百分比为27%; (4) Dissolving and filtering: Dissolve the block solid obtained above in an aqueous solution of EDTA with a concentration of 0.18mol/L, and the molar ratio of EDTA to iron is 1.1:1, then filter to obtain the filtrate and residue, the residue is iron cement , the percentage of filtrate water-soluble vanadium accounting for the total weight of vanadium in the vanadium slag is 96%, and the percentage of water-soluble iron accounting for the total weight of iron in the vanadium slag is 27%;
⑸钒的沉淀:向上述的滤液中通入步骤⑶得到的氨气,并控制pH为1.3,温度为40℃,使滤液中的钒沉淀,并在220℃灼烧70min,得到五氧化二钒;该步骤中以五氧化二钒形式沉淀的钒占滤液中钒总重量的百分比99%;以氧化铁形式沉淀的铁占滤液中铁总重量的百分比0.0005%。 (5) Precipitation of vanadium: pass the ammonia gas obtained in step (3) into the above-mentioned filtrate, and control the pH to 1.3 and the temperature to 40°C to precipitate the vanadium in the filtrate, and burn at 220°C for 70min to obtain vanadium pentoxide In this step, the vanadium precipitated in the form of vanadium pentoxide accounts for 99% of the total weight of vanadium in the filtrate; the iron precipitated in the form of iron oxide accounts for 0.0005% of the total weight of iron in the filtrate.
⑹氧化铁的制备:向钒沉淀的母液中通入步骤⑶得到的氨气,调节pH为6.8,并将母液在520℃灼烧40min,获取氧化铁;将灼烧过程中产生的气态物质冷却,得到硫酸铵和硫酸铵钾混合物,该混合物循环到步骤⑵进行再利用。 (6) Preparation of iron oxide: pass the ammonia gas obtained in step (3) into the mother liquor of vanadium precipitation, adjust the pH to 6.8, and burn the mother liquor at 520°C for 40 minutes to obtain iron oxide; cool the gaseous substance produced during the burning process , to obtain ammonium sulfate and potassium ammonium sulfate mixture, which is recycled to step (2) for reuse.
经检测,所述的产物五氧化二钒重量纯度98.7%;氧化铁重量纯度99.1%,其晶型为纳米氧化铁。 After testing, the product vanadium pentoxide has a weight purity of 98.7%; iron oxide has a weight purity of 99.1%, and its crystal form is nano iron oxide.
实施例3: Example 3:
⑴破碎和粉磨:将含铁的重量百分比为30%,钒的重量百分比为0.8%的钒渣经破碎和粉磨得到直径100μm的粉末; (1) Crushing and grinding: the vanadium slag containing 30% by weight of iron and 0.8% by weight of vanadium is crushed and ground to obtain a powder with a diameter of 100 μm;
⑵混料:按重量比钒渣粉末:硫酸铵:硫酸铵钾=1:12:2称取原料,将钒渣粉末与硫酸铵、硫酸铵钾混合均匀; (2) Mixing: According to the weight ratio of vanadium slag powder: ammonium sulfate: potassium ammonium sulfate = 1:12:2, weigh the raw materials, and mix the vanadium slag powder with ammonium sulfate and potassium ammonium sulfate evenly;
⑶熔融:将上述混匀的物料升温至400℃并保温10min,得到块状固体和氨气; (3) Melting: raise the temperature of the above-mentioned mixed material to 400°C and keep it warm for 10 minutes to obtain massive solid and ammonia gas;
⑷溶解和过滤:将上述所获块状固体置于浓度为0.1mol/L的EDTA的水溶液中溶解,且EDTA与铁的摩尔比为0.8:1,然后过滤得到滤液和残渣,残渣为铁水泥,滤液水溶性钒占钒渣中钒的总重量的百分比为93%,水溶性铁占钒渣中铁的总重量的百分比为15%; (4) Dissolving and filtering: Dissolve the block solid obtained above in an aqueous solution of EDTA with a concentration of 0.1mol/L, and the molar ratio of EDTA to iron is 0.8:1, then filter to obtain the filtrate and residue, the residue is iron cement , the percentage of filtrate water-soluble vanadium accounting for the total weight of vanadium in the vanadium slag is 93%, and the percentage of water-soluble iron accounting for the total weight of iron in the vanadium slag is 15%;
⑸钒的沉淀:向上述的滤液中通入步骤⑶得到的氨气,并控制pH为2.7,温度为70℃,使滤液中的钒沉淀,并在360℃灼烧30min,得到五氧化二钒;该步骤中以五氧化二钒形式沉淀的钒占滤液中钒总重量的百分比99.8%;以氧化铁形式沉淀的铁占滤液中铁总重量的百分比0.0001%。 (5) Precipitation of vanadium: pass the ammonia gas obtained in step (3) into the above-mentioned filtrate, and control the pH to 2.7 and the temperature to 70°C to precipitate the vanadium in the filtrate, and burn at 360°C for 30min to obtain vanadium pentoxide In this step, the vanadium precipitated in the form of vanadium pentoxide accounts for 99.8% of the total weight of vanadium in the filtrate; the iron precipitated in the form of iron oxide accounts for 0.0001% of the total weight of iron in the filtrate.
⑹氧化铁的制备:向钒沉淀的母液中通入步骤⑶得到的氨气,调节pH为7.5,并将母液在400℃灼烧50min,获取氧化铁;将灼烧过程中产生的气态物质冷却,得到硫酸铵和硫酸铵钾混合物,该混合物循环到步骤⑵进行再利用。 (6) Preparation of iron oxide: pass the ammonia gas obtained in step (3) into the mother liquor of vanadium precipitation, adjust the pH to 7.5, and burn the mother liquor at 400°C for 50 minutes to obtain iron oxide; cool the gaseous substance produced during the burning process , to obtain ammonium sulfate and potassium ammonium sulfate mixture, which is recycled to step (2) for reuse.
经检测,所述的产物五氧化二钒重量纯度99%;氧化铁重量纯度99.2%,其晶型为纳米氧化铁。 After testing, the product vanadium pentoxide has a weight purity of 99%; iron oxide has a weight purity of 99.2%, and its crystal form is nano iron oxide.
实施例4: Example 4:
⑴破碎和粉磨:将含铁的重量百分比为26%,钒的重量百分比为1.5%的钒渣经破碎和粉磨得到直径100μm的粉末; (1) Crushing and grinding: the vanadium slag containing 26% by weight of iron and 1.5% by weight of vanadium is crushed and ground to obtain a powder with a diameter of 100 μm;
⑵混料:按重量比钒渣粉末:硫酸铵:硫酸铵钾=1:8:4称取原料,将钒渣粉末与硫酸铵、硫酸铵钾混合均匀; (2) Mixing: According to the weight ratio of vanadium slag powder: ammonium sulfate: potassium ammonium sulfate = 1:8:4, weigh the raw materials, and mix the vanadium slag powder with ammonium sulfate and potassium ammonium sulfate evenly;
⑶熔融:将上述混匀的物料升温至440℃并保温30min,得到块状固体和氨气; (3) Melting: raise the temperature of the above-mentioned mixed material to 440°C and keep it warm for 30 minutes to obtain massive solid and ammonia gas;
⑷溶解和过滤:将上述所获块状固体置于浓度为0.3mol/L的EDTA的水溶液中溶解,且EDTA与铁的摩尔比为0.5:1,然后过滤得到滤液和残渣,残渣为铁水泥,滤液水溶性钒占钒渣中钒的总重量的百分比为98%,水溶性铁占钒渣中铁的总重量的百分比为8%; (4) Dissolving and filtering: Dissolve the block solid obtained above in an aqueous solution of EDTA with a concentration of 0.3mol/L, and the molar ratio of EDTA to iron is 0.5:1, then filter to obtain the filtrate and residue, the residue is iron cement , the percentage of filtrate water-soluble vanadium accounting for the total weight of vanadium in the vanadium slag is 98%, and the percentage of water-soluble iron accounting for the total weight of iron in the vanadium slag is 8%;
⑸钒的沉淀:向上述的滤液中通入步骤⑶得到的氨气,并控制pH为1.6,温度为80℃,使滤液中的钒沉淀,并在230℃灼烧150min,得到五氧化二钒;该步骤中以五氧化二钒形式沉淀的钒占滤液中钒总重量的百分比99.1%;以氧化铁形式沉淀的铁占滤液中铁总重量的百分比0.0003%; (5) Precipitation of vanadium: pass the ammonia gas obtained in step (3) into the above-mentioned filtrate, and control the pH to 1.6 and the temperature to 80°C to precipitate the vanadium in the filtrate, and burn at 230°C for 150min to obtain vanadium pentoxide In this step, the vanadium precipitated in the form of vanadium pentoxide accounts for 99.1% of the total weight of vanadium in the filtrate; the iron precipitated in the form of iron oxide accounts for 0.0003% of the total weight of iron in the filtrate;
⑹氧化铁的制备:向钒沉淀的母液中通入步骤⑶得到的氨气,调节pH为7.0,并将母液在450℃灼烧30min,获取氧化铁;将灼烧过程中产生的气态物质冷却,得到硫酸铵和硫酸铵钾混合物,该混合物循环到步骤⑵进行再利用。 (6) Preparation of iron oxide: pass the ammonia gas obtained in step (3) into the mother liquor of vanadium precipitation, adjust the pH to 7.0, and burn the mother liquor at 450°C for 30 minutes to obtain iron oxide; cool the gaseous substance produced during the burning process , to obtain ammonium sulfate and potassium ammonium sulfate mixture, which is recycled to step (2) for reuse.
经检测,所述的产物五氧化二钒重量纯度98.3%;氧化铁重量纯度99.7%,其晶型为纳米氧化铁。 After testing, the product vanadium pentoxide has a weight purity of 98.3%; iron oxide has a weight purity of 99.7%, and its crystal form is nanometer iron oxide.
实施例5: Example 5:
⑴破碎和粉磨:将含铁的重量百分比为21%,钒的重量百分比为2.0%的钒渣经破碎和粉磨得到直径170μm的粉末; (1) Crushing and grinding: the vanadium slag containing 21% by weight of iron and 2.0% by weight of vanadium is crushed and ground to obtain a powder with a diameter of 170 μm;
⑵混料:按重量比钒渣粉末:硫酸铵:硫酸铵钾=1:5:2称取原料,将钒渣粉末与硫酸铵、硫酸铵钾混合均匀; (2) Mixing: According to the weight ratio of vanadium slag powder: ammonium sulfate: potassium ammonium sulfate = 1:5:2, weigh the raw materials, and mix the vanadium slag powder with ammonium sulfate and potassium ammonium sulfate evenly;
⑶熔融:将上述混匀的物料升温至320℃并保温45min,得到块状固体和氨气; (3) Melting: raise the temperature of the above mixed material to 320°C and keep it warm for 45 minutes to obtain massive solid and ammonia gas;
⑷溶解和过滤:将上述所获块状固体置于浓度为0.24mol/L的EDTA的水溶液中溶解,且EDTA与铁的摩尔比为1:1,然后过滤得到滤液和残渣,残渣为铁水泥,滤液水溶性钒占钒渣中钒的总重量的百分比为98%,水溶性铁占钒渣中铁的总重量的百分比为30%; (4) Dissolving and filtering: Dissolve the blocky solid obtained above in an aqueous solution of EDTA with a concentration of 0.24mol/L, and the molar ratio of EDTA to iron is 1:1, then filter to obtain the filtrate and residue, the residue is iron cement , the percentage of filtrate water-soluble vanadium accounting for the total weight of vanadium in the vanadium slag is 98%, and the percentage of water-soluble iron accounting for the total weight of iron in the vanadium slag is 30%;
⑸钒的沉淀:向上述的滤液中通入步骤⑶得到的氨气,并控制pH为2.0,温度为50℃,使滤液中的钒沉淀,并在300℃灼烧60min,得到五氧化二钒;该步骤中以五氧化二钒形式沉淀的钒占滤液中钒总重量的百分比99.9%;以氧化铁形式沉淀的铁占滤液中铁总重量的百分比0.0002%; (5) Precipitation of vanadium: pass the ammonia gas obtained in step (3) into the above-mentioned filtrate, and control the pH to 2.0 and the temperature to 50°C to precipitate the vanadium in the filtrate, and burn at 300°C for 60min to obtain vanadium pentoxide In this step, the vanadium precipitated in the form of vanadium pentoxide accounts for 99.9% of the total weight of vanadium in the filtrate; the iron precipitated in the form of iron oxide accounts for 0.0002% of the total weight of iron in the filtrate;
⑹氧化铁的制备:向钒沉淀的母液中通入步骤⑶得到的氨气,调节pH为7.0,并将母液在420℃灼烧45min,获取氧化铁;将灼烧过程中产生的气态物质冷却,得到硫酸铵和硫酸铵钾混合物,该混合物循环到步骤⑵进行再利用。 (6) Preparation of iron oxide: pass the ammonia gas obtained in step (3) into the vanadium-precipitated mother liquor, adjust the pH to 7.0, and burn the mother liquor at 420°C for 45 minutes to obtain iron oxide; cool the gaseous substances produced during the burning process , to obtain ammonium sulfate and potassium ammonium sulfate mixture, which is recycled to step (2) for reuse.
经检测,所述的产物五氧化二钒重量纯度99.8%;氧化铁重量纯度99%,其晶型为纳米氧化铁。 After testing, the product vanadium pentoxide has a weight purity of 99.8%; iron oxide has a weight purity of 99%, and its crystal form is nanometer iron oxide.
实施例6: Embodiment 6:
⑴破碎和粉磨:将含铁的重量百分比为27%,钒的重量百分比为2.8%的钒渣经破碎和粉磨得到直径160μm的粉末; (1) Crushing and grinding: the vanadium slag containing 27% by weight of iron and 2.8% by weight of vanadium is crushed and ground to obtain a powder with a diameter of 160 μm;
⑵混料:按重量比钒渣粉末:硫酸铵:硫酸铵钾=1:5:2称取原料,将钒渣粉末与硫酸铵、硫酸铵钾混合均匀; (2) Mixing: According to the weight ratio of vanadium slag powder: ammonium sulfate: potassium ammonium sulfate = 1:5:2, weigh the raw materials, and mix the vanadium slag powder with ammonium sulfate and potassium ammonium sulfate evenly;
⑶熔融:将上述混匀的物料升温至420℃并保温45min,得到块状固体和氨气; (3) Melting: heat the above-mentioned mixed material to 420°C and keep it warm for 45 minutes to obtain massive solid and ammonia gas;
⑷溶解和过滤:将上述所获块状固体置于浓度为0.26mol/L的EDTA的水溶液中溶解,且EDTA与铁的摩尔比为1:1,然后过滤得到滤液和残渣,残渣为铁水泥,滤液水溶性钒占钒渣中钒的总重量的百分比为99%,水溶性铁占钒渣中铁的总重量的百分比为1.5%; (4) Dissolving and filtering: Dissolve the blocky solid obtained above in an aqueous solution of EDTA with a concentration of 0.26mol/L, and the molar ratio of EDTA to iron is 1:1, then filter to obtain the filtrate and residue, the residue is iron cement , the percentage of filtrate water-soluble vanadium accounting for the total weight of vanadium in the vanadium slag is 99%, and the percentage of water-soluble iron accounting for the total weight of iron in the vanadium slag is 1.5%;
⑸钒的沉淀:向上述的滤液中通入步骤⑶得到的氨气,并控制pH为2.0,温度为75℃,使滤液中的钒沉淀,并在300℃灼烧100min,得到五氧化二钒;该步骤中以五氧化二钒形式沉淀的钒占滤液中钒总重量的百分比99.3%;以氧化铁形式沉淀的铁占滤液中铁总重量的百分比0.0002%; (5) Precipitation of vanadium: Pass the ammonia gas obtained in step (3) into the above-mentioned filtrate, and control the pH to 2.0 and the temperature to 75°C to precipitate the vanadium in the filtrate, and burn at 300°C for 100min to obtain vanadium pentoxide In this step, the vanadium precipitated in the form of vanadium pentoxide accounts for 99.3% of the total weight of vanadium in the filtrate; the iron precipitated in the form of iron oxide accounts for 0.0002% of the total weight of iron in the filtrate;
⑹氧化铁的制备:向钒沉淀的母液中通入步骤⑶得到的氨气,调节pH为7.0,并将母液在420℃灼烧45min,获取氧化铁;将灼烧过程中产生的气态物质冷却,得到硫酸铵和硫酸铵钾混合物,该混合物循环到步骤⑵进行再利用。 (6) Preparation of iron oxide: pass the ammonia gas obtained in step (3) into the vanadium-precipitated mother liquor, adjust the pH to 7.0, and burn the mother liquor at 420°C for 45 minutes to obtain iron oxide; cool the gaseous substances produced during the burning process , to obtain ammonium sulfate and potassium ammonium sulfate mixture, which is recycled to step (2) for reuse.
经检测,所述的产物五氧化二钒重量纯度99.8%;氧化铁重量纯度99%,其晶型为纳米氧化铁。 After testing, the product vanadium pentoxide has a weight purity of 99.8%; iron oxide has a weight purity of 99%, and its crystal form is nanometer iron oxide.
EDTA为乙二胺四乙酸或者其二钠盐。 EDTA is ethylenediaminetetraacetic acid or its disodium salt.
本发明通过低污染的途径进行高效率的提钒工艺,效果明显,很好的解决了以往的提钒工艺中所存在的高污染、低效率的问题,利于推广应用。 The invention carries out a high-efficiency vanadium extraction process through a low-pollution approach, and the effect is obvious, which well solves the problems of high pollution and low efficiency in the previous vanadium extraction process, and is beneficial to popularization and application.
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