CN108190924B - A kind of preparation method that reduces magnesium hydroxide chlorine content - Google Patents
A kind of preparation method that reduces magnesium hydroxide chlorine content Download PDFInfo
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- 238000002360 preparation method Methods 0.000 title claims abstract description 26
- UKMPWHAWRCCJFK-UHFFFAOYSA-K [OH-].[Mg+2].[Cl+].[OH-].[OH-] Chemical compound [OH-].[Mg+2].[Cl+].[OH-].[OH-] UKMPWHAWRCCJFK-UHFFFAOYSA-K 0.000 title 1
- VTHJTEIRLNZDEV-UHFFFAOYSA-L magnesium dihydroxide Chemical compound [OH-].[OH-].[Mg+2] VTHJTEIRLNZDEV-UHFFFAOYSA-L 0.000 claims abstract description 145
- 239000000347 magnesium hydroxide Substances 0.000 claims abstract description 145
- 229910001862 magnesium hydroxide Inorganic materials 0.000 claims abstract description 145
- 238000003756 stirring Methods 0.000 claims abstract description 85
- 238000005406 washing Methods 0.000 claims abstract description 67
- 239000000460 chlorine Substances 0.000 claims abstract description 66
- 229910052801 chlorine Inorganic materials 0.000 claims abstract description 66
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 claims abstract description 64
- 238000006298 dechlorination reaction Methods 0.000 claims abstract description 59
- 238000000034 method Methods 0.000 claims abstract description 39
- 238000004140 cleaning Methods 0.000 claims abstract description 37
- 239000012535 impurity Substances 0.000 claims abstract description 12
- TWRXJAOTZQYOKJ-UHFFFAOYSA-L Magnesium chloride Chemical compound [Mg+2].[Cl-].[Cl-] TWRXJAOTZQYOKJ-UHFFFAOYSA-L 0.000 claims description 70
- 238000006243 chemical reaction Methods 0.000 claims description 53
- 239000000243 solution Substances 0.000 claims description 43
- 229910001629 magnesium chloride Inorganic materials 0.000 claims description 33
- 239000007788 liquid Substances 0.000 claims description 29
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 claims description 24
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 22
- 239000013078 crystal Substances 0.000 claims description 20
- 239000011777 magnesium Substances 0.000 claims description 16
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 claims description 12
- CPLXHLVBOLITMK-UHFFFAOYSA-N Magnesium oxide Chemical compound [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 claims description 12
- 229910052749 magnesium Inorganic materials 0.000 claims description 12
- 239000000395 magnesium oxide Substances 0.000 claims description 7
- 239000007853 buffer solution Substances 0.000 claims description 5
- 238000000605 extraction Methods 0.000 claims description 5
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims description 4
- 239000001257 hydrogen Substances 0.000 claims description 4
- 229910052739 hydrogen Inorganic materials 0.000 claims description 4
- 239000006210 lotion Substances 0.000 claims description 3
- 239000002904 solvent Substances 0.000 claims description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 claims description 2
- 239000000908 ammonium hydroxide Substances 0.000 claims 4
- 125000001309 chloro group Chemical group Cl* 0.000 claims 1
- 238000003801 milling Methods 0.000 claims 1
- 230000002411 adverse Effects 0.000 abstract 1
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 46
- 239000000047 product Substances 0.000 description 33
- 230000000694 effects Effects 0.000 description 31
- 238000001914 filtration Methods 0.000 description 28
- 230000032683 aging Effects 0.000 description 26
- 235000011114 ammonium hydroxide Nutrition 0.000 description 26
- 229910021529 ammonia Inorganic materials 0.000 description 24
- 239000007787 solid Substances 0.000 description 22
- 239000000463 material Substances 0.000 description 21
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 20
- 238000004519 manufacturing process Methods 0.000 description 17
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonium chloride Substances [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 description 16
- 239000002245 particle Substances 0.000 description 15
- 238000013019 agitation Methods 0.000 description 14
- 238000000227 grinding Methods 0.000 description 12
- 230000018109 developmental process Effects 0.000 description 9
- 238000002474 experimental method Methods 0.000 description 9
- DHRRIBDTHFBPNG-UHFFFAOYSA-L magnesium dichloride hexahydrate Chemical compound O.O.O.O.O.O.[Mg+2].[Cl-].[Cl-] DHRRIBDTHFBPNG-UHFFFAOYSA-L 0.000 description 9
- 159000000003 magnesium salts Chemical class 0.000 description 9
- 239000002994 raw material Substances 0.000 description 9
- 238000011161 development Methods 0.000 description 8
- 230000035484 reaction time Effects 0.000 description 8
- 239000002002 slurry Substances 0.000 description 8
- 239000012267 brine Substances 0.000 description 7
- HPALAKNZSZLMCH-UHFFFAOYSA-M sodium;chloride;hydrate Chemical compound O.[Na+].[Cl-] HPALAKNZSZLMCH-UHFFFAOYSA-M 0.000 description 7
- 238000011175 product filtration Methods 0.000 description 6
- 230000008901 benefit Effects 0.000 description 5
- 238000011160 research Methods 0.000 description 5
- 150000003839 salts Chemical class 0.000 description 5
- 238000004062 sedimentation Methods 0.000 description 5
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 4
- JLVVSXFLKOJNIY-UHFFFAOYSA-N Magnesium ion Chemical compound [Mg+2] JLVVSXFLKOJNIY-UHFFFAOYSA-N 0.000 description 4
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 4
- 238000002425 crystallisation Methods 0.000 description 4
- 230000008025 crystallization Effects 0.000 description 4
- 230000003247 decreasing effect Effects 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 239000003337 fertilizer Substances 0.000 description 4
- 229910001425 magnesium ion Inorganic materials 0.000 description 4
- 229940072033 potash Drugs 0.000 description 4
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Substances [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 description 4
- 235000015320 potassium carbonate Nutrition 0.000 description 4
- 238000004448 titration Methods 0.000 description 4
- 230000009286 beneficial effect Effects 0.000 description 3
- 230000007423 decrease Effects 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 238000004090 dissolution Methods 0.000 description 3
- 239000012452 mother liquor Substances 0.000 description 3
- 239000002244 precipitate Substances 0.000 description 3
- 238000001556 precipitation Methods 0.000 description 3
- 238000012545 processing Methods 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 238000012360 testing method Methods 0.000 description 3
- CSNNHWWHGAXBCP-UHFFFAOYSA-L Magnesium sulfate Chemical compound [Mg+2].[O-][S+2]([O-])([O-])[O-] CSNNHWWHGAXBCP-UHFFFAOYSA-L 0.000 description 2
- YBOIOUUOHIKJTL-UHFFFAOYSA-L N.[Mg++].[Cl-].[Cl-] Chemical compound N.[Mg++].[Cl-].[Cl-] YBOIOUUOHIKJTL-UHFFFAOYSA-L 0.000 description 2
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 2
- FOGVNFMUZXDMTR-UHFFFAOYSA-N [Mg].Cl Chemical compound [Mg].Cl FOGVNFMUZXDMTR-UHFFFAOYSA-N 0.000 description 2
- 235000019270 ammonium chloride Nutrition 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 230000018044 dehydration Effects 0.000 description 2
- 238000006297 dehydration reaction Methods 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 238000001704 evaporation Methods 0.000 description 2
- 230000008020 evaporation Effects 0.000 description 2
- 239000012065 filter cake Substances 0.000 description 2
- 239000000706 filtrate Substances 0.000 description 2
- 239000003063 flame retardant Substances 0.000 description 2
- 238000009776 industrial production Methods 0.000 description 2
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical compound [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 description 2
- 229910017604 nitric acid Inorganic materials 0.000 description 2
- 238000001953 recrystallisation Methods 0.000 description 2
- 239000013535 sea water Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000012546 transfer Methods 0.000 description 2
- RNFJDJUURJAICM-UHFFFAOYSA-N 2,2,4,4,6,6-hexaphenoxy-1,3,5-triaza-2$l^{5},4$l^{5},6$l^{5}-triphosphacyclohexa-1,3,5-triene Chemical compound N=1P(OC=2C=CC=CC=2)(OC=2C=CC=CC=2)=NP(OC=2C=CC=CC=2)(OC=2C=CC=CC=2)=NP=1(OC=1C=CC=CC=1)OC1=CC=CC=C1 RNFJDJUURJAICM-UHFFFAOYSA-N 0.000 description 1
- 239000010963 304 stainless steel Substances 0.000 description 1
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 description 1
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 229910019440 Mg(OH) Inorganic materials 0.000 description 1
- 229910000589 SAE 304 stainless steel Inorganic materials 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- CQCUILSBDALIQK-UHFFFAOYSA-N [Cl].N.[Mg] Chemical compound [Cl].N.[Mg] CQCUILSBDALIQK-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 239000011449 brick Substances 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 238000006477 desulfuration reaction Methods 0.000 description 1
- 230000023556 desulfurization Effects 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 239000012153 distilled water Substances 0.000 description 1
- 229910000514 dolomite Inorganic materials 0.000 description 1
- 239000010459 dolomite Substances 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 239000003546 flue gas Substances 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 239000001095 magnesium carbonate Substances 0.000 description 1
- 235000014380 magnesium carbonate Nutrition 0.000 description 1
- ZLNQQNXFFQJAID-UHFFFAOYSA-L magnesium carbonate Chemical compound [Mg+2].[O-]C([O-])=O ZLNQQNXFFQJAID-UHFFFAOYSA-L 0.000 description 1
- 229910000021 magnesium carbonate Inorganic materials 0.000 description 1
- 229910052943 magnesium sulfate Inorganic materials 0.000 description 1
- 235000019341 magnesium sulphate Nutrition 0.000 description 1
- 235000010755 mineral Nutrition 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 231100000252 nontoxic Toxicity 0.000 description 1
- 230000003000 nontoxic effect Effects 0.000 description 1
- XAEFZNCEHLXOMS-UHFFFAOYSA-M potassium benzoate Chemical compound [K+].[O-]C(=O)C1=CC=CC=C1 XAEFZNCEHLXOMS-UHFFFAOYSA-M 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 230000001376 precipitating effect Effects 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 238000013341 scale-up Methods 0.000 description 1
- 229910052709 silver Inorganic materials 0.000 description 1
- 239000004332 silver Substances 0.000 description 1
- 238000000967 suction filtration Methods 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 230000009967 tasteless effect Effects 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F5/00—Compounds of magnesium
- C01F5/14—Magnesium hydroxide
- C01F5/145—Purification
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F5/00—Compounds of magnesium
- C01F5/14—Magnesium hydroxide
- C01F5/20—Magnesium hydroxide by precipitation from solutions of magnesium salts with ammonia
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2006/00—Physical properties of inorganic compounds
- C01P2006/80—Compositional purity
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Inorganic Chemistry (AREA)
- Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
Abstract
Description
技术领域technical field
本发明属于氢氧化镁制备领域,具体涉及一种低氯根高纯氢氧化镁的制备工艺The invention belongs to the field of magnesium hydroxide preparation, in particular to a preparation process of low-chloride high-purity magnesium hydroxide
背景技术Background technique
我国盐湖资源也非常的丰富,中有1km2以上的盐湖面积有731个,这些总面积加起来达到了23784km2.当中资源丰富的要属青海柴达木盆地,该地区盐湖中钾盐储量约为40.4亿吨,镁盐储量约为48.15亿吨,其中65.3%的镁盐为氯化镁,34.7%为硫酸镁。国外的盐湖资源主要有美国的西尔斯盐湖和大盐湖、智利的阿塔卡玛盐湖、以色列和约旦附近的死海等。随着科技的不断进步,国外对盐湖资源开发已经不再满足于生产单一的化工产品,而是向着多元化综合利用。China's salt lake resources are also very rich. Among them, there are 731 salt lakes with an area of more than 1km 2 , and the total area of these lakes has reached 23,784km 2 . Among them, the Qaidam Basin in Qinghai is rich in resources, and the potassium salt reserves in the salt lakes in this area are about The magnesium salt reserves are about 4.815 billion tons, of which 65.3% are magnesium chloride and 34.7% are magnesium sulfate. Foreign salt lake resources mainly include Sears Salt Lake and Great Salt Lake in the United States, Atacama Salt Lake in Chile, and the Dead Sea near Israel and Jordan. With the continuous advancement of science and technology, the development of salt lake resources in foreign countries is no longer satisfied with the production of a single chemical product, but is moving towards diversified and comprehensive utilization.
青海察尔汗盐湖是我国重要的钾肥生产基地,在钾肥生产过程中要产生大量富集了氯化镁的老卤,利用当地得天独厚的气候条件,很容易通过盐田蒸发、浓缩结晶得到价廉质优的水氯镁石(MgCl2.6H2O)固体矿,是一种十分重要的盐湖镁资源。Qinghai Chaerhan Salt Lake is an important potash fertilizer production base in China. In the process of potash fertilizer production, a large amount of old brine enriched with magnesium chloride is produced. Taking advantage of the unique local climate conditions, it is easy to obtain low-cost and high-quality brine through salt field evaporation, concentration and crystallization. Bischofite (MgCl 2 .6H 2 O) solid ore is a very important salt lake magnesium resource.
我国盐湖镁资源十分丰富,盐湖镁资源的生产开发主要是盐湖钾肥副产物水氯镁石的生产开发,目前尚处于起步阶段,还没有建立起一套完整的水氯镁石资源综合开发利用工业体系。my country's salt lake magnesium resources are very rich, and the production and development of salt lake magnesium resources is mainly the production and development of bischofite, a by-product of salt lake potash fertilizer. system.
我国盐湖镁资源的开发主要是察尔汗盐湖水氯镁石资源的开发,它是在钾肥生产过程中排放的富集了镁盐的老卤,利用当地得天独厚的自然气候条件,通过盐田蒸发浓缩结晶得到的一种二次镁资源固体矿物,具有品位高、杂质含量低、资源量大等特点。柴达木地区具有丰富的水电、石油等资源,为镁盐生产工厂提供充足的保障。加上目前建设中的“西气东输”工程为镁加工产业不断升级提供了最有力的支持。同时国家西部大开发相关国家政策的积极支持,土地便宜,市场更加规范,制度更加齐全,因此盐湖镁资源的开发具有显著地优势。The development of magnesium resources in salt lakes in my country is mainly the development of bichoromagnesite resources in Chaerhan Salt Lake. It is an old brine rich in magnesium salts discharged during the production of potash fertilizers. It is concentrated by evaporation in salt fields by utilizing the unique local natural climate conditions. A secondary magnesium resource solid mineral obtained by crystallization, which has the characteristics of high grade, low impurity content, and large resource volume. The Qaidam area is rich in hydropower, oil and other resources, which provide sufficient guarantee for the magnesium salt production plant. In addition, the "West-to-East Gas Pipeline" project currently under construction provides the most powerful support for the continuous upgrading of the magnesium processing industry. At the same time, with the active support of national policies related to the western development of the country, the land is cheap, the market is more standardized, and the system is more complete, so the development of salt lake magnesium resources has significant advantages.
氢氧化镁,白色,性状为无色晶体,属六方晶系,没有味道,且无毒和腐蚀性。高纯氢氧化镁是指氢氧化镁含量大于99%的产品,分解温度高,吸收热量大,是一种重要的无机化工材料,应用广泛,主要是在阻燃剂、烟气脱硫、废水处理等方面。Magnesium hydroxide, white, colorless crystal, belongs to hexagonal crystal system, tasteless, non-toxic and corrosive. High-purity magnesium hydroxide refers to products with a magnesium hydroxide content greater than 99%. It has a high decomposition temperature and a large heat absorption. It is an important inorganic chemical material and is widely used, mainly in flame retardants, flue gas desulfurization, wastewater treatment, etc. .
高纯氢氧化镁最早是“镁砖”工厂用盐酸对镁石进行富选,并将其粒度磨碎到0.5mm以下,再溶解在浓度为12.5-20%的盐酸中,经过除杂处理,沉淀得到高纯氢氧化镁。在世界上,美国、日本、和英国最早获得制备高纯镁砂的成熟技术。之后,意大利,墨西哥,挪威和希腊等国相继制备出高纯氢氧化镁。High-purity magnesium hydroxide was first enriched with hydrochloric acid in the "magnesia brick" factory, and its particle size was ground to less than 0.5mm, and then dissolved in hydrochloric acid with a concentration of 12.5-20%, after impurity removal treatment, and precipitation. High-purity magnesium hydroxide. In the world, the United States, Japan, and the United Kingdom were the first to obtain mature technologies for preparing high-purity magnesia. After that, countries such as Italy, Mexico, Norway and Greece successively prepared high-purity magnesium hydroxide.
西欧地区大都是海水法,其中的沉降速度和洗涤效率是关注点。研究表明白云石灰作沉淀剂和海水反应造出氢氧化镁最佳条件,在使用A-130絮凝剂,其沉降速度大大加强,装置能力也相应提高。Seawater method is mostly used in Western Europe, where the sedimentation speed and washing efficiency are the focus. Studies have shown that dolomite lime as a precipitant reacts with seawater to create the best conditions for magnesium hydroxide. When A-130 flocculant is used, the settling speed is greatly enhanced, and the device capacity is also improved accordingly.
中国高纯氢氧化镁的生产规模小,设备老化,不能满足市场的需求。近年来高纯镁盐产品科研成果不断涌出,大多的都投入到市场,但就算这些也远远不够国内市场的需求,出口更是少之又少,由于生产量少,镁盐企业经济也提高不了。所以生产功能化镁盐产品是镁盐发展的必经之路。The production scale of China's high-purity magnesium hydroxide is small and the equipment is aging, which cannot meet the market demand. In recent years, scientific research achievements of high-purity magnesium salt products have been continuously poured out, and most of them have been put into the market, but even these are far from enough to meet the needs of the domestic market, and exports are even less. Due to the small production volume, the economy of magnesium salt enterprises cannot be improved. . Therefore, the production of functional magnesium salt products is the only way for the development of magnesium salt.
总体来说,中国镁盐生产仍处于初级阶段,产品单一,附加值不够,功能性不强。例如阻燃剂氢氧化镁,医药用氢氧化镁等,国内需求一大就只能进口。这种局面早已引起国内众多院校、科研院及镁盐企业注意,现在要做的就是积极投入人力、物力开发新技术、新工艺来满足国内及国外的需求,提高产品档次,占领国际市场。Generally speaking, the production of magnesium salt in China is still in its infancy, with a single product, insufficient added value, and weak functionality. For example, flame retardant magnesium hydroxide, magnesium hydroxide for medicine, etc., can only be imported if the domestic demand is large. This situation has already attracted the attention of many domestic universities, scientific research institutes and magnesium salt enterprises. What we need to do now is to actively invest in manpower and material resources to develop new technologies and new processes to meet domestic and foreign needs, improve product grades, and occupy the international market.
现有技术中,氢氧化镁的氯含量较高,但本领域并未关注氢氧化镁的氯含量。In the prior art, the chlorine content of magnesium hydroxide is relatively high, but the chlorine content of magnesium hydroxide has not been paid attention to in this field.
发明内容Contents of the invention
本发明首次聚焦氢氧化镁的氯含量的技术问题,提供了一种降低氢氧化镁氯含量的制备方法,通过本发明独创地多级逆流搅拌洗涤,旨在明显降低得到的氢氧化镁的氯含量。The present invention focuses on the technical problem of the chlorine content of magnesium hydroxide for the first time, and provides a preparation method for reducing the chlorine content of magnesium hydroxide. Through the original multi-stage countercurrent stirring washing of the present invention, the chlorine content of the obtained magnesium hydroxide is obviously reduced. content.
一种降低氢氧化镁氯含量的制备方法,将含有氯杂质的待处理氢氧化镁进行单级的搅拌洗涤;或者经除氯系统的多级逆流搅拌洗涤,得除氯氢氧化镁;A preparation method for reducing the chlorine content of magnesium hydroxide. The magnesium hydroxide containing chlorine impurities is subjected to single-stage agitation and washing; or multi-stage countercurrent agitation and washing of a chlorine removal system to obtain chlorine-removing magnesium hydroxide;
所述的除氯系统包括多级除氯单元;各除氯单元均设置有氢氧化镁的入口和出口、清洗液的出口和入口;各除氯单元通过氢氧化镁的出口和入口彼此串联连接,其中,第一级除氯单元的氢氧化镁入口为待处理的氢氧化镁的进入口,最后一级除氯单元的氢氧化镁出口为除氯后的氢氧化镁的采出口;The dechlorination system includes multi-stage dechlorination units; each dechlorination unit is provided with an inlet and an outlet of magnesium hydroxide, and an outlet and an inlet of cleaning liquid; each dechlorination unit is connected in series through the outlet and inlet of magnesium hydroxide , wherein, the magnesium hydroxide inlet of the first stage dechlorination unit is the inlet of magnesium hydroxide to be treated, and the magnesium hydroxide outlet of the last stage dechlorination unit is the recovery outlet of magnesium hydroxide after dechlorination;
第一级的除氯单元的清洗液出口为清洗后的洗涤液的采出口,最后一级的除氯单元的清液液入口为清水的进入口;其他各级的除氯单元的清洗液的出口与各自相串联的上一级除氯单元的清洗液入口连接;The outlet of the cleaning solution of the first-level dechlorination unit is the extraction outlet of the cleaned washing solution, and the clear liquid inlet of the last-level dechlorination unit is the inlet of clean water; the cleaning solution of the dechlorination units of other levels The outlets are connected to the cleaning liquid inlets of the respective upper-stage dechlorination units connected in series;
氢氧化镁由第一级除氯单元的氢氧化镁入口进入所述的除氯系统,清水由最后一级的料液入口进入除氯系统;氢氧化镁由第一级除氯单元向最后一级除氯单元运动;清洗液由最后一级向第一级除氯单元运动,氢氧化镁和清液液在各除氯单元中搅拌洗涤,搅拌洗涤后的氢氧化镁由最后一级除氯单元的氢氧化镁出口采出,清洗液由第一级除氯单元的清洗液出口采出。Magnesium hydroxide enters the dechlorination system from the magnesium hydroxide inlet of the first-stage dechlorination unit, and clear water enters the dechlorination system from the feed liquid inlet of the last stage; Stage dechlorination unit movement; cleaning liquid moves from the last stage to the first stage dechlorination unit, magnesium hydroxide and clear liquid are stirred and washed in each dechlorination unit, and the stirred and washed magnesium hydroxide is dechlorinated by the last stage The magnesium hydroxide outlet of the unit is extracted, and the cleaning liquid is extracted from the cleaning liquid outlet of the first-stage dechlorination unit.
首先,本发明首次提出清洗氢氧化镁中的氯含量的方法。此外,本发明人独创性地提供了一种可降低氢氧化镁的氯含量的制备方法,即通过本发明所述的除氯系统,对所述的氢氧化镁进行多级逆流搅拌洗涤,可高效脱除氢氧化镁中的氯含量。First of all, the present invention proposes a method for cleaning the chlorine content in magnesium hydroxide for the first time. In addition, the inventors of the present invention provide a preparation method that can reduce the chlorine content of magnesium hydroxide, that is, through the chlorine removal system described in the present invention, the magnesium hydroxide is subjected to multi-stage countercurrent stirring and washing, which can Efficiently remove chlorine content in magnesium hydroxide.
本发明所述的处理系统,各除氯单元中,所述的氢氧化镁的出口优选设置在除氯单元的下部;所述的氢氧化镁的入口优选设置在除氯单元的顶部。所述的清洗液的入口和出口均优选设置在除氯单元的上部,所述的清洗液的出口和入口设置在除氯单元上部的相对位置。In the treatment system of the present invention, in each chlorine removal unit, the outlet of the magnesium hydroxide is preferably arranged at the lower part of the chlorine removal unit; the inlet of the magnesium hydroxide is preferably arranged at the top of the chlorine removal unit. Both the inlet and the outlet of the cleaning solution are preferably arranged on the upper part of the chlorine removal unit, and the outlet and inlet of the cleaning solution are arranged at opposite positions on the upper part of the chlorine removal unit.
本发明所述的各除氯单元,还设置有搅拌装置、将氢氧化镁转移至下一级除氯单元的转移装置,以及将清洗液向上一级除氯单元转移的转送装置。Each chlorine removal unit described in the present invention is also provided with a stirring device, a transfer device for transferring magnesium hydroxide to the next-stage chlorine removal unit, and a transfer device for transferring the cleaning liquid to the upper-stage chlorine removal unit.
待处理的氢氧化镁由第一级除氯单元进入除氯系统,清水由最后一级的清洗液入口进入系统;氢氧化镁先在第一级除氯单元中和第二级除氯单元转移过来的清洗液进行搅拌洗涤,随后将第一级搅拌洗涤后的氢氧化镁连续或者间断地转移至第二级除氯单元,与第三级转移过来的清洗液进行搅拌洗涤,如此在所述的处理系统中进行多级逆流搅拌洗涤;直至由最后一级的氢氧化镁的出口采出。The magnesium hydroxide to be treated enters the dechlorination system from the first-stage dechlorination unit, and the clean water enters the system from the last-stage cleaning liquid inlet; the magnesium hydroxide is first transferred in the first-stage dechlorination unit and the second-stage dechlorination unit The cleaning liquid that comes over is stirred and washed, and then the magnesium hydroxide after the first-stage stirring and washing is continuously or intermittently transferred to the second-stage dechlorination unit, and the cleaning liquid transferred from the third stage is stirred and washed. Multi-stage countercurrent stirring and washing is carried out in the treatment system; until it is extracted from the outlet of the last stage of magnesium hydroxide.
本发明人研究发现,配合本发明独创性地采用本发明所述的除氯系统进行所述的多级逆流搅拌洗涤,控制合适的搅拌洗涤参数,可进一步提升除氯效果。The inventors of the present invention have found that the multi-stage countercurrent agitation and washing with the inventive dechlorination system of the present invention can further improve the dechlorination effect by controlling appropriate agitation and washing parameters.
研究发现,对待处理的氢氧化镁的粒径(堆积密度)、洗涤过程的搅拌转速、液固比、洗涤温度等参数进行调控,可进一步提升除氯效果。Studies have found that adjusting parameters such as the particle size (bulk density) of the magnesium hydroxide to be treated, the stirring speed of the washing process, the liquid-solid ratio, and the washing temperature can further improve the chlorine removal effect.
作为优选,所述的待处理氢氧化镁的堆积密度0.8-2.0g/ml;进一步优选为1.2-1.5g/ml。研究发现,控制在合适的堆积密度范围内,可进一步提升除氯效果,还有助于进一步利于本发明所述的多级逆流搅拌洗涤,有助于提升制备效果。Preferably, the bulk density of the magnesium hydroxide to be treated is 0.8-2.0 g/ml; more preferably 1.2-1.5 g/ml. Studies have found that controlling the bulk density within an appropriate range can further improve the chlorine removal effect, and also help to further benefit the multi-stage countercurrent stirring washing described in the present invention, and help to improve the preparation effect.
实际生产中,可预先将所述的待处理的氢氧化镁进行研磨处理,可通过研磨时间,控制得到的待处理的氢氧化镁的堆积密度在所优选的范围内。作为优选,所述的待处理氢氧化镁在洗涤前预先进行研磨处理,研磨时间为5~20min,进一步优选为5~10min。In actual production, the magnesium hydroxide to be treated can be ground in advance, and the bulk density of the magnesium hydroxide to be treated can be controlled within the preferred range through the grinding time. Preferably, the magnesium hydroxide to be treated is ground before washing, and the grinding time is 5-20 minutes, more preferably 5-10 minutes.
多级逆流搅拌洗涤过程中,在各除氯单元中,由上一级转移过来的氢氧化镁与由下一级转移过来的清洗液进行搅拌洗涤;控制合适的固液比和搅拌转速以及在各除氯单元停留的时间,可协同提升氯的去除洗涤效果。In the process of multi-stage countercurrent stirring and washing, in each dechlorination unit, the magnesium hydroxide transferred from the upper stage and the cleaning liquid transferred from the next stage are stirred and washed; the appropriate solid-liquid ratio and stirring speed are controlled and the The residence time of each dechlorination unit can synergistically improve the chlorine removal and washing effect.
作为优选,搅拌洗涤过程中,氢氧化镁和清洗液的液固重量比为1~5∶1。液体部分的比例较大时,可有助于提升除氯效果,但较高的液体占比,制备效果低,且过滤速度有所下降。Preferably, during the stirring and washing process, the liquid-solid weight ratio of the magnesium hydroxide to the cleaning solution is 1-5:1. When the proportion of the liquid part is larger, it can help to improve the chlorine removal effect, but the higher the liquid proportion, the lower the preparation effect and the lower the filtration speed.
进一步优选,搅拌洗涤过程中,氢氧化镁和清洗液的液固重量比比为2~4∶1。在该优选的液固比下,除氯效果好,且制备效率高。Further preferably, during the stirring and washing process, the liquid-solid weight ratio of the magnesium hydroxide to the cleaning solution is 2-4:1. Under the preferred liquid-solid ratio, the chlorine removal effect is good, and the production efficiency is high.
作为优选,搅拌洗涤过程的温度为50~90℃。研究发现,范围温度较高时,可进一步提升除氯效果,较低和较高的洗涤温度下的除氯效果有所下降。Preferably, the temperature of the stirring and washing process is 50-90°C. The study found that the dechlorination effect can be further improved when the range temperature is higher, and the dechlorination effect is decreased at lower and higher washing temperatures.
进一步优选,搅拌洗涤过程的温度为60~80℃。在该优选的温度下,除氯效果理想,且制备效率高,过滤速度快,利于工业大规模生产。More preferably, the temperature of the stirring and washing process is 60-80°C. At this preferred temperature, the chlorine removal effect is ideal, the preparation efficiency is high, and the filtration speed is fast, which is beneficial to large-scale industrial production.
作为优选,搅拌洗涤过程中,搅拌转速不低于50r/min。搅拌较快时,氯的脱除效果较好,但搅拌过快,不利于工业生产实施,且过滤速度慢。Preferably, during the stirring and washing process, the stirring speed is not lower than 50r/min. When the stirring is faster, the removal effect of chlorine is better, but if the stirring is too fast, it is not conducive to the implementation of industrial production, and the filtration speed is slow.
进一步优选,搅拌洗涤过程中,搅拌转速为50~250r/min;最优选为100~250r/min。在该优选的搅拌转速下,生产效率高,且除氯效果更理想。More preferably, during the stirring and washing process, the stirring speed is 50-250 r/min; most preferably 100-250 r/min. Under the preferred stirring speed, the production efficiency is high, and the chlorine removal effect is more ideal.
作为优选,在所述的搅拌洗涤温度、固液比、搅拌转速下,优选的搅拌洗涤时间大于10min。搅拌洗涤时间延长,除氯效果进一步提升,但过滤速度有所下降。As a preference, under the agitation washing temperature, solid-to-liquid ratio, and agitation speed, the preferred agitation washing time is greater than 10 min. The longer the stirring and washing time, the further improved the dechlorination effect, but the filtration speed decreased.
进一步优选,搅拌洗涤时间大于或等于10min,为10~60min,进一步优选为30~60min。在该优选的搅拌洗涤时间下,除氯效果、生产效果均更理想。More preferably, the stirring and washing time is greater than or equal to 10 minutes, and is 10-60 minutes, more preferably 30-60 minutes. Under the preferred stirring and washing time, the dechlorination effect and production effect are more ideal.
本发明方法可适用于任意Cl-含量的氢氧化镁的处理;优选适用于氯杂质含量为0.6-0.9%的氢氧化镁的处理。The method of the present invention is applicable to the treatment of magnesium hydroxide with any Cl- content; preferably suitable for the treatment of magnesium hydroxide with chlorine impurity content of 0.6-0.9%.
本发明中,单级洗涤过程的清洗液为清水。In the present invention, the cleaning solution in the single-stage washing process is clear water.
在所述的单级洗涤的参数下,可以将氢氧化镁的氯含量降至0.3%左右,但清洗效果不稳定。本发明中,采用本发明优选的多级逆流清洗方法,氯的清洗效果更好,且可以实现连续化清洗,相对来说,使用的清洗液量更省。Under the parameters of the single-stage washing, the chlorine content of magnesium hydroxide can be reduced to about 0.3%, but the cleaning effect is not stable. In the present invention, by adopting the preferred multi-stage countercurrent cleaning method of the present invention, the cleaning effect of chlorine is better, and continuous cleaning can be realized. Relatively speaking, the amount of cleaning liquid used is less.
作为优选,所述的除氯系统中,所述的除氯单元的串联级数为2~10级;优选为3~6级。在所述的多级洗涤条件下,在任何氯含量的氢氧化镁下,均可获得氯含量在0.2%左右及以下。Preferably, in the chlorine removal system, the number of serial stages of the chlorine removal unit is 2-10; preferably 3-6. Under the above multi-stage washing conditions, under magnesium hydroxide with any chlorine content, the chlorine content can be obtained at about 0.2% or below.
本发明所述的待处理氢氧化镁可为外购的现有产品,也可为采用现有技术合成的产品。The magnesium hydroxide to be treated in the present invention can be an existing product purchased from outside, or a product synthesized by using the prior art.
本发明中,所述的待处理氢氧化镁优选采用氨法得到。In the present invention, the magnesium hydroxide to be treated is preferably obtained by ammonia method.
作为优选,所述的待处理氢氧化镁的制备过程为:将氯化镁溶液和氨水一起滴加到加有氢氧化镁晶种的氨水-氯化铵缓冲体系中,搅拌反应,制得待处理氢氧化镁。As a preference, the preparation process of the magnesium hydroxide to be treated is as follows: adding the magnesium chloride solution and ammonia water dropwise to the ammonia water-ammonium chloride buffer system added with magnesium hydroxide seeds, stirring and reacting to obtain the hydrogen to be treated magnesium oxide.
本发明人研究发现,对待处理的氢氧化镁的制备过程的参数,例如氯化镁溶液、氨水的浓度,滴加方式、滴加比例、晶种以及晶种的投加量、搅拌反应的搅拌转速、反应温度等参数进行合理控制,制得具有更利于本发明多级逆流搅拌洗涤的待处理氢氧化镁,配合本发明所述的多级逆流搅拌洗涤,可进一步降低除氯效果,且提升过滤性能,提升制备效果,使其更适用于工业放大化生产。The present inventor's research has found that the parameters of the preparation process of the magnesium hydroxide to be treated, such as the concentration of magnesium chloride solution, ammoniacal liquor, dropwise addition mode, dropwise addition ratio, crystal seed and the dosage of crystal seed, the stirring speed of stirring reaction, Parameters such as the reaction temperature are reasonably controlled, and the magnesium hydroxide to be treated that is more conducive to the multi-stage countercurrent agitation and washing of the present invention is obtained. Cooperating with the multi-stage counter-current agitation and washing of the present invention can further reduce the chlorine removal effect and improve the filtration performance. , improve the preparation effect and make it more suitable for industrial scale-up production.
所述的氯化镁溶液可为水氯镁石溶解后经常规的除杂工艺除杂后得到的溶液,也可为采用分析级氯化镁溶剂在水中得到的溶液。The magnesium chloride solution may be a solution obtained by dissolving bischofite and removing impurities through a conventional impurity removal process, or may be a solution obtained in water by using an analytical grade magnesium chloride solvent.
作为优选,所述的氯化镁溶液的摩尔浓度为1~4moL/L;进一步优选为2~3moL/L。Preferably, the molar concentration of the magnesium chloride solution is 1-4 moL/L; more preferably 2-3 moL/L.
作为优选,氨水的浓度为10~13.3mol/L。Preferably, the concentration of ammonia water is 10-13.3 mol/L.
作为优选,氯化镁溶液与氨水的投加比例(摩尔比)为1∶2-1∶8;进一步优选为1∶2-1∶5;更进一步优选为1∶2.2~2.8。Preferably, the dosing ratio (molar ratio) of magnesium chloride solution to ammonia water is 1:2-1:8; more preferably 1:2-1:5; still more preferably 1:2.2-2.8.
本发明中,将所述的氯化镁溶液、氨水同时滴加至反应体系中,通过控制搅拌转速和反应温度,配合本发明所述的多级逆流搅拌洗涤,可进一步提升除氯效果。In the present invention, the magnesium chloride solution and ammonia water are added dropwise to the reaction system at the same time, and the dechlorination effect can be further improved by controlling the stirring speed and reaction temperature, combined with the multi-stage countercurrent stirring and washing described in the present invention.
本发明所述的氨水-氯化铵缓冲体系为氨水和氯化铵配比的pH=9的缓冲溶液。The ammonia water-ammonium chloride buffer system of the present invention is a buffer solution with a pH=9 ratio of ammonia water and ammonium chloride.
作为优选,所述的氢氧化镁晶种添加量为产物的10~40%。Preferably, the added amount of the magnesium hydroxide seed crystal is 10-40% of the product.
研究发现,晶种的加入量可影响产物的转化率、影响产物的过滤速度和堆积密度。作为优选,所述的所述的氢氧化镁晶种添加量为20~30%。在该优选的晶种添加量下,产物的转化率高、过滤效率高,得到的产物配合本发明所述的搅拌洗涤方法,可进一步提升除氯效果。The study found that the amount of seed crystals added can affect the conversion rate of the product, and affect the filtration speed and bulk density of the product. Preferably, the added amount of the magnesium hydroxide seed crystal is 20-30%. Under the preferred addition amount of seed crystals, the conversion rate of the product is high and the filtration efficiency is high, and the obtained product can further improve the dechlorination effect by using the stirring and washing method described in the present invention.
作为优选,搅拌反应的搅拌转速不低于50r/min;进一步优选50~150r/min。搅拌速度增大,过滤性能增强,但是只要搅拌起来使溶液分散,在增大搅拌速度,过滤性能就变化不大,说明搅拌速度起到使氢氯化镁溶液的分散而降低瞬时饱和度,生成沉淀的粒度增大。Preferably, the stirring speed of the stirring reaction is not lower than 50r/min; more preferably 50-150r/min. When the stirring speed is increased, the filtration performance is enhanced, but as long as the solution is stirred to disperse, the filtration performance does not change much when the stirring speed is increased, indicating that the stirring speed plays a role in dispersing the magnesium hydrochloride solution to reduce the instantaneous saturation and generate precipitation. The particle size increases.
进一步优选,搅拌反应的搅拌转速为100~150r/min。More preferably, the stirring speed of the stirring reaction is 100-150 r/min.
作为优选,所述的搅拌反应过程的温度为40~80℃。Preferably, the temperature of the stirring reaction process is 40-80°C.
作为优选,搅拌反应时间为10~40min,30mins时;粒最大。Preferably, the stirring reaction time is 10 to 40 minutes, and at 30 minutes, the particles are the largest.
本发明的降低氯含量的方法,特别适用于采用氯镁氨法制得的氢氧化镁的除氯。在处理氯镁氨法制得的氢氧化镁的过程中,采用本发明的多级逆流清洗的工艺相较于单级洗涤,优势更明显,例如,可以将氯含量稳定在0.2%左右,除氯效果更好,且可以良好去除氢氧化镁中的氨。The method for reducing the chlorine content of the present invention is particularly suitable for dechlorination of magnesium hydroxide produced by the magnesium chloride ammonia method. In the process of processing magnesium hydroxide produced by the magnesium chloride ammonia method, the multi-stage countercurrent cleaning process of the present invention has more obvious advantages than single-stage washing. For example, the chlorine content can be stabilized at about 0.2%, and chlorine removal The effect is better, and the ammonia in magnesium hydroxide can be removed well.
有益效果Beneficial effect
1、本发明独创性地采用多级逆流搅拌洗涤方式,可有助于明显提升氯的脱除效果。1. The invention uniquely adopts the multi-stage countercurrent stirring washing method, which can help to significantly improve the chlorine removal effect.
2、本发明采用搅拌洗涤方式,通过研究陈化温度、陈化时间、液固比、搅拌速度等因素,并创造性的发明研磨、多段逆流搅拌洗涤陈化等技术降低产品中氯根含量,以确定降低氯根的最佳工艺条件。2. The present invention adopts the method of agitation and washing, by studying factors such as aging temperature, aging time, liquid-solid ratio, stirring speed, etc., and creatively inventing technologies such as grinding, multi-stage countercurrent agitation, washing and aging to reduce the chloride content in the product, so as to Determine the optimal process conditions for reducing chloride.
3、本发明所述的待处理氢氧化镁可由水氯镁石为原料,先用纯水溶解、过滤及净化除杂得到高浓度的卤水,然后以氨水为沉淀剂,采用卤水-氨沉淀法制取氢氧化镁,研究反应温度、反应时间、搅拌速度及加料方式和加料速度等因素对氢氧化镁粒度及过滤搅拌洗涤性能的影响,3. The magnesium hydroxide to be treated according to the present invention can be made of bischofite as a raw material, first dissolved with pure water, filtered and purified to remove impurities to obtain high-concentration brine, and then use ammonia as a precipitating agent and adopt the brine-ammonia precipitation method Get magnesium hydroxide, study the influence of factors such as reaction temperature, reaction time, stirring speed and feeding mode and feeding speed on magnesium hydroxide particle size and filter agitation washing performance,
4、利用本发明方法清洗氯镁氨法制得的氢氧化镁,多级逆流洗涤除可使除氯效果控制在0.2%及以下,还可明显除氨,维持得到的氢氧化镁的粒度。4. Utilize the inventive method to clean the magnesium hydroxide that chlorine magnesium ammonia method makes, multistage countercurrent washing can make dechlorination effect be controlled at 0.2% and below, also can obviously remove ammonia, maintain the granularity of the magnesium hydroxide that obtains.
附图说明:Description of drawings:
图1为氢氧化镁的制备流程示意图;Fig. 1 is the preparation flow schematic diagram of magnesium hydroxide;
图2为多级搅拌逆流搅拌洗涤示意图。Fig. 2 is a schematic diagram of washing with multi-stage agitation and countercurrent agitation.
具体实施方式Detailed ways
菱镁矿轻烧粉工业级甘肃金茂矿业发展有限公司提供。Gansu Jinmao Mining Development Co., Ltd. provides industrial grade lightly burned magnesite powder.
本发明所述的氯化镁溶液,可采用以下方法得到:称取500g左右的水氯镁石,加入100ml蒸馏水溶解,放置过夜,真空抽滤,除去掉不溶物质,将不溶物质放入下一次溶解烧杯中,以免造成浪费,配置好的饱和氯化镁溶液放入大烧杯中备用。测定氯化镁浓度为4.81mol/l。The magnesium chloride solution of the present invention can be obtained by the following method: take about 500g of bischofite, add 100ml of distilled water to dissolve, leave it overnight, vacuum filter, remove the insoluble matter, and put the insoluble matter into the next dissolution beaker In order to avoid waste, put the prepared saturated magnesium chloride solution into a large beaker for later use. The magnesium chloride concentration was determined to be 4.81 mol/l.
实验得到的饱和氯化镁溶液加热到120℃,放到室温下慢慢冷却后重结晶得到水氯镁石,两者做出来的饱和氯化镁中元素的含量,结果如表1:The saturated magnesium chloride solution obtained in the experiment was heated to 120°C, cooled slowly at room temperature, and then recrystallized to obtain bischofite. The content of elements in the saturated magnesium chloride produced by the two is shown in Table 1:
表1一次结晶与重结晶溶解后饱和氯化镁中元素的对比Table 1 The comparison of elements in saturated magnesium chloride after primary crystallization and recrystallization dissolution
由表1可知,重结晶得到的水氯镁石杂质元素明显比一次结晶的少,纯度达到了99%以上。所以为了减少原料水氯镁石中的杂质,选择重结晶后的水氯镁石做我后续实验的原料。It can be known from Table 1 that the bischofite obtained by recrystallization has significantly less impurity elements than that obtained by primary crystallization, and the purity has reached more than 99%. Therefore, in order to reduce the impurities in the raw material bischofite, I chose the recrystallized bischofite as the raw material for my follow-up experiments.
本实验是氯化镁溶液和氨水一起滴加到加有氢氧化镁晶种的氨水-氯化铵缓冲体系中,控制一定的反应温度和滴加速度,经过反应制得氢氧化镁。最后洗涤、过滤、干燥得到产物。In this experiment, magnesium chloride solution and ammonia water are added dropwise to the ammonia water-ammonium chloride buffer system added with magnesium hydroxide seeds, and the reaction temperature and dropping speed are controlled to obtain magnesium hydroxide through reaction. Finally, the product was obtained by washing, filtering and drying.
本发明中,实施例1~7筛查氢氧化镁的制备过程的参数:实施例1~7中,除特别声明外,采用的氯化镁的摩尔浓度均为上述制得的4.81mol/1;氨水浓度13.33mol/1。Among the present invention, embodiment 1~7 screens the parameter of the preparation process of magnesium hydroxide: Among embodiment 1~7, except special statement, the molar concentration of the magnesium chloride that adopts is all above-mentioned 4.81mol/1 that makes; The concentration is 13.33mol/1.
实施例1Example 1
分别将不同浓度的MgCl2溶液进行单因素试验,同时加入MgCl2和氨水溶液(13.33mol/l),氯化镁和氨水反应滴加速度都为10ml/min、搅拌速率为150r/min、反应温度80℃、物料加完后继续搅拌时间为30min,反应得到的氢氧化镁,结果如表2:Different concentrations of MgCl2 solutions were carried out single factor test, and MgCl2 and ammonia solution (13.33mol/l) were added at the same time, the reaction rate of magnesium chloride and ammonia solution was 10ml/min, the stirring rate was 150r/min, and the reaction temperature was 80°C 1. After the material is added, the stirring time is continued to be 30min, and the magnesium hydroxide obtained by the reaction is shown in Table 2 as a result:
表2卤水镁离子浓度对产物过滤速度影响The impact of table 2 brine magnesium ion concentration on product filtration rate
从镁转化率来看,Mg Cl2浓度在3mol/l时,镁转化率较高。在低浓度时,增加Mg2+浓度转化率明显提升,过滤速度稍微提高,超过3mol/l后,转化率变化减慢,过滤速度和堆积密度变化明显,这是因为Mg2+浓度升高,溶液出现胶状,搅拌作用被弱化,镁离子扩散受到影响。因此卤水镁离子浓度选3mol/l。From the perspective of magnesium conversion rate, when the concentration of MgCl 2 is 3mol/l, the magnesium conversion rate is higher. At low concentration, increasing the Mg 2+ concentration increases the conversion rate significantly, and the filtration rate increases slightly. After exceeding 3mol/l, the conversion rate slows down, and the filtration rate and bulk density change significantly. This is because the Mg 2+ concentration increases. The solution appears colloidal, the stirring effect is weakened, and the diffusion of magnesium ions is affected. Therefore, the concentration of magnesium ions in brine is 3mol/l.
实施例2Example 2
实验过程中,同时加入MgCl2和氨水溶液,氯化镁和氨水反应滴加速度都为10ml/min、搅拌速率为150r/min、反应温度80℃、物料加完后继续搅拌时间为30min,反应得到的氢氧化镁,MgCl2与氨物料摩尔比分别为1∶2.2,1∶2.4,1∶2.6,1∶2.8,其他条件保持一样。得到结果如表3:During the experiment, MgCl and ammonia solution were added at the same time, the reaction titration rate of magnesium chloride and ammonia solution was 10ml/min, the stirring rate was 150r/min, the reaction temperature was 80°C, and the stirring time was continued for 30min after the addition of the materials. Magnesium oxide, MgCl 2 and ammonia material molar ratio are respectively 1: 2.2, 1: 2.4, 1: 2.6, 1: 2.8, and other conditions remain the same. The results are shown in Table 3:
表3物料比对产物过滤速度影响Table 3 Material Ratio Effect on Product Filtration Speed
从实验数据可以看出,氨水量增加,有利于晶体长大,过滤速度和堆积密度明显变化,但物料比超过1∶2.6后,过滤速度缓慢减小,这是因为反应中游离氨浓度大,使氢氧化镁的瞬时过饱和度增大,有利于晶核形成却不利于生长。所以实验选择氨物料比为1∶2.6。It can be seen from the experimental data that the increase in the amount of ammonia water is conducive to the growth of crystals, and the filtration speed and bulk density change significantly. However, after the material ratio exceeds 1:2.6, the filtration speed decreases slowly. This is because the concentration of free ammonia in the reaction is large. The instantaneous supersaturation of magnesium hydroxide increases, which is beneficial to the formation of crystal nuclei but not conducive to growth. Therefore, the ratio of ammonia to material was chosen to be 1:2.6 in the experiment.
实施例3Example 3
同时加入MgCl2(3mol/l)和氨水溶液(MgCl2与氨物料摩尔比分别为1∶2.6),氯化镁和氨水反应滴加速度都为10ml/min、搅拌速率为150r/min、反应温度80℃、物料加完后继续搅拌时间为30min,加入产物反应量10%-40%的氢氧化镁作为晶体,反应得到的氢氧化镁,结果如表4:Add MgCl simultaneously (3mol/l) and ammoniacal solution (MgCl and ammonia material molar ratio are respectively 1 : 2.6), magnesium chloride and ammoniacal liquor reaction rate of addition are all 10ml/min, stirring speed is 150r/min, 80 ℃ of reaction temperatures, After adding the materials, continue to stir for 30 minutes, add magnesium hydroxide with a product reaction volume of 10%-40% as crystals, and react the magnesium hydroxide obtained. The results are shown in Table 4:
表4晶种加入量对产物过滤速度影响Table 4 The effect of seed crystal addition on product filtration speed
在晶种量为10%时,滤饼呈板结过滤速度较慢,20%以上,过滤速度缓慢增加,而加入30%转化率最大,所以选择加入反应量30%的氢氧化镁作为晶种较合适。When the amount of seed crystals is 10%, the filter cake is hardened and the filtration speed is slow. If it is more than 20%, the filtration speed increases slowly, and the conversion rate is the largest when 30% is added. Therefore, it is better to select magnesium hydroxide with 30% reaction amount as the crystal seed. Suitable.
实施例4Example 4
同时加入MgCl2(3mol/1)和氨水溶液,氯化镁和氨水反应滴加速度都为10ml/min(MgCl2与氨物料摩尔比分别为1∶2.6)、搅拌速率为50~150r/min、反应温度80℃、物料加完后继续搅拌时间为30min,加入产物反应量30%的氢氧化镁作为晶体,反应得到的氢氧化镁,不同搅拌转速下得到的结果如表5:Add MgCl 2 (3mol/1) and ammonia solution simultaneously, magnesium chloride and ammonia solution reaction rate of addition are all 10ml/min (MgCl 2 and ammonia material molar ratio are 1: 2.6 respectively), stirring rate is 50~150r/min, reaction temperature 80°C, after adding the materials, continue to stir for 30 minutes, add magnesium hydroxide with a reaction volume of 30% of the product as a crystal, and react the obtained magnesium hydroxide. The results obtained under different stirring speeds are shown in Table 5:
表5搅拌速度对产物过滤速度影响The influence of table 5 stirring speed on product filtration speed
从表5,可以看出其他条件不变,搅拌速度增大,过滤性能增强,但是只要搅拌起来使溶液分散,在增大搅拌速度,过滤性能就变化不大,说明搅拌速度起到使氢氯化镁溶液的分散而降低瞬时饱和度,生成沉淀的粒度增大。所以选择搅拌速度150r/min。From table 5, it can be seen that other conditions are constant, the stirring speed increases, and the filtration performance strengthens, but as long as the solution is dispersed by stirring, and the stirring speed is increased, the filtration performance does not change much, indicating that the stirring speed plays a role in making magnesium hydrochloride The dispersion of the solution reduces the instantaneous saturation, and the particle size of the generated precipitate increases. So choose stirring speed 150r/min.
实施例5Example 5
同时加入MgCl2和氨水溶液(MgCl2与氨物料摩尔比分别为1∶2.6),氯化镁和氨水反应滴加速度都为10ml/min、搅拌速率为150r/min、加入产物反应量30%的氢氧化镁作为晶体,物料加完后在40~80℃、在150r/min下继续搅拌时间为30min,反应得到的氢氧化镁,Add MgCl 2 and ammonia solution simultaneously (MgCl 2 and ammonia material molar ratio are 1: 2.6 respectively), magnesium chloride and ammonia water reaction titration rate are all 10ml/min, stirring speed is 150r/min, add the hydroxide of 30% product reaction amount Magnesium is used as a crystal. After the material is added, the stirring time is continued at 40-80°C and 150r/min for 30 minutes. The magnesium hydroxide obtained by the reaction,
不同温度条件下的结果如表6所示:The results under different temperature conditions are shown in Table 6:
表6反应温度对产物过滤速度影响The influence of table 6 reaction temperature on product filtration speed
由表6可知,温度高,过滤速度加快,但是温度过高,氨水利用率降低,三口瓶内压力增大还容易引起实验事故,所以温度达到80℃时,温度不宜再加。It can be seen from Table 6 that the higher the temperature, the faster the filtration rate, but if the temperature is too high, the utilization rate of ammonia water will decrease, and the increase in the pressure in the three-necked bottle will easily cause experimental accidents. Therefore, when the temperature reaches 80°C, the temperature should not be increased.
实施例6Example 6
将MgCl2溶液(浓度3moL/L)进行单因素试验,同时加入MgCl2和氨水溶液((MgCl2与氨物料摩尔比分别为1∶2.6)),搅拌速率为150r/min、反应温度80℃、物料加完后继续搅拌时间为30min,反应得到的氢氧化镁,其他条件不变,改变反应滴加速度,结果如表7。The MgCl 2 solution (concentration 3moL/L) was subjected to a single factor test, while adding MgCl 2 and ammonia solution ((MgCl 2 and ammonia material molar ratio were 1:2.6)), the stirring rate was 150r/min, and the reaction temperature was 80°C 1. After the material has been added, the stirring time is continued for 30min, and the magnesium hydroxide obtained by the reaction, other conditions are constant, and the reaction rate of addition is changed, and the results are shown in Table 7.
表7氨水、氯化镁滴加速度对产物过滤速度影响Table 7 ammoniacal liquor, magnesium chloride drop speed influence on product filtration speed
根据表7,可以分析出:当氯化镁滴加过快时,氨气通入量不够,反应不完全,粒度很小;当氨水通入快时,反应液中游离氨浓度大,使氢氧化镁的瞬时过饱和度增大,有利于晶核成形却不利于生长,颗粒也很小;当两边滴加速度相等且较慢时,粒度明显变大,过滤速度变快。所以氯化镁,氨水反应滴加速度都为10ml/min较合适。According to Table 7, it can be analyzed that: when magnesium chloride was added dropwise too fast, the amount of ammonia gas feeding was not enough, the reaction was not complete, and the particle size was very small; The instantaneous supersaturation increases, which is conducive to the formation of crystal nuclei but not conducive to growth, and the particles are also very small; when the dropping speed on both sides is equal and slow, the particle size becomes obviously larger and the filtration speed becomes faster. Therefore, it is more appropriate for magnesium chloride and ammonia water reaction titration rate to be 10ml/min.
实施例7Example 7
分别将MgCl2溶液(浓度3moL/L)进行单因素试验,同时加入MgCl2和氨水溶液,(MgCl2与氨物料摩尔比分别为1∶2.6),氯化镁和氨水反应滴加速度都为10ml/min、搅拌速率为150r/min、反应温度80℃、反应时间主要是对镁转化率的影响,但是在探究实验时发现,反应时间太长产品也会难以过滤,所以实验其它因素照上诉最佳方案做,反应时间分别有样品1∶10min;样品2∶20min;样品3∶30min;样品4∶40min;样品5∶50min,样品6∶60min结果如表8. MgCl2 solution (concentration 3moL/L) is carried out single factor test respectively, add MgCl2 and ammonia solution simultaneously, ( MgCl2 and ammonia material molar ratio are respectively 1: 2.6), magnesium chloride and ammoniacal liquor reaction titration rate are all 10ml/min , The stirring rate is 150r/min, the reaction temperature is 80°C, and the reaction time mainly affects the conversion rate of magnesium. However, when exploring the experiment, it is found that the product will be difficult to filter if the reaction time is too long, so other factors in the experiment follow the best plan of the appeal. Do, the reaction time has respectively sample 1: 10min; Sample 2: 20min; Sample 3: 30min; Sample 4: 40min; Sample 5: 50min, sample 6: 60min.
表8反应时间对转化率和过滤性的影响The impact of table 8 reaction time on conversion rate and filterability
很容易看出,随着时间的增加,反应转化率逐渐上升,在前20分钟时,氯化镁和氨水浓度都高,两者结合生成大量的氢氧化镁,随着两边滴加完毕,OH-1和Mg2+浓度双双下降,反应变得缓慢,晶体慢慢长大。大于40分钟后,反应转化率几乎没改变,氢氧化镁转化率下降,因为这时几乎没生成产品且Mg(OH)2会反溶,造成粒径缩小,溶液难过滤,所以将30分钟作为最佳反应时间。It is easy to see that with the increase of time, the conversion rate of the reaction gradually increases. In the first 20 minutes, the concentration of magnesium chloride and ammonia water is high, and the combination of the two generates a large amount of magnesium hydroxide . Both the concentration of Mg 2+ and Mg 2+ decrease, the reaction becomes slow, and the crystal grows slowly. After more than 40 minutes, the conversion rate of reaction hardly changed, and the conversion rate of magnesium hydroxide decreased, because at this time, almost no product was generated and Mg(OH) 2 would be reversely dissolved, causing the particle size to dwindle, and the solution was difficult to filter, so 30 minutes were used as optimal reaction time.
本实例采用氨法制备氢氧化镁,单因素法考虑不同条件对其过滤速度的影响,找出过滤性好的工艺条件,为下一章的降氯根浓度提供便利,得出结论如下:This example uses the ammonia method to prepare magnesium hydroxide. The single factor method considers the influence of different conditions on its filtration speed, finds out the process conditions with good filterability, and provides convenience for the reduction of chloride concentration in the next chapter. The conclusions are as follows:
(1)实验中卤水镁离子浓度3.0mol/L、氯化镁溶液和氨水的摩尔比为1∶2.6、加入产物量30%的氢氧化镁做晶种、氯化镁和氨水反应滴加速度都为10ml/min、搅拌速率为150r/min、反应温度80℃、物料加完后继续搅拌时间为30min,反应得到的氢氧化镁粒径大、过滤性能好(523ml/min)、堆积密度高(0.87g/ml)。(1) In the experiment, the concentration of magnesium ions in brine is 3.0mol/L, the mol ratio of magnesium chloride solution and ammoniacal liquor is 1: 2.6, the magnesium hydroxide that adds product amount 30% is made crystal seed, and magnesium chloride and ammoniacal liquor reaction rate of addition are all 10ml/min , the stirring speed is 150r/min, the reaction temperature is 80°C, and the stirring time after the addition of the materials is 30min, the magnesium hydroxide particle size obtained by the reaction is large, the filtration performance is good (523ml/min), and the bulk density is high (0.87g/ml ).
实施例1~7制得的氢氧化镁的氯含量在0.8%。制备的氢氧化镁中忽略了其中氯离子含量,本发明首次关注制得的氢氧化镁中的氯含量问题。通过采用以下的实施例,进行陈化洗涤,旨在降低氯含量;此外,以下实施例,通过考察氢氧化镁的粒度,陈化洗涤温度,陈化洗涤时间及液固比等因素对降低氯根浓度的影响,以确定了最佳陈化工艺条件。The chlorine content of the magnesium hydroxide that embodiment 1~7 makes is at 0.8%. The content of chloride ions therein is ignored in the prepared magnesium hydroxide, and the present invention pays attention to the problem of chlorine content in the prepared magnesium hydroxide for the first time. By adopting the following examples, aging and washing are carried out to reduce the chlorine content; in addition, the following examples, by investigating the particle size of magnesium hydroxide, the aging washing temperature, the aging washing time and the liquid-solid ratio and other factors to reduce chlorine root concentration to determine the optimal aging process conditions.
本发明氯含量的测定方法为:洗涤后固液分离后,将滤液提出可以做制氢氧化镁的母液,再定量分批加水洗涤滤饼,真空抽滤,每次取一定量的滤液和硝酸银反应,直到几乎无白色沉淀。烘干后,取一定量称重与稀硝酸反应至刚好溶解,测其氯根浓度。The measuring method of chlorine content of the present invention is: after the solid-liquid separation after washing, the filtrate is put forward and can be used as the mother liquor of making magnesium hydroxide, then quantitatively add water in batches to wash the filter cake, vacuum suction filtration, take a certain amount of filtrate and nitric acid each time The silver was reacted until almost no white precipitate was left. After drying, take a certain amount and weigh it to react with dilute nitric acid until it just dissolves, and measure its chloride concentration.
实施例8Example 8
本发明以实施例1(例如采用3号实验产品)制得的氢氧化镁为原料(氯含量在0.8%),The present invention is raw material (chlorine content is at 0.8%) with the magnesium hydroxide that embodiment 1 (for example adopts No. 3 experimental product) to make,
将样品分为1:无研磨;2:研磨5min;3:研磨10min;4:研磨15min;5:研磨20min。放入液固质量比为2∶1的烧杯中,80℃下,搅拌40分钟,结果如表9(原产品中氯根含量为0.97)。Divide the samples into 1: no grinding; 2: grinding for 5 min; 3: grinding for 10 min; 4: grinding for 15 min; 5: grinding for 20 min. Put it into a beaker with a liquid-solid mass ratio of 2:1, stir at 80°C for 40 minutes, and the results are shown in Table 9 (the content of chloride in the original product is 0.97).
表9研磨时间对氯根含量和过滤速度的影响The impact of table 9 grinding time on chloride radical content and filtration speed
从表9可以看到,氢氧化镁研磨时间越长,氯根含量越小,但是到了研磨10分钟后,氯根含量几乎没有变化,这是因为研磨使产品粒度减小,加大了与水接触面积。As can be seen from Table 9, the longer the magnesium hydroxide grinding time, the smaller the chloride content, but after 10 minutes of grinding, the chloride content hardly changes, this is because the grinding reduces the particle size of the product and increases the water content. Contact area.
实施例9Example 9
本发明以实施例1(例如采用3号实验产品)制得的氢氧化镁为原料,考察了以确定了最佳陈化工艺条件,采用不研磨,将样品放入到液固比为2∶1的烧杯中,分别在50℃、60℃、70℃、80℃、90℃下,搅拌40分钟,氯根含量如表10。The present invention takes the magnesium hydroxide that embodiment 1 (for example adopts No. 3 experimental product) to make as raw material, has investigated to have determined optimal aging process condition, adopts not to grind, and sample is put into the liquid-solid ratio and is 2: 1 in a beaker, respectively at 50°C, 60°C, 70°C, 80°C, and 90°C, and stirred for 40 minutes. The content of chloride radicals is shown in Table 10.
表10温度对氯根含量和过滤速度的影响The influence of table 10 temperature on chlorine radical content and filtering speed
从表10中看出,开始温度越高,氯根含量越低,在80℃以上后,氯根含量几乎没有变化。It can be seen from Table 10 that the higher the starting temperature, the lower the content of chloride radicals, and there is almost no change in the content of chloride radicals above 80°C.
温度升高,体系中离子活性加大,氯根更容易溶于水;此后温度上升,产品容易聚集,粒度变大,容易包裹氯根;合适的洗涤温度为80℃。As the temperature rises, the ion activity in the system increases, and the chloride radicals are more easily soluble in water; after the temperature rises, the product is easy to aggregate, the particle size becomes larger, and it is easy to wrap the chloride radicals; the suitable washing temperature is 80°C.
实施例10Example 10
本发明以实施例1(例如采用3号实验产品)制得的氢氧化镁为原料,以确定了最佳搅拌转速的最佳工艺条件,将样品放入到液固比为2∶1的烧杯中,在80℃下,反应40分钟,搅拌速度分别为50r/min、100r/min、150r/min、200r/min、250r/min,氯根含量如表11。The present invention takes the magnesium hydroxide that embodiment 1 (for example adopts No. 3 experimental product) to make as raw material, to determine the optimum process condition of optimum stirring speed, sample is put into the beaker that liquid-solid ratio is 2: 1 , at 80°C, reacted for 40 minutes, stirring speeds were 50r/min, 100r/min, 150r/min, 200r/min, 250r/min, and the chloride content was shown in Table 11.
表11搅拌速度对氯根含量和过滤速度的影响The impact of table 11 stirring speed on chloride radical content and filtration speed
从表11可以看到,搅拌速度越大,氯根的含量越低,当搅拌速度50r/min时,沉淀没搅拌起来,氯含量下降慢。It can be seen from Table 11 that the greater the stirring speed, the lower the content of chlorine radicals. When the stirring speed was 50r/min, the precipitate was not stirred and the chlorine content decreased slowly.
之后搅拌速度快,加大氯根和水接触机会,氯含量下降快,所以实验搅拌速度选择到250r/min。Afterwards, the stirring speed is fast, and the chance of contact between chlorine radicals and water is increased, and the chlorine content drops rapidly, so the experimental stirring speed is selected to be 250r/min.
实施例11Example 11
本发明以实施例1(例如采用3号实验产品)制得的氢氧化镁为原料,研究液固比的最佳工艺条件,将液固比分别为1,2,3,4,5的5种样品,在80℃,250r/min搅拌40分钟后,得到氯根含量如表12。The present invention is with the magnesium hydroxide that embodiment 1 (for example adopts No. 3 experimental product) to make as raw material, researches the optimal process condition of liquid-solid ratio, and liquid-solid ratio is respectively 1,2,3,4,5 5 After a sample was stirred at 80°C and 250r/min for 40 minutes, the chloride content was obtained as shown in Table 12.
表12液固比对氯根含量和过滤速度的影响The impact of table 12 liquid-solid ratio on chloride content and filtration speed
表12中看到,液固比越大,氯根含量只是稍有下降,液固比1∶1时氯根较多,原因可能是水相比于固体太少,搅拌过后,有些固体跟水没有接触。It can be seen in Table 12 that the larger the liquid-solid ratio, the chloride content is only slightly reduced. When the liquid-solid ratio is 1:1, there are more chlorine radicals. The reason may be that water is too small compared to solids. After stirring, some solids and water no contact.
实施例12Example 12
本发明以实施例1(例如采用3号实验产品)制得的氢氧化镁为原料,研究搅拌时间对氯根含量的最佳工艺条件将液固比2∶1的样品在80℃,搅拌速度达250r/min下,反应时间分别为10min;20min;30min;40min;50min,结果如下表13。The present invention is with the magnesium hydroxide that embodiment 1 (for example adopts No. 3 experimental products) to make as raw material, researches stirring time to the best process condition of chloride root content with the sample of liquid-solid ratio 2: 1 at 80 ℃, stirring speed At 250r/min, the reaction time is 10min; 20min; 30min; 40min; 50min, the results are shown in Table 13 below.
表13搅拌时间对氯根含量和过滤速度的影响The impact of table 13 stirring time on chloride radical content and filtration speed
由表13分析,搅拌时间越长,氯根含量越低,但到了40分钟以后,变化就不太明显,这是因为搅拌越久,氢氧化镁粒径越小,氯根溶解更彻底。考虑到过滤情况,实验该选搅拌时间40分钟最佳。According to the analysis in Table 13, the longer the stirring time, the lower the chloride content, but after 40 minutes, the change is not obvious, because the longer the stirring, the smaller the particle size of magnesium hydroxide and the more thorough dissolution of chloride. Considering the filtration situation, the best stirring time for the experiment is 40 minutes.
单级洗涤能达到一定的效果,但得到的氢氧化镁的氯含量不稳定,很多情况下,洗涤后的氢氧化镁的氯含量并不能降至0.3%以下,工艺不稳定,Single-stage washing can achieve a certain effect, but the chlorine content of the magnesium hydroxide obtained is unstable. In many cases, the chlorine content of the magnesium hydroxide after washing cannot be reduced to below 0.3%, and the process is unstable.
实施例13Example 13
如附图2所示示意图,As shown in the schematic diagram in Figure 2,
将沉降罐含固量500kg/m3的料浆按30m3/h的流量泵入1号陈化罐中,同时2号陈化罐溢流洗液(60m3/h)也进入1号陈化罐中,并在该陈化罐中进行搅拌陈化沉降分离,上清液(60m3/h)并入母液去蒸氨工段,底料料浆含固量控制在30kg/m3泵入2号陈化罐,同时3号陈化罐洗液也进入2号陈化罐进行搅拌陈化沉降分离,其余类推,铵根、氯根含量如表14;单罐中的洗涤过程的温度为80℃;搅拌转速为250r/min;洗涤固液比为1∶2。Pump the slurry with a solid content of 500kg/m3 in the settling tank into the No. 1 aging tank at a flow rate of 30m3/h, and at the same time, the overflow washing liquid (60m3/h) of the No. 2 aging tank also enters the No. 1 aging tank , and carry out stirring, aging, sedimentation and separation in the aging tank, the supernatant (60m3/h) is incorporated into the mother liquor de-ammonia distillation section, and the solid content of the bottom material slurry is controlled at 30kg/m3 and pumped into No. 2 aging tank At the same time, the No. 3 aging tank lotion also enters the No. 2 aging tank for stirring, aging, sedimentation and separation, and the rest are analogous. The contents of ammonium and chloride are shown in Table 14; It is 250r/min; the washing solid-liquid ratio is 1:2.
表14多段逆流沉降洗涤铵根氯根含量的影响The impact of table 14 multistage countercurrent sedimentation washing ammonium chloride content
沉降罐游离氨含量一般控制在2kmol/m3,假设1、2、3、4、5、6号陈化罐中的游离氨含量分别为C1、C2、C3、C4、C5、C6、则下列关系式成立:The free ammonia content in the settling tank is generally controlled at 2 kmol/m3, assuming that the free ammonia content in No. 1, 2, 3, 4, 5, and 6 aging tanks are respectively C1, C2, C3, C4, C5, and C6, then the following relationship The formula is established:
C1=(30×2+60C2)/90=(2+2C2)/3 (1)C1=(30×2+60C2)/90=(2+2C2)/3 (1)
C2=(30C1+60C3)/90=(C1+2C3)/3 (2)C2=(30C1+60C3)/90=(C1+2C3)/3 (2)
C3=(30C2+60C4)/90=(C2+2C4)/3 (3)C3=(30C2+60C4)/90=(C2+2C4)/3 (3)
C4=(30C3+60C5)/90=(C3+2C5)/3 (4)C4=(30C3+60C5)/90=(C3+2C5)/3 (4)
C5=(30C4+60C6)/90=(C4+2C6)/3 (5)C5=(30C4+60C6)/90=(C4+2C6)/3 (5)
C6=30C5/90=C5/3 (6)C6=30C5/90=C5/3 (6)
C1=63C6,C2=31C6,C3=15C6,C4=7C6,C5=3C6C1=63C6, C2=31C6, C3=15C6, C4=7C6, C5=3C6
将C1=63C6,C2=31C6代入(1)式中Substitute C1=63C6, C2=31C6 into (1) formula
63C6=(2+2×31 C6)/363C6=(2+2×31 C6)/3
C6=0.01575kmol/m3C6=0.01575kmol/m3
即经过6个陈化罐洗涤搅拌陈化后,洗液中游离氨含量由原料的2kmol/m3降到了0.01575kmol/m3,比照上述氨的洗涤效果,沉降罐中氯离子浓度为6.254kmol/m3,同样经过6个陈化罐洗涤搅拌陈化后,氯离子浓度应降为:That is, after washing, stirring and aging in 6 aging tanks, the content of free ammonia in the lotion dropped from 2 kmol/m3 of the raw material to 0.01575 kmol/m3. Compared with the above-mentioned ammonia washing effect, the chloride ion concentration in the settling tank was 6.254 kmol/m3 , after washing, stirring and aging in 6 aging tanks, the chloride ion concentration should be reduced to:
(6.254/2)×0.01575=0.04925kmol/m3=1.748kg/m3(6.254/2)×0.01575=0.04925kmol/m3=1.748kg/m3
假设6号陈化罐底料料浆(含固量500kg/m3)经离心机脱水后含水率为10%,则不经洗涤时,氢氧化镁产品中氯根含量为:(1.5m3×1.748kg/m3)/15000kg=0.01748%。Assuming that No. 6 aging tank bottom material slurry (solid content 500kg/m3) has a water content of 10% after centrifuge dehydration, then without washing, the chlorine content in the magnesium hydroxide product is: (1.5m3 * 1.748 kg/m3)/15000kg=0.01748%.
通过实施例13与实施例8~12比较发现,采用实施例13的多级逆流洗涤,具有以下进一步的优势:By comparing Example 13 with Examples 8-12, it is found that the multistage countercurrent washing of Example 13 has the following further advantages:
相比单级洗涤相比氯根在0.25-3.2%之间,采用连续多段逆流沉降的洗涤方法,氢氧化镁料浆经过6级陈化后,①产品中的氯根含量能够降到最低水平可以将氯根含量降到0.2%(0.01748)以下,而且比较稳定,这样可望彻底解决过去一直存在的产品质量(特别是氯根含量)不稳定的问题。Compared with single-stage washing, the chlorine root content is between 0.25-3.2%, and the continuous multi-stage countercurrent sedimentation washing method is adopted. After the magnesium hydroxide slurry undergoes 6-stage aging, ① the chlorine root content in the product can be reduced to the lowest level Chloride content can be reduced to less than 0.2% (0.01748), and relatively stable, which is expected to completely solve the problem of unstable product quality (especially chloride content) that has always existed in the past.
②氢氧化镁料浆经过6级陈化后,料浆中的游离氨含量可降到0.01575mol/L,再通过离心机过滤分离时不会有氨气溢出,使离心机操作环境大为改善。② After the magnesium hydroxide slurry has been aged for 6 stages, the free ammonia content in the slurry can be reduced to 0.01575mol/L, and there will be no ammonia gas overflow when it is filtered and separated by the centrifuge, which greatly improves the operating environment of the centrifuge .
③氢氧化镁料浆经过6级陈化后,离心机分离时无需再加水洗涤(或加很少量的水),直接脱水即可满足产品质量要求,这样离心机的处理能力大大增加,可以大幅度降低能耗。③ After the magnesium hydroxide slurry has undergone 6-stage aging, there is no need to add water for washing (or add a small amount of water) when the centrifuge is separated, and the direct dehydration can meet the product quality requirements. In this way, the processing capacity of the centrifuge is greatly increased, which can Significantly reduce energy consumption.
④氢氧化镁料浆通过加水连续陈化,洗涤加水量少且恒定,可以确保蒸氨母液成分的稳定,因而可以确保生产工艺的稳定。④ The magnesium hydroxide slurry is continuously aged by adding water, and the amount of water added for washing is small and constant, which can ensure the stability of the ammonia distilled mother liquor composition, thus ensuring the stability of the production process.
⑤可以不用当心6台离心机304不锈钢材质的问题。⑤ You don't have to worry about the 304 stainless steel material of the 6 centrifuges.
⑥新增加的设备投资费用不多。⑥ The newly added equipment investment cost is not much.
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