CN101709390B - An online circulation method for vanadium extraction process from stone coal - Google Patents
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- 238000000034 method Methods 0.000 title claims abstract description 85
- 229910052720 vanadium Inorganic materials 0.000 title claims abstract description 74
- LEONUFNNVUYDNQ-UHFFFAOYSA-N vanadium atom Chemical compound [V] LEONUFNNVUYDNQ-UHFFFAOYSA-N 0.000 title claims abstract description 74
- 239000003245 coal Substances 0.000 title claims abstract description 25
- 239000004575 stone Substances 0.000 title claims abstract description 25
- 238000000605 extraction Methods 0.000 title description 19
- 239000002253 acid Substances 0.000 claims abstract description 47
- 239000000243 solution Substances 0.000 claims abstract description 38
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims abstract description 37
- 238000002386 leaching Methods 0.000 claims abstract description 36
- GNTDGMZSJNCJKK-UHFFFAOYSA-N divanadium pentaoxide Chemical compound O=[V](=O)O[V](=O)=O GNTDGMZSJNCJKK-UHFFFAOYSA-N 0.000 claims abstract description 22
- 239000011734 sodium Substances 0.000 claims abstract description 22
- 229910052708 sodium Inorganic materials 0.000 claims abstract description 22
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonia chloride Chemical compound [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 claims abstract description 20
- 239000002893 slag Substances 0.000 claims abstract description 19
- 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 abstract description 18
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 18
- 239000007921 spray Substances 0.000 claims abstract description 16
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims abstract description 12
- 239000011347 resin Substances 0.000 claims abstract description 11
- 229920005989 resin Polymers 0.000 claims abstract description 11
- 235000019270 ammonium chloride Nutrition 0.000 claims abstract description 10
- 238000001179 sorption measurement Methods 0.000 claims abstract description 10
- 238000005507 spraying Methods 0.000 claims abstract description 10
- 238000001354 calcination Methods 0.000 claims abstract description 9
- 229910021529 ammonia Inorganic materials 0.000 claims abstract description 8
- 150000002500 ions Chemical class 0.000 claims abstract description 8
- 238000006386 neutralization reaction Methods 0.000 claims abstract description 5
- 150000003863 ammonium salts Chemical class 0.000 claims abstract description 3
- 239000007788 liquid Substances 0.000 claims description 35
- 238000001556 precipitation Methods 0.000 claims description 27
- 230000002378 acidificating effect Effects 0.000 claims description 20
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 17
- 239000003546 flue gas Substances 0.000 claims description 17
- 239000012452 mother liquor Substances 0.000 claims description 13
- VWBLQUSTSLXQON-UHFFFAOYSA-N N.[V+5] Chemical compound N.[V+5] VWBLQUSTSLXQON-UHFFFAOYSA-N 0.000 claims description 12
- 239000003929 acidic solution Substances 0.000 claims description 7
- 238000007654 immersion Methods 0.000 claims description 5
- 238000005554 pickling Methods 0.000 claims description 4
- 230000009615 deamination Effects 0.000 claims description 3
- 238000006481 deamination reaction Methods 0.000 claims description 3
- VZEXJUAYWWLSEP-UHFFFAOYSA-N N.[Cl].Cl Chemical compound N.[Cl].Cl VZEXJUAYWWLSEP-UHFFFAOYSA-N 0.000 claims description 2
- 239000007789 gas Substances 0.000 abstract description 8
- 238000004519 manufacturing process Methods 0.000 abstract description 8
- 239000002351 wastewater Substances 0.000 abstract description 8
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- 230000000694 effects Effects 0.000 abstract description 3
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- 238000004064 recycling Methods 0.000 abstract description 2
- 230000001376 precipitating effect Effects 0.000 abstract 3
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- 235000013336 milk Nutrition 0.000 description 5
- 210000004080 milk Anatomy 0.000 description 5
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 description 4
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 4
- 235000011941 Tilia x europaea Nutrition 0.000 description 4
- 239000004571 lime Substances 0.000 description 4
- 238000007664 blowing Methods 0.000 description 3
- 239000010445 mica Substances 0.000 description 3
- 229910052618 mica group Inorganic materials 0.000 description 3
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 2
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 2
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 2
- 239000000920 calcium hydroxide Substances 0.000 description 2
- 235000011116 calcium hydroxide Nutrition 0.000 description 2
- 239000000460 chlorine Substances 0.000 description 2
- 229910052804 chromium Inorganic materials 0.000 description 2
- 239000011651 chromium Substances 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- 235000019738 Limestone Nutrition 0.000 description 1
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 239000004480 active ingredient Substances 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 239000001110 calcium chloride Substances 0.000 description 1
- 229910001628 calcium chloride Inorganic materials 0.000 description 1
- 239000000292 calcium oxide Substances 0.000 description 1
- 235000012255 calcium oxide Nutrition 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 238000002425 crystallisation Methods 0.000 description 1
- 230000008025 crystallization Effects 0.000 description 1
- 238000005261 decarburization Methods 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 238000007791 dehumidification Methods 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 239000000706 filtrate Substances 0.000 description 1
- 239000003517 fume Substances 0.000 description 1
- 239000010440 gypsum Substances 0.000 description 1
- 229910052602 gypsum Inorganic materials 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 239000006028 limestone Substances 0.000 description 1
- 235000010755 mineral Nutrition 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 229910052938 sodium sulfate Inorganic materials 0.000 description 1
- 235000011152 sodium sulphate Nutrition 0.000 description 1
- LSGOVYNHVSXFFJ-UHFFFAOYSA-N vanadate(3-) Chemical compound [O-][V]([O-])([O-])=O LSGOVYNHVSXFFJ-UHFFFAOYSA-N 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
Description
技术领域technical field
本发明属于石煤提钒技术领域。具体涉及一种用于石煤提钒工艺的在线循环方法。The invention belongs to the technical field of vanadium extraction from stone coal. In particular, it relates to an online circulation method used in the process of extracting vanadium from stone coal.
背景技术Background technique
石煤是我国独特的、重要的一种含钒资源。石煤中的钒主要以低价态形式赋存于云母等矿物晶格中,从石煤中提取钒,必须将钒从云母相中解离出来。破坏石煤中含钒云母晶格结构最有效的方法是高温氧化焙烧,现有的石煤提钒工艺多为“脱碳-钠化焙烧-水浸-酸浸-离子树脂交换-酸性铵盐沉钒-脱氨煅烧”,尽管该提钒工艺操作简单,但工艺过程中亦产生大量的废气、废水和废渣:钠化焙烧产生酸性气体,其中含有HCl、Cl2、SO2;脱氨煅烧和吹脱沉钒母液产生氨气,这些气体都需经过处理才能排放;工艺过程中产生的废水是水浸液经过离子树脂吸附后形成的吸附下液,以及铵盐沉钒后的沉钒母液;吸附下液虽可直接排放,但也会浪费宝贵的水资源;沉钒母液pH值为3左右且含有8000~10000mg/L的NH4 +,需经处理后才能达到排放标准;酸浸液也需经过处理后才可回收其中的钒。在环保日益重视、倡导节能减排的今天,对工艺过程中产生的废气、废水及相应的渣等都需进行合理的处理,达到相应的排放标准。为此,已引起科技人员的关注:Stone coal is a unique and important vanadium resource in my country. Vanadium in stone coal mainly exists in the low-valence state in mica and other mineral lattices. To extract vanadium from stone coal, vanadium must be dissociated from the mica phase. The most effective way to destroy the vanadium-containing mica lattice structure in stone coal is high-temperature oxidation roasting. The existing vanadium extraction process from stone coal is mostly "decarburization-sodium roasting-water leaching-acid leaching-ion resin exchange-acid ammonium salt Vanadium Precipitation - Deamination Calcination", although the vanadium extraction process is simple to operate, a large amount of waste gas, waste water and waste residue are also produced in the process: sodium roasting produces acid gas, which contains HCl, Cl 2 , SO 2 ; deammonization calcining And blow off the vanadium precipitation mother liquor to produce ammonia gas, these gases need to be treated before they can be discharged; the wastewater generated in the process is the adsorption liquid formed after the water immersion solution is absorbed by the ion resin, and the vanadium precipitation mother liquor after the ammonium salt vanadium precipitation ; Although the adsorbed liquid can be directly discharged, it will also waste precious water resources; the pH value of the vanadium precipitation mother liquid is about 3 and contains 8000-10000 mg/L NH 4 + , and it needs to be treated before it can reach the discharge standard; acid leaching liquid It also needs to be processed before the vanadium in it can be recovered. Today, with increasing emphasis on environmental protection and advocating energy conservation and emission reduction, the waste gas, waste water and corresponding slag generated in the process need to be treated reasonably to meet the corresponding emission standards. For this reason, it has attracted the attention of scientific and technical personnel:
“钠化焙烧法生产五氧化二钒的废气处理方法”(CN101322907A)专利技术公开了一种钠化焙烧法生产五氧化二钒的废气处理方法,采用由三个多功能塔和多个循环水池组成的循环系统来消除废气。"Exhaust gas treatment method for producing vanadium pentoxide by sodium roasting method" (CN101322907A) patent technology discloses a waste gas treatment method for producing vanadium pentoxide by sodium roasting method, using three multifunctional towers and multiple circulating pools Composed of circulation system to eliminate exhaust gas.
“五氧化二钒生产中的废气治理及其综合利用技术”(CN100998931A)专利技术公开了一种五氧化二钒生产废气治理及其综合利用技术。采用废气降温、石灰乳喷雾中和、生石灰颗粒过滤吸收除湿三步处理,废气降温处理产生的冷凝液和石灰乳喷雾处理后的石灰乳澄清液,通过调节pH值和蒸发、浓缩、结晶、干燥脱水制取氯化钙。"Exhaust gas treatment and comprehensive utilization technology in the production of vanadium pentoxide" (CN100998931A) patent technology discloses a production waste gas treatment and comprehensive utilization technology of vanadium pentoxide. Adopt three-step treatment of waste gas cooling, lime milk spray neutralization, quicklime particle filtration, absorption and dehumidification, the condensate produced by waste gas cooling treatment and the lime milk clarified liquid after lime milk spray treatment, through adjusting the pH value and evaporation, concentration, crystallization, and drying Dehydration to produce calcium chloride.
“一种处理酸性沉钒废水的工艺”(CN1406882A)专利技术公开了一种处理酸性沉钒废水的工艺。具体为先除铬,再除氨,使最后排放的尾水铬和氨都达到排放标准。"A Process for Treating Acidic Vanadium Precipitation Wastewater" (CN1406882A) patent technology discloses a process for treating acidic vanadium precipitation wastewater. Specifically, chromium is removed first, and then ammonia is removed, so that both chromium and ammonia in the tail water discharged at the end can meet the emission standards.
“一种含钒石煤钠化焙烧烟气净化方法”(CN101069807A)专利技术公开了一种含钒石煤钠化焙烧烟气净化方法。该方法用石灰乳或石灰石乳做焙烧烟气净化剂,经过吸收HCl等酸性气体后过滤,滤液加酸或碱调节pH值后,再加硫酸钠转型二次过滤,得到石膏和氯化钠溶液。"A method for purifying flue gas from sodium roasting of vanadium-containing stone coal" (CN101069807A) patent technology discloses a method for purifying flue gas from sodium roasting of vanadium-containing stone coal. In this method, lime milk or limestone milk is used as a roasting flue gas purifier, after absorbing HCl and other acidic gases, it is filtered, and the filtrate is added with acid or alkali to adjust the pH value, and then sodium sulfate is added for secondary filtration to obtain gypsum and sodium chloride solution. .
但上述这些技术方法均只是针对石煤提钒工艺过程中“三废”的一种进行处理,且其目的均在于将“三废”进行无害化后排放,或在处理过程中获得一些其他工业副产品,而不是将“三废”中的有效成分进行综合利用,无法实现将“三废”转化为提钒工艺过程中所需的中间产品循环利用。However, the above-mentioned technical methods are only for the treatment of one of the "three wastes" in the process of vanadium extraction from stone coal, and their purpose is to discharge the "three wastes" harmlessly, or to obtain some other industrial by-products during the treatment process Instead of comprehensively utilizing the active ingredients in the "three wastes", it is impossible to realize the recycling of the intermediate products required in the process of converting the "three wastes" into vanadium extraction.
发明内容Contents of the invention
本发明旨在克服已有技术缺陷,目的是提供一种工艺简单、流程合理、环境友好、节能减排、可降低生产成本的用于石煤提钒工艺的在线循环方法。The invention aims to overcome the defects of the existing technology, and aims to provide an online circulation method for vanadium extraction from stone coal, which has simple process, reasonable process, environment-friendly, energy saving and emission reduction, and can reduce production cost.
为实现上述目的,本发明在现有的石煤原矿经“脱碳-钠化焙烧-水浸-酸浸-离子树脂交换-酸性铵盐沉钒-脱氨煅烧”的提钒工艺基础上,采用的技术方案是:In order to achieve the above object, the present invention is based on the vanadium extraction process of the existing stone coal raw ore through "decarburization-sodium roasting-water leaching-acid leaching-ion resin exchange-acidic ammonium salt vanadium precipitation-deammoniation calcination", The technical solutions adopted are:
(1)用离子树脂交换工序中产生的吸附下液对钠化焙烧工序产生的酸性烟气进行一级喷淋,经一级喷淋形成的酸性溶液返回酸浸工序。(1) The acidic flue gas produced in the sodium roasting process is sprayed with the adsorption liquid produced in the ion resin exchange process, and the acidic solution formed by the primary spray is returned to the acid leaching process.
(2)将酸浸工序所得的酸浸液进行中和处理得富钒渣和处理液;富钒渣返回钠化焙烧工序,处理液达标外排。(2) Neutralize the acid leaching solution obtained in the acid leaching process to obtain a vanadium-rich slag and a treatment solution; return the vanadium-rich slag to the sodium roasting process, and discharge the treatment solution up to the standard.
(3)酸性铵盐沉钒工序产生的沉钒母液经吹脱处理产生氨气和碱性处理液,吹脱处理所得的氨气和脱氨煅烧工序产生的氨气用盐酸溶液喷淋产生氯化铵,氯化铵返回酸性铵盐沉钒工序;碱性处理液对经一级喷淋的酸性烟气进行二级喷淋,二级喷淋后烟气排放,所形成的喷淋下液返回水浸工序。(3) The vanadium precipitation mother liquor produced in the acidic ammonium salt vanadium precipitation process is stripped to produce ammonia and alkaline treatment liquid, and the ammonia gas produced in the stripping process and the ammonia gas produced in the deamination and calcination process are sprayed with hydrochloric acid solution to produce chlorine Ammonium chloride and ammonium chloride return to the acidic ammonium salt vanadium precipitation process; the alkaline treatment liquid performs secondary spraying on the acidic flue gas that has been sprayed in the primary level, and the flue gas is discharged after the secondary spraying, and the formed spray liquid Return to the flooding process.
所述的石煤原矿的五氧化二钒品位≥0.7%。The vanadium pentoxide grade of the raw stone coal ore is ≥0.7%.
所述的中和处理是:先将五氧化二钒浓度为100~300mg/l的酸浸所得的低浓度含钒酸浸液预热至20~45℃,再按物质的量比为nV∶nFe=1∶1~1∶3向该酸浸液中加入FeSO4·7H2O,然后调节至pH=4~6,在45~60℃条件下反应10~30min,最后经固液分离得富钒渣和处理液。The neutralization treatment is: first preheating the low-concentration vanadium-containing acid leaching solution obtained by acid leaching with a vanadium pentoxide concentration of 100-300mg/l to 20-45°C, and then setting the ratio of n V :n Fe =1:1~1:3 Add FeSO 4 ·7H 2 O to the pickling solution, then adjust to pH=4~6, react at 45~60°C for 10~30min, and finally pass solid-liquid The vanadium-rich slag and treatment liquid are separated.
由于采用上述技术方案,本发明在现有的石煤原矿经“脱碳-钠化焙烧-水浸-酸浸-离子树脂交换-酸性铵盐沉钒-脱氨煅烧”的提钒工艺基础上,采用在线循环技术,即根据现有提钒工艺的自身特点,将所产生的废气、废水,如吸附下液、酸性烟气、氨气、酸浸液和沉钒母液等进行综合利用处理,使之形成工艺过程中能使用的中间产品,如酸性溶液、富钒渣、氯化铵等,循环利用于提钒工艺中。其特点在于:Due to the adoption of the above technical scheme, the present invention is based on the vanadium extraction process of the existing stone coal raw ore through "decarburization-sodium roasting-water leaching-acid leaching-ion resin exchange-acidic ammonium salt vanadium precipitation-deammoniation calcination" , using online circulation technology, that is, according to the characteristics of the existing vanadium extraction process, the waste gas and waste water generated, such as adsorption liquid, acid flue gas, ammonia gas, acid leaching solution and vanadium precipitation mother liquor, etc. are comprehensively utilized and treated. Make it into intermediate products that can be used in the process, such as acid solution, vanadium-rich slag, ammonium chloride, etc., which can be recycled in the vanadium extraction process. Its characteristics are:
1、在离子树脂交换工序中产生的吸附下液为含一定杂质离子的中性溶液,将该溶液用于对钠化焙烧产生的酸性烟气进行一级喷淋,温度为300℃左右的高温酸性烟气经过一级喷淋后,形成的温度约为40℃、浓度约为5%的酸性溶液用于提钒过程中的酸浸工序。上述工艺将吸附下液和钠化焙烧产生的酸性气体转变为酸浸工序所需的酸性溶液,既减少了酸性工序中新添加酸的消耗,也处理了烟气,又循环利用了吸附下液。1. The lower liquid adsorbed in the ion resin exchange process is a neutral solution containing certain impurity ions. This solution is used for primary spraying of the acidic flue gas generated by sodium roasting, and the temperature is about 300 ° C. After the acid flue gas is sprayed through the first stage, an acidic solution with a temperature of about 40°C and a concentration of about 5% is formed for the acid leaching process in the vanadium extraction process. The above process converts the acid gas produced by the adsorption lower liquid and sodium roasting into the acidic solution required for the acid leaching process, which not only reduces the consumption of newly added acid in the acidic process, but also treats the flue gas and recycles the adsorption lower liquid .
2、酸性铵盐沉钒工序后产生多聚钒酸铵和沉钒母液,沉钒母液的温度约80℃,其中含有8000~10000mg/L的NH4 +,将该沉钒母液注入氨气吹脱装置中,加石灰乳调节pH值至11以上,吹脱出氨气,使氨气进入氨气喷淋塔中。多聚钒酸铵煅烧制备五氧化二钒时分解产生的氨气,亦进入氨气喷淋塔中,和沉钒母液吹脱产生的氨气一并采用盐酸溶液喷淋,喷淋后形成的氯化铵返回酸性铵盐沉钒工序。2. After the acidic ammonium salt vanadium precipitation process, ammonium polyvanadate and vanadium precipitation mother liquor are produced. The temperature of the vanadium precipitation mother liquor is about 80°C, which contains 8000-10000 mg/L NH 4 + . The vanadium precipitation mother liquor is injected into the ammonia gas blowing In the removal device, add milk of lime to adjust the pH value to above 11, blow off the ammonia gas, and make the ammonia gas enter the ammonia gas spray tower. The ammonia gas produced by the decomposition of ammonium polyvanadate to prepare vanadium pentoxide also enters the ammonia gas spray tower, and is sprayed with hydrochloric acid solution together with the ammonia gas produced by blowing off the vanadium precipitation mother liquor. Ammonium chloride returns to the acidic ammonium salt vanadium precipitation process.
3、酸浸工序产生的V2O5浓度约为100~300mg/L的酸浸液,进行中和处理:先将酸浸液预热至20~45℃,再按物质的量比为nV∶nFe=1∶1~1∶3向该酸浸液中加入FeSO4·7H2O,然后调节至pH=4~6,在45~60℃条件下反应10~30min,最后经固液分离得富钒渣和处理液;富钒渣返回钠化焙烧工序,即相对提高了石煤原矿的品位,又可促进钠化焙烧过程中低价钒的氧化,使酸浸液中的钒以水浸方式回收,显著提高提钒效率;处理液可直接外排。3. The V 2 O 5 concentration produced in the acid leaching process is about 100-300mg/L acid leaching solution, and neutralization treatment: first preheat the acid leaching solution to 20-45°C, and then set the ratio of substances to n V : n Fe =1:1~1:3 Add FeSO 4 ·7H 2 O to the pickling solution, then adjust to pH=4~6, react at 45~60°C for 10~30min, and finally solidify The vanadium-rich slag and treatment liquid are separated from the liquid; the vanadium-rich slag is returned to the sodium roasting process, which not only improves the grade of the raw stone coal ore, but also promotes the oxidation of low-priced vanadium in the process of sodium roasting, so that the vanadium in the acid leaching solution It is recovered by water immersion, which significantly improves the efficiency of vanadium extraction; the treatment liquid can be directly discharged.
因此,本发明将工艺过程中产生的酸性烟气、吸附下液、沉钒母液、氨气以及处理酸浸液得到的富钒渣,经过在线循环处理措施后形成酸性溶液、富钒渣、氯化铵等中间产品,均可回用于提钒工艺过程中。故本发明:Therefore, the present invention forms acidic solution, vanadium-rich slag, and chlorine Intermediate products such as ammonium chloride can be reused in the vanadium extraction process. Therefore the present invention:
1)工艺简单,流程合理、降低了生产成本,提高经济效益;1) The process is simple, the process is reasonable, the production cost is reduced, and the economic benefit is improved;
2)将“三废”转化为工艺中所需的中间产品,真正变废为宝;2) Transform the "three wastes" into intermediate products required in the process, truly turning waste into treasure;
3)环境友好、节能减排效果显著。3) Environmentally friendly, energy-saving and emission-reducing effects are remarkable.
附图说明Description of drawings
图1是本发明的一种工艺流程图。Fig. 1 is a kind of process flow chart of the present invention.
具体实施方式Detailed ways
下面结合附图和具体实施方式对本发明作进一步的描述:Below in conjunction with accompanying drawing and specific embodiment the present invention will be further described:
一种用于石煤提钒工艺的在线循环方法:本方法是在现有的石煤提钒工艺基础上采用在线循环技术。现有的石煤提钒工艺流程如图1中的框图虚线部分所示:对五氧化二钒品位≥0.7%的石煤原矿采用脱碳、钠化焙烧和水浸工序处理后,产生水浸液和水浸渣,钠化焙烧中产生酸性烟气;水浸液进行离子树脂交换后得富钒液和吸附下液,富钒液经酸性铵盐沉钒工序得多聚钒酸铵和沉钒母液,多聚钒酸铵进行脱氨煅烧后制得V2O5产品同时产生氨气;水浸渣进行酸浸处理得酸浸液和渣。An on-line circulation method for vanadium extraction process from stone coal: this method adopts on-line circulation technology on the basis of the existing vanadium extraction process from stone coal. The existing stone coal vanadium extraction process flow is shown in the dotted line of the block diagram in Figure 1: after the stone coal raw ore with a vanadium pentoxide grade ≥ 0.7% is treated by decarburization, sodium roasting and water leaching, water leaching occurs. Liquid and water leaching residue, acidic flue gas is produced during sodium roasting; the water immersion liquid is exchanged with ion resin to obtain vanadium-rich liquid and adsorption lower liquid, and the vanadium-rich liquid is polyammonium vanadate and precipitated by acidic ammonium salt vanadium precipitation process. The vanadium mother liquor and ammonium polyvanadate are deaminated and calcined to obtain V 2 O 5 products and ammonia gas is produced at the same time; the water leaching slag is subjected to acid leaching treatment to obtain acid leaching liquid and slag.
在该工艺的基础上,本实施例采用的工艺流程如图1的框图实线部分所示:On the basis of this process, the process flow adopted in this embodiment is shown in the solid line part of the block diagram in Figure 1:
(1)用离子树脂交换工序中产生的吸附下液对钠化焙烧工序产生的300℃左右的酸性烟气进行一级喷淋,经一级喷淋形成的温度约40℃、浓度约为5%的酸性溶液返回酸浸工序。(1) Use the adsorption liquid produced in the ion resin exchange process to spray the acidic fume at about 300 °C generated in the sodium roasting process, and the temperature formed by the first level spray is about 40 °C and the concentration is about 5 % of the acidic solution is returned to the acid leaching process.
(2)将酸浸工序所得的V2O5浓度为100~300mg/L的酸浸液进行中和处理,即将该酸浸液预热至20~45℃,再按物质的量比为nV∶nFe=1∶1~1∶3向该酸浸液中加入FeSO4·7H2O,然后调节至pH=4~6,在45~60℃条件下反应10~30min,最后经固液分离得富钒渣和处理液;富钒渣返回钠化焙烧工序后经水浸和酸浸工序,所得的酸浸液依次循环,处理液达标外排。(2) Neutralize the acid leaching solution obtained in the acid leaching process with a V 2 O 5 concentration of 100-300 mg/L, that is, preheat the acid leaching solution to 20-45°C, and then set the ratio of substances to n V : n Fe =1:1~1:3 Add FeSO 4 ·7H 2 O to the pickling solution, then adjust to pH=4~6, react at 45~60°C for 10~30min, and finally solidify The vanadium-rich slag and treatment solution are separated from the liquid; the vanadium-rich slag is returned to the sodium roasting process and then undergoes water leaching and acid leaching processes.
(3)酸性铵盐沉钒工序产生的沉钒母液温度约80℃,含有8000~10000mg/L的NH4 +,将该沉钒母液注入氨气吹脱装置中,加石灰乳调节pH值至11以上,经吹脱处理产生氨气和碱性处理液,氨气进入氨气喷淋塔中;多聚钒酸铵在550~600℃下脱氨煅烧成V2O5产品时分解产生的氨气,亦进入氨气喷淋塔中。然后将吹脱处理所得的氨气和脱氨煅烧工序产生的氨气用盐酸溶液喷淋产生氯化铵,氯化铵返回酸性铵盐沉钒工序;碱性处理液对经一级喷淋的酸性烟气进行二级喷淋,二级喷淋后烟气排放,所形成的喷淋下液返回水浸工序。(3) The temperature of the vanadium precipitation mother liquor produced in the acidic ammonium salt vanadium precipitation process is about 80°C and contains 8000-10000 mg/L NH 4 + . The vanadium precipitation mother liquor is injected into the ammonia gas stripping device, and the pH value is adjusted by adding milk of lime to Above 11, ammonia gas and alkaline treatment liquid are produced after stripping treatment, and the ammonia gas enters the ammonia gas spray tower; it is produced by the decomposition of ammonium polyvanadate when it is deaminated and calcined into V 2 O 5 products at 550-600 °C Ammonia also enters the ammonia spray tower. Then the ammonia gas obtained by blowing off and the ammonia gas produced in the deammonization and calcination process are sprayed with hydrochloric acid solution to produce ammonium chloride, and the ammonium chloride is returned to the acidic ammonium salt precipitation process; The acidic flue gas is subjected to secondary spraying, and the flue gas is discharged after the secondary spraying, and the formed spray liquid is returned to the water immersion process.
本具体实施方式根据现有的提钒工艺的自身特点,将所产生的废气、废水,如吸附下液、酸性烟气、氨气、酸浸液和沉钒母液等进行综合利用处理,使之形成工艺过程中能使用的中间产品,如酸性溶液、富钒渣、氯化铵等,循环利用于提钒工艺中。According to the self characteristics of the existing vanadium extraction process, this specific embodiment will comprehensively utilize and treat the waste gas and waste water produced, such as adsorption lower liquid, acid flue gas, ammonia gas, acid leaching solution and vanadium precipitation mother liquor, etc., so that Intermediate products that can be used in the formation process, such as acidic solution, vanadium-rich slag, ammonium chloride, etc., are recycled in the vanadium extraction process.
因此,本方法具有如下特点:1)工艺简单,流程合理、降低了生产成本,提高经济效益;2)将“三废”转化为工艺中所需的中间产品,真正变废为宝;3)环境友好、节能减排效果显著。Therefore, this method has the following characteristics: 1) the process is simple, the process is reasonable, the production cost is reduced, and the economic benefit is improved; 2) the "three wastes" are converted into the intermediate products required in the process, and the waste is truly turned into wealth; 3) the environment Friendly, energy saving and emission reduction effect is remarkable.
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