TW201540668A - Method for recycling ammonium sulfate to manufacture dihydrate gypsum - Google Patents
Method for recycling ammonium sulfate to manufacture dihydrate gypsum Download PDFInfo
- Publication number
- TW201540668A TW201540668A TW103114127A TW103114127A TW201540668A TW 201540668 A TW201540668 A TW 201540668A TW 103114127 A TW103114127 A TW 103114127A TW 103114127 A TW103114127 A TW 103114127A TW 201540668 A TW201540668 A TW 201540668A
- Authority
- TW
- Taiwan
- Prior art keywords
- gypsum
- ammonium sulfate
- dihydrate gypsum
- ammonia
- reaction
- Prior art date
Links
- 229910052602 gypsum Inorganic materials 0.000 title claims abstract description 166
- 239000010440 gypsum Substances 0.000 title claims abstract description 166
- 150000004683 dihydrates Chemical class 0.000 title claims abstract description 105
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 title claims abstract description 83
- 229910052921 ammonium sulfate Inorganic materials 0.000 title claims abstract description 82
- 235000011130 ammonium sulphate Nutrition 0.000 title claims abstract description 82
- 238000000034 method Methods 0.000 title claims abstract description 29
- 238000004519 manufacturing process Methods 0.000 title claims abstract description 19
- 238000004064 recycling Methods 0.000 title abstract description 5
- 238000006243 chemical reaction Methods 0.000 claims abstract description 67
- 238000006703 hydration reaction Methods 0.000 claims abstract description 45
- 239000000243 solution Substances 0.000 claims abstract description 42
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical class [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 claims abstract description 36
- 235000012255 calcium oxide Nutrition 0.000 claims abstract description 36
- 239000011259 mixed solution Substances 0.000 claims abstract description 27
- 235000011116 calcium hydroxide Nutrition 0.000 claims abstract description 21
- 239000000203 mixture Substances 0.000 claims abstract description 16
- 150000004679 hydroxides Chemical class 0.000 claims abstract description 11
- 159000000007 calcium salts Chemical class 0.000 claims abstract description 7
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 82
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 45
- 229910021529 ammonia Inorganic materials 0.000 claims description 40
- 230000036571 hydration Effects 0.000 claims description 33
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims description 32
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 30
- 239000000292 calcium oxide Substances 0.000 claims description 25
- 239000013078 crystal Substances 0.000 claims description 25
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 23
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 claims description 21
- 239000000920 calcium hydroxide Substances 0.000 claims description 18
- 229910001861 calcium hydroxide Inorganic materials 0.000 claims description 18
- 238000000926 separation method Methods 0.000 claims description 18
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 claims description 16
- 235000011114 ammonium hydroxide Nutrition 0.000 claims description 16
- 238000001035 drying Methods 0.000 claims description 15
- 238000005649 metathesis reaction Methods 0.000 claims description 13
- 239000002253 acid Substances 0.000 claims description 12
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 claims description 12
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 claims description 11
- 230000035484 reaction time Effects 0.000 claims description 10
- 239000002002 slurry Substances 0.000 claims description 9
- ZOMBKNNSYQHRCA-UHFFFAOYSA-J calcium sulfate hemihydrate Chemical compound O.[Ca+2].[Ca+2].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O ZOMBKNNSYQHRCA-UHFFFAOYSA-J 0.000 claims description 7
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 6
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 claims description 6
- 229910052925 anhydrite Inorganic materials 0.000 claims description 6
- 238000004821 distillation Methods 0.000 claims description 4
- 238000002156 mixing Methods 0.000 claims description 4
- 239000007787 solid Substances 0.000 claims description 4
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 claims description 3
- 229910000147 aluminium phosphate Inorganic materials 0.000 claims description 3
- 229910017604 nitric acid Inorganic materials 0.000 claims description 3
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonium chloride Substances [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 claims description 2
- 238000010521 absorption reaction Methods 0.000 claims description 2
- 238000000265 homogenisation Methods 0.000 claims description 2
- 229910000272 alkali metal oxide Inorganic materials 0.000 claims 2
- 230000000887 hydrating effect Effects 0.000 claims 1
- 239000000126 substance Substances 0.000 claims 1
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 abstract description 4
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 17
- 239000007788 liquid Substances 0.000 description 16
- 239000002699 waste material Substances 0.000 description 13
- 150000008044 alkali metal hydroxides Chemical class 0.000 description 12
- 239000000047 product Substances 0.000 description 6
- 239000002351 wastewater Substances 0.000 description 5
- 239000001166 ammonium sulphate Substances 0.000 description 4
- 239000007789 gas Substances 0.000 description 3
- 230000003287 optical effect Effects 0.000 description 3
- 239000004065 semiconductor Substances 0.000 description 3
- 238000005406 washing Methods 0.000 description 3
- ZCCIPPOKBCJFDN-UHFFFAOYSA-N calcium nitrate Chemical compound [Ca+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O ZCCIPPOKBCJFDN-UHFFFAOYSA-N 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000000706 filtrate Substances 0.000 description 2
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 239000001110 calcium chloride Substances 0.000 description 1
- 229910001628 calcium chloride Inorganic materials 0.000 description 1
- 235000011148 calcium chloride Nutrition 0.000 description 1
- 239000001506 calcium phosphate Substances 0.000 description 1
- 229910000389 calcium phosphate Inorganic materials 0.000 description 1
- 235000011010 calcium phosphates Nutrition 0.000 description 1
- 235000011132 calcium sulphate Nutrition 0.000 description 1
- 238000005660 chlorination reaction Methods 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- NJPPVKZQTLUDBO-UHFFFAOYSA-N novaluron Chemical compound C1=C(Cl)C(OC(F)(F)C(OC(F)(F)F)F)=CC=C1NC(=O)NC(=O)C1=C(F)C=CC=C1F NJPPVKZQTLUDBO-UHFFFAOYSA-N 0.000 description 1
- 238000000053 physical method Methods 0.000 description 1
- OTYBMLCTZGSZBG-UHFFFAOYSA-L potassium sulfate Chemical compound [K+].[K+].[O-]S([O-])(=O)=O OTYBMLCTZGSZBG-UHFFFAOYSA-L 0.000 description 1
- 229910052939 potassium sulfate Inorganic materials 0.000 description 1
- 235000011151 potassium sulphates Nutrition 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 229910052938 sodium sulfate Inorganic materials 0.000 description 1
- 235000011152 sodium sulphate Nutrition 0.000 description 1
- 238000005496 tempering Methods 0.000 description 1
- 239000010409 thin film Substances 0.000 description 1
- QORWJWZARLRLPR-UHFFFAOYSA-H tricalcium bis(phosphate) Chemical compound [Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O QORWJWZARLRLPR-UHFFFAOYSA-H 0.000 description 1
Landscapes
- Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
Abstract
Description
本創作係關於一種回收硫酸銨製造二水石膏的方法,特別是使用於電子工業或一般工業處理含氨廢水,得到的硫酸銨廢液處理,用以製造純度高的二水石膏,以提供工業上再利用而頗具經濟價值之技術方法。
The present invention relates to a method for recovering dihydrate gypsum from ammonium sulfate, especially for treating ammonia-containing wastewater in the electronics industry or general industry, and treating the obtained ammonium sulfate waste liquid to produce dihydrate gypsum with high purity to provide industry A technical method of reusing and having economic value.
近年來國內產業蓬勃發展,相對地在製造過程中產生的廢水種類及數量隨之增加,例如電子工業或石化工業產生出來的含氨廢水,因受到政府環保法規要求氨氮管制之規定,不得不予以處理。含氨廢水的處理方法很多,例如氣提脫除、汽提回收、生化處理、薄膜蒸餾、折點加氯等,其中之一方法就是將氨轉成硫酸銨。硫酸銨利用的主要用途在於農業肥料,但因主管機關考量電子工業內含有很多重金屬或稀有金屬,產生的硫酸銨廢液用於農業時,將會造成不可預測的污染問題,而不建議用於農業,因此硫酸銨的用途大受限制,加上硫酸銨鮮少直接應用在農業以外之工業上而必須尋找其它再利用途徑。In recent years, the domestic industry has flourished, and the types and quantities of wastewater generated in the manufacturing process have increased. For example, ammonia-containing wastewater produced by the electronics industry or the petrochemical industry has to be regulated by the government's environmental regulations. deal with. There are many treatment methods for ammonia-containing wastewater, such as stripping, stripping, biochemical treatment, thin film distillation, and chlorination. One of the methods is to convert ammonia into ammonium sulfate. The main use of ammonium sulphate is in agricultural fertilizers. However, because the competent authority considers that many heavy metals or rare metals are contained in the electronics industry, the ammonium sulphate waste liquid produced in agriculture will cause unpredictable pollution problems and is not recommended for use. Agriculture, therefore, the use of ammonium sulphate is greatly limited, and the application of ammonium sulphate is rarely directly applied to industries other than agriculture, and other recycling routes must be sought.
目前國內硫酸銨的再利用技術,排除硫酸銨的直接應用,還處於摸索狀態,大部分重點在回收氨水,還沒有商業上技術可同時回收氨水及將硫酸銨內的硫酸根,轉成經濟價值高,純度高的二水石膏,而是當成廢棄物處理掉,造成資源利用上相當大的浪費。At present, the domestic ammonium sulfate recycling technology, in addition to the direct application of ammonium sulfate, is still in the state of exploration, most of the focus is on the recovery of ammonia water, there is no commercial technology to recover ammonia water at the same time and convert the sulfate in ammonium sulfate into economic value. High-purity, high-purity dihydrate gypsum, but treated as waste, resulting in considerable waste of resource utilization.
又,美國專利第3,637,347號提及,在處理燃料鍋爐產生的SOX
空氣污染時,利用氨水吸收SOX
生成硫酸銨,然後加入氧化鈣,生成硫酸鈣與氨水,氨水回收使用,但硫酸鈣則當做廢棄物處理掉。
Further, U.S. Patent No. 3,637,347 mentions that in the treatment of SO X air pollution generated by a fuel boiler, ammonia water is used to absorb SO X to form ammonium sulfate, and then calcium oxide is added to form calcium sulfate and ammonia water, and ammonia water is recycled, but calcium sulfate is used. Dispose of as waste.
為解決上述問題,本創作提供一種回收硫酸銨製造二水石膏的方法,包括反應步驟,將硫酸銨或硫酸銨溶液在20。 C~120。 C的溫度下與鈣的氧化物及/或氫氧化物及進行複分解反應,生成氨與石膏的混合物,然後利用物理方法將氨自混合溶液中分離出來並加以收集而得到氨水與去除氨之石膏混合液,調均步驟,在去除氨之石膏混合溶液加入硫酸或其他酸,將去除氨之石膏混合溶液中未反應之鈣的氧化物及/或氫氧化物,轉化成石膏或可溶性鈣鹽,水化步驟,將調均後溶液在20。 C~120。 C且低於反應步驟之溫度的條件下,進行石膏的水化反應,生成純度高的二水石膏,進一步獲得含高純度二水石膏的溶液,分離步驟,將含高純度二水石膏的溶液,利用分離設備,分離出含有游離水的高純度二水石膏。In order to solve the above problems, the present invention provides a method for recovering dihydrate gypsum from ammonium sulfate, comprising a reaction step of applying ammonium sulfate or ammonium sulfate solution at 20 . C~120 . At a temperature of C, it reacts with calcium oxides and/or hydroxides to form a mixture of ammonia and gypsum, and then physically separates ammonia from the mixed solution and collects it to obtain ammonia water and ammonia-removing gypsum. Mixing liquid, adjusting the average step, adding sulfuric acid or other acid to the ammonia-removing gypsum mixed solution, and converting the unreacted calcium oxide and/or hydroxide in the ammonia-gypsum mixed solution into gypsum or soluble calcium salt. In the hydration step, the solution will be adjusted to 20 after homogenization . C~120 . C and lower than the temperature of the reaction step, the hydration reaction of gypsum is carried out to form dihydrate gypsum with high purity, a solution containing high-purity dihydrate gypsum is further obtained, and a separation step is carried out to prepare a solution containing high-purity dihydrate gypsum. Using a separation device, high-purity dihydrate gypsum containing free water is separated.
本創作方法可以回收氨水,還可以得到純度高的二水石膏或,達到廢棄物回收及再利用目的。
The creation method can recover ammonia water, and can also obtain dihydrate gypsum with high purity, and achieve the purpose of waste recycling and reuse.
20‧‧‧硫酸銨溶液貯槽
22‧‧‧氧化鈣或氫氧化鈣漿液槽
24‧‧‧鹼金屬氫氧化物貯槽
25‧‧‧反應槽
26‧‧‧去除氨之石膏混合溶液
28‧‧‧氨汽
28‧‧‧A氨水貯槽
30‧‧‧調均後混合液
32‧‧‧水
33‧‧‧調均槽
34‧‧‧硫酸或其他酸
35‧‧‧水化槽
36‧‧‧二水石膏晶種
38‧‧‧含高純度二水石膏的溶液
39‧‧‧分離設備
40‧‧‧濾液
42‧‧‧含有游離水的高純度二水石膏
43‧‧‧乾燥設備
44‧‧‧二水石膏
R1‧‧‧反應步驟
R2‧‧‧調均步驟
R3‧‧‧水化步驟
S1‧‧‧分離步驟
D1‧‧‧乾燥步驟20‧‧‧Ammonium sulphate solution storage tank 22‧‧‧ Calcium oxide or calcium hydroxide slurry tank 24‧‧• Alkali metal hydroxide storage tank 25‧‧‧Reaction tank 26‧‧‧Ammonia-depleted gypsum mixed solution 28‧‧‧ Ammonia vapor 28‧‧A ammonia water storage tank 30‧‧ ‧After mixing mixture 32‧‧‧Water 33‧‧‧ Adjusting trough 34‧‧‧Sulfuric acid or other acid 35‧‧‧ Hydration tank 36‧‧‧2 Water gypsum seed crystal 38‧‧‧Solid containing high-purity dihydrate gypsum 39‧‧‧Separation equipment 40‧‧‧Development 42‧‧‧High-purity dihydrate gypsum containing free water 43‧‧‧ Drying equipment 44‧‧‧ Dihydrate gypsum
R1‧‧‧ reaction steps
R2‧‧‧ adjustment steps
R3‧‧‧Hydration step
S1‧‧‧ separation step
D1‧‧‧ drying step
第1圖顯示本創作方法製造二水石膏的簡要流程圖。Figure 1 shows a simplified flow chart for the production of dihydrate gypsum by the present authoring method.
第2圖顯示本創作方法製造二水石膏的設備流程圖。
Figure 2 shows a flow chart of the apparatus for manufacturing dihydrate gypsum by the present method.
以下說明僅便於解釋本創作基本教導而已,圖式說明中將對構成較佳實施例之成份、使用量、操作濃度、溫度及其他相關延伸將有所說明,在閱讀及了解本創作的敎導後相關之變化實施屬於業界技能。另外,在閱讀及了解本創作敎導後,配合特定設備、作用濃度、作用溫度及類似要求之改變亦屬業界技能。The following description is only for the convenience of explaining the basic teachings of the present invention. The description of the components, the amount of use, the operating concentration, the temperature and other related extensions constituting the preferred embodiment will be explained in reading and understanding of the creation. Post-related changes are implemented in industry skills. In addition, after reading and understanding the creative guidelines, changes in specific equipment, concentration, temperature and similar requirements are also industry skills.
依據圖式顯示,本創作提供一種自工業中回收硫酸銨製造二水石膏的方法10(如第1圖所示),其程序步驟包括反應步驟R1、調均步驟R2、水化步驟R3、分離步驟S1及乾燥步驟D1,其中:According to the schematic display, the present invention provides a method 10 for producing dihydrate gypsum from industrial ammonium sulfate (as shown in Fig. 1), the procedure comprising the reaction step R1, the adjustment step R2, the hydration step R3, and the separation. Step S1 and drying step D1, wherein:
反應步驟R1,係自工業回收的硫酸銨或硫酸銨溶液在20。 C~120。 C的溫度下與鈣的氧化物、氫氧化物或鹼金屬氫氧化物的其中任意至少一種進行複分解反應,而生成氨與石膏的混合物,然後利用物理方法將氨自石膏的混合物中分離出來,獲得氨水與去除氨之石膏混合溶液。Reaction step R1 is carried out from an industrially recovered ammonium sulfate or ammonium sulfate solution at 20 . C~120 . a metathesis reaction with any of at least one of calcium oxides, hydroxides or alkali metal hydroxides at a temperature of C to form a mixture of ammonia and gypsum, and then physically separating the ammonia from the mixture of gypsum, A mixed solution of ammonia water and ammonia-removing gypsum is obtained.
調均步驟R2,在去除氨之石膏混合溶液加入硫酸或其他酸,將去除氨之石膏混合溶液中未反應之鈣的氧化物及/或氫氧化物,轉化成石膏或可溶性鈣鹽,而獲得調均後混合液。Adjusting the average step R2, adding sulfuric acid or other acid to the ammonia-removing gypsum mixed solution, and converting the unreacted calcium oxide and/or hydroxide in the ammonia-gypsum mixed solution into gypsum or soluble calcium salt, thereby obtaining Adjust the mixture after mixing.
水化步驟R3,調均後溶液在20。 C~120。 C的溫度且低於反應段之溫度的條件下,進行石膏的水化反應,生成含高純度二水石膏的溶液。The hydration step R3, after adjusting the average solution, is at 20 . C~120 . The hydration reaction of gypsum is carried out under the conditions of the temperature of C and lower than the temperature of the reaction section to form a solution containing high-purity dihydrate gypsum.
分離步驟S1,將含高純度二水石膏的溶液利用分離設備分離取得含有游離水的高純度二水石膏。In the separation step S1, the solution containing the high-purity dihydrate gypsum is separated by a separation device to obtain high-purity dihydrate gypsum containing free water.
此外為了將二水石膏製成其他結晶的石膏產品,進一步可以利用一乾燥步驟D1將分離出之含有游離水的高純度二水石膏,利用乾燥設備去除游離水或去除結晶水,生產出不同結晶型態之石膏,也就是說依據去除游離水或結晶水的程度可以製成二水、半水或無水的石膏產品。In addition, in order to make the dihydrate gypsum into other crystallized gypsum products, the high-purity dihydrate gypsum containing the free water can be further separated by a drying step D1, and the free water or the crystal water can be removed by using a drying device to produce different crystals. The type of gypsum, that is to say, the dihydrate, semi-aqueous or anhydrous gypsum product can be produced according to the degree of removal of free water or crystal water.
以上各段採用的設備,可以依照製造工序,例如採用連續式或批次操作,將各段設備獨立進行,或將數段程序合併在一座或一座以上設備進行,例如批次反應時,反應步驟、調均步驟、與水化步驟可以使用單座、雙座、或參座設備進行。The equipment used in the above paragraphs may be carried out independently according to the manufacturing process, for example, by continuous or batch operation, or by combining several stages of equipment in one or more equipment, such as batch reaction, reaction steps. The adjustment step, and the hydration step can be performed using a single seat, two seat, or pedestal device.
本創作方法在反應步驟R1中,自工業中回收的硫酸銨或硫酸銨溶液並不需要限制在特定的飽和濃度下才能進行複分解反應,但建議加入水調整硫酸銨溶液之濃度介於5%~40%,最佳濃度為10%~30%,因為硫酸銨溶液若濃度太低,反應設備所需的空間較大,若硫酸銨溶液濃度太高,超過飽和溶解度,複分解反應效率變低,且石膏結晶變細,造成在分離步驟(S1)時取得含有游離水之高純度二水石膏變的困難。In the reaction step R1, the ammonium sulfate or ammonium sulfate solution recovered from the industry does not need to be restricted to a specific saturation concentration to carry out the metathesis reaction, but it is recommended to add water to adjust the concentration of the ammonium sulfate solution to be 5%. 40%, the optimum concentration is 10% to 30%, because if the concentration of ammonium sulfate solution is too low, the space required for the reaction equipment is large. If the concentration of ammonium sulfate solution is too high, exceeds the saturation solubility, the metathesis reaction efficiency becomes low, and The gypsum crystals become fine, which makes it difficult to obtain high-purity dihydrate gypsum containing free water in the separation step (S1).
另外,鈣的氧化物較佳使用氧化鈣(CaO),氫氧化物較佳使用氫氧化鈣(Ca(OH)2 ),純度愈高愈好,氧化鈣(CaO)或氫氧化鈣(Ca(OH)2 )之純度最佳90%以上,因為若氧化鈣(CaO)或氫氧化鈣(Ca(OH)2 )的純度過低,生產的石膏純度會降低,氧化鈣(CaO)或氫氧化鈣(Ca(OH)2 )可以單獨使用或混合使用,而且可以使用固態或配成漿狀,其中較佳的選擇是將氧化鈣(CaO)或氫氧化鈣(Ca(OH)2 )配成漿狀,如此可將氧化鈣消化生成氫氧化鈣,而且易於使用幫浦輸送,氧化鈣(CaO)或氫氧化鈣(Ca(OH)2 )漿狀的濃度沒有特別限制,一般濃度為10%~40%,最佳濃度為20%~30%。Further, calcium oxide is preferably calcium oxide (CaO), and hydroxide is preferably calcium hydroxide (Ca(OH) 2 ). The higher the purity, the better, calcium oxide (CaO) or calcium hydroxide (Ca ( OH) 2 ) the purity is better than 90%, because if the purity of calcium oxide (CaO) or calcium hydroxide (Ca(OH) 2 ) is too low, the purity of the produced gypsum will decrease, calcium oxide (CaO) or hydroxide Calcium (Ca(OH) 2 ) may be used singly or in combination, and may be used in a solid form or in a slurry form, and a preferred option is to formulate calcium oxide (CaO) or calcium hydroxide (Ca(OH) 2 ). It is slurried, so that calcium oxide can be digested to form calcium hydroxide, and it is easy to use pump delivery. The concentration of calcium oxide (CaO) or calcium hydroxide (Ca(OH) 2 ) is not particularly limited, and the concentration is generally 10%. ~40%, the best concentration is 20%~30%.
本創作方法在反應步驟R1中進行複分解反應的理論摩爾比為1:1,反應時摩爾比沒有特別限制,但為使硫酸銨轉化成氨的效率提高,硫酸銨與氧化鈣或氫氧化鈣之摩爾比一般設定在1:1~1:1.2之間,摩爾比過高表示硫酸銨過量,沒有反應的硫酸銨增多,反應後溶液內之可溶性銨含量增加,對於銨-氮排放管制不利,摩爾比過低表示鈣的氧化物及/或氫氧化物過量,沒有反應的鈣的氧化物及/或氫氧化物增多,對於後續的水化步驟,必須增加中和時酸的用量,對操作與成本不利。The theoretical molar ratio of the metathesis reaction in the reaction step R1 is 1:1, and the molar ratio at the time of the reaction is not particularly limited, but the efficiency of converting ammonium sulfate into ammonia is improved, and ammonium sulfate and calcium oxide or calcium hydroxide are used. The molar ratio is generally set between 1:1 and 1:1.2. If the molar ratio is too high, the ammonium sulfate is excessive, and the unreacted ammonium sulfate is increased. The soluble ammonium content in the solution increases after the reaction, which is unfavorable for the ammonium-nitrogen emission control. If the ratio is too low, the calcium oxide and/or hydroxide is excessive, and the unreacted calcium oxide and/or hydroxide is increased. For the subsequent hydration step, the amount of acid during neutralization must be increased. The cost is unfavorable.
本創作方法在反應步驟R1中為增加複分解反應速率,可以進一步添加適量的鹼金屬氫氧化物,鹼金屬氫氧化物為氫氧化鈉、氫氧化鉀的其中任意一種,且鹼金屬氫氧化物可以使用液狀或固狀型態,當鹼金屬氫氧化物配成液狀時,該液狀的鹼金屬氫氧化物濃度沒有特別限制,約設定在45%~55%,最佳的飽和濃度在50%,使用量可以跟氧化鈣(CaO)或氫氧化鈣(Ca(OH)2 )的使用量配合,使硫酸銨與鈣的氧化物、氫氧化物之任意至少一者再加上氫氧化鈉或氫氧化鉀後的摩爾比維持在1:1-1:1.2之間。又,反應步驟的反應溫度沒有特別限制,一般為20℃至120℃,最佳為50℃-110℃。以及反應時間沒有特別限制,溫度低,反應時間增長,相反的溫度高,反應時間減少,一般為0.5-4小時,最佳為1-3小時。反應壓力一般為常壓(1大氣壓力),但為使反應溫度更高,可以提高壓力至常壓(1大氣壓力)以上。In the reaction step R1, in order to increase the metathesis reaction rate, an appropriate amount of an alkali metal hydroxide may be further added, and the alkali metal hydroxide is any one of sodium hydroxide and potassium hydroxide, and the alkali metal hydroxide may be When the alkali metal hydroxide is formulated into a liquid state, the liquid alkali metal hydroxide concentration is not particularly limited, and is set at about 45% to 55%, and the optimum saturation concentration is in the liquid state or the solid state. 50%, the amount can be used in combination with the amount of calcium oxide (CaO) or calcium hydroxide (Ca(OH) 2 ) to add at least one of ammonium sulfate and calcium oxides and hydroxides to the hydroxide. The molar ratio after sodium or potassium hydroxide is maintained between 1:1 and 1:1.2. Further, the reaction temperature in the reaction step is not particularly limited and is usually from 20 ° C to 120 ° C, preferably from 50 ° C to 110 ° C. The reaction time is not particularly limited, the temperature is low, the reaction time is increased, the opposite temperature is high, and the reaction time is decreased, and is usually 0.5 to 4 hours, preferably 1-3 hours. The reaction pressure is generally normal pressure (1 atmosphere), but in order to make the reaction temperature higher, the pressure can be increased to a normal pressure (1 atmosphere) or more.
本創作方法在反應步驟R1中進行複分解反應而生成氨與石膏的混合物,如為進一步分離氨與石膏,可以利用已知的物理方法,如蒸餾、汽提(氣提)等方式,將氨汽自混合溶液中分離出來,再利用水將氨汽吸收下來的方式得到氨水溶液。The present method performs a metathesis reaction in the reaction step R1 to form a mixture of ammonia and gypsum. For further separation of ammonia and gypsum, the ammonia vapor can be removed by a known physical method such as distillation, stripping (gas stripping), and the like. The aqueous ammonia solution is obtained by separating it from the mixed solution and then using water to absorb the ammonia vapor.
本創作方法在調均步驟R2中,對於來自反應步驟R1產生的去除氨之石膏混合溶液中加入硫酸、硝酸、鹽酸、磷酸等其他酸的其中任意一種,將去除氨之石膏混合溶液中未反應之鈣的氧化物及/或氫氧化物轉化為石膏,及/或將鹼金屬氫氧化物轉化成可溶性鈣鹽(例如硝酸鈣、氯化鈣、磷酸鈣、硫酸鈉、硫酸鉀等)。如不加入硫酸或其他酸,未反應之鈣的氧化物及/或氫氧化物會降低後續的水化步驟R3之水化效率與二水石膏純度。硫酸或其他酸的使用濃度沒有特別限制,去除氨之石膏混合溶液的PH值一般的控制範圍為1-10,最佳為4-6,PH值太低會造成遊離酸過多,對水洗不好,PH值太高造成鈣的氧化物及/或氫氧化物的溶解性不好。In the tempering step R2, any one of sulfuric acid, nitric acid, hydrochloric acid, phosphoric acid or the like is added to the ammonia-removing gypsum mixed solution generated from the reaction step R1, and the ammonia-free gypsum mixed solution is not reacted. The calcium oxides and/or hydroxides are converted to gypsum and/or the alkali metal hydroxide is converted to a soluble calcium salt (eg, calcium nitrate, calcium chloride, calcium phosphate, sodium sulfate, potassium sulfate, etc.). If no sulfuric acid or other acid is added, the unreacted calcium oxides and/or hydroxides reduce the hydration efficiency of the subsequent hydration step R3 and the purity of the dihydrate gypsum. The concentration of sulfuric acid or other acid used is not particularly limited. The pH of the ammonia-depleted mixed solution is generally controlled in the range of 1-10, preferably 4-6. If the pH is too low, the free acid will be too much, and the washing will not be good. If the pH is too high, the solubility of calcium oxides and/or hydroxides is not good.
本創作方法在水化步驟R3中,如果含高純度二水石膏的溶液沒有適當的操作控制,得到的石膏型態,可能同時含有二水石膏(CaSO4 2H2 O)、半水石膏(CaSO4 1/2H2 O)或無水石膏(CaSO4 )等一種或二種以上的結晶型態。如要得到常溫下穩定的二水石膏結晶型態,必須在適當的操作濃度、溫度、與水化時間條件下進行石膏的水化反應,才能讓石膏全部轉化生成純度高的二水石膏及二水結晶型態。一般操作上反應步驟R1的溫度比水化溫度要高約高5℃~30℃,使去除氨之石膏混合溶液內的石膏在反應步驟R1生成半水或無水石膏,再於水化步驟R3控制較低於反應步驟R1的溫度,使半水或無水石膏慢慢水化轉成二水石膏。其中水化步驟R3的溫度並沒有特別限制,一般為20℃至120℃且最佳為30℃~100℃但水化步驟R3溫度需低於反應步驟溫度。水化步驟的反應時間沒有特別限制,一般為0.5-4小時,最佳為2-4小時。水化時可加入二水石膏晶種,促進水化及二水結晶生成之速度,二水石膏晶種的加入量一般為去除氨之石膏混合溶液之重量0.1%~5.0%,最佳為去除氨之石膏混合溶液之重量的0.5%~2.0%。In the hydration step R3, if the solution containing high-purity dihydrate gypsum is not properly controlled, the obtained gypsum form may contain both dihydrate gypsum (CaSO 4 2H 2 O) and hemihydrate gypsum (CaSO). One or more crystalline forms such as 4 1/2H 2 O) or anhydrite (CaSO 4 ). In order to obtain the crystalline form of dihydrate gypsum which is stable at room temperature, the hydration reaction of gypsum must be carried out under the appropriate operating concentration, temperature and hydration time, in order to completely convert the gypsum into high-purity dihydrate gypsum and Water crystal form. Generally, the temperature of the reaction step R1 is higher than the hydration temperature by about 5 ° C to 30 ° C, so that the gypsum in the ammonia-depleted gypsum mixed solution generates semi-aqueous or anhydrous gypsum in the reaction step R1, and then controlled in the hydration step R3. Lower than the temperature of the reaction step R1, the semi-aqueous or anhydrite is slowly hydrated to dihydrate gypsum. The temperature of the hydration step R3 is not particularly limited, and is generally 20 ° C to 120 ° C and most preferably 30 ° C to 100 ° C. However, the hydration step R 3 temperature is lower than the reaction step temperature. The reaction time of the hydration step is not particularly limited and is usually from 0.5 to 4 hours, preferably from 2 to 4 hours. When hydration, the dihydrate gypsum seed crystal can be added to promote the hydration and the formation rate of the dihydrate crystal. The amount of the dihydrate gypsum seed crystal is generally 0.1% to 5.0% of the weight of the ammonia-removing gypsum mixed solution, and the best is removed. The weight of the ammonia gypsum mixed solution is 0.5% to 2.0%.
本創作方法在分離步驟S1中,自水化步驟R3得到的含高純度二水石膏溶液,可以利用固-液分離設備,例如離心機、壓濾機等,將二水石膏分離出來,分離出的二水石膏內含有游離水,也可能含有未反應的硫酸銨或可溶性鈣鹽等雜質,此時可以使用水洗,將雜質水洗掉,得到純度高的產品直接出售或進行乾燥後出售。In the separation step S1, the high-purity dihydrate gypsum solution obtained from the hydration step R3 can be separated by using a solid-liquid separation device such as a centrifuge or a filter press to separate the gypsum. The dihydrate gypsum contains free water and may contain unreacted ammonium sulfate or soluble calcium salt. In this case, the water may be washed with water to wash off the impurities, and the product having high purity may be directly sold or dried and sold.
本創作方法在乾燥步驟D1中,自分離步驟S1得到的二水石膏,如果需要的規格對游離水份或結晶水之含量有限制,可以利用乾燥設備例如烘箱、氣流式乾燥機、真空乾燥機等,去除游離水或去除結晶水,生產不同石膏結晶型態的產品,例如含二水、半水、或無水的石膏產品,詳細地說將二水石膏快速加入至80。 C以上一段時間,可以使二水石膏轉化成半水石膏,再將半水石膏持續於80。 C以上加熱一段時間後,半水石膏就會轉化成無水石膏。In the drying step D1, the dihydrate gypsum obtained from the separation step S1, if the required specification has a limit on the content of free water or crystal water, may use drying equipment such as an oven, a gas flow dryer, a vacuum dryer. Etc., remove free water or remove crystal water to produce products of different gypsum crystalline forms, such as gypsum products containing dihydrate, semi-water, or anhydrous, and in detail, the dihydrate gypsum is quickly added to 80 . For a period of time above C, the dihydrate gypsum can be converted into hemihydrate gypsum, and the hemihydrate gypsum can be continued at 80 . After heating for a period of time above C, the hemihydrate gypsum is converted into anhydrite.
配合參看第2圖所示,本創作自工業中回收的硫酸銨製造二水石膏的方法,其實施例流程係以一個硫酸銨貯槽20存放自工業回收的硫酸銨或硫酸銨溶液,並且在一個氧化鈣或氫氧化鈣漿液貯槽22中所存放的氧化鈣或氫氧化鈣漿液,而且在一鹼金屬氫氧化物貯槽24中所存放鹼金屬氫氧化物,並且將硫酸銨液貯槽20中的硫酸銨或硫酸銨溶液調整至濃度介於5%~40%之間,將氧化鈣或氧化鈣漿液槽22中的氧化鈣或氧化鈣漿濃度調整至10%~40%,將鹼金屬氫氧化物貯槽24之飽和濃度調整至約50%,再將硫酸銨與氧化鈣或氫氧化鈣漿以摩爾比1:1~1:1.2的比例混合進入一反應槽25進行複分解反應,或者將硫酸銨與氧化鈣或氫氧化鈣漿加入鹼金屬氫氧化物後之摩爾比1:1~1:1.2的比例混合進入反應槽25,因而在反應槽25中生成氨與石膏的混合溶液,反應期間加入水32調整濃度維持在5%~40%之間,反應結束後,利用蒸餾或汽提(氣提)等方式進行除氨,氨汽28自反應槽分離出來之後,以水吸收製成氨水,送至一個氨水貯槽28A內,就能獲得去除氨之石膏混合溶液,再將去除氨之石膏混合溶液26送入一調均槽33中,並且在調均槽33中加入硫酸或其他酸34,將去除氨之石膏混合溶液調整至PH值介於1~10之間,而在調均槽33中獲得調均後混合液之後,將調均後混合液30送入一水化槽35,並且加入二水石膏晶種36進行水化,因而在水化槽35中獲得含高純度二水石膏的溶液,進一步將含高純度二水石膏的溶液38送入諸如離心機或壓濾機所構成的一分離設備39中,分離含有游離水的高純度二水石膏42與濾液40,濾液40進入廢水區處理,含有游離水的二水石膏42則送入諸如烘箱、氣流式乾燥機、真空乾燥機所構成之一乾燥設備43進行乾燥得到乾燥的二水石膏44產品。Referring to Fig. 2, the method for producing dihydrate gypsum from ammonium sulfate recovered from the industry is carried out in an ammonium sulfate storage tank 20 from an industrially recovered ammonium sulfate or ammonium sulfate solution, and in one Calcium oxide or calcium hydroxide slurry stored in the calcium oxide or calcium hydroxide slurry storage tank 22, and alkali metal hydroxide stored in an alkali metal hydroxide storage tank 24, and sulfuric acid in the ammonium sulfate liquid storage tank 20 The ammonium or ammonium sulfate solution is adjusted to a concentration of between 5% and 40%, and the calcium oxide or calcium oxide slurry concentration in the calcium oxide or calcium oxide slurry tank 22 is adjusted to 10% to 40%, and the alkali metal hydroxide is used. The saturation concentration of the storage tank 24 is adjusted to about 50%, and the ammonium sulfate and the calcium oxide or calcium hydroxide slurry are mixed in a molar ratio of 1:1 to 1:1.2 into a reaction tank 25 for metathesis reaction, or ammonium sulfate and Calcium oxide or calcium hydroxide slurry is added to the reaction tank 25 at a molar ratio of 1:1 to 1:1.2 after adding an alkali metal hydroxide, thereby forming a mixed solution of ammonia and gypsum in the reaction tank 25, and reacting The concentration of water 32 is maintained between 5% and 40%. After the reaction is completed, ammonia is removed by distillation or stripping (gas stripping), and ammonia vapor 28 is separated from the reaction tank and then made by water absorption. The ammonia water is sent to an ammonia water storage tank 28A to obtain a mixed solution of the ammonia-removing gypsum, and then the ammonia-removing gypsum mixed solution 26 is sent to the uniform tank 33, and sulfuric acid or other acid is added to the adjusting tank 33. 34, the ammonia removal gypsum mixed solution is adjusted to a pH between 1 and 10, and after the adjusted average mixed solution is obtained in the equalization tank 33, the adjusted mixed liquid 30 is sent to the hydration tank 35. And adding the dihydrate gypsum seed crystal 36 for hydration, thereby obtaining a solution containing high-purity dihydrate gypsum in the hydration tank 35, and further feeding the solution 38 containing high-purity dihydrate gypsum to a centrifuge or a filter press, for example. In a separating device 39, a high-purity dihydrate gypsum 42 containing free water and a filtrate 40 are separated, and the filtrate 40 is treated in a waste water zone, and the dihydrate gypsum 42 containing free water is sent to, for example, baked. , Air dryer, a vacuum dryer drying apparatus 43 constitutes one of the dried gypsum 44 to obtain dried products.
本創作係依據上述製造二水石膏的方法及其設備假設符合所述之方法的條件下的實例作說明,但請瞭解本創作並不為具體實施例所述之條件及內容所限:This creation is based on the above examples of the method for manufacturing dihydrate gypsum and its equipment, assuming that the method is in accordance with the method described, but it is understood that the creation is not limited by the conditions and contents described in the specific examples:
實施例1:來自半導體產業產生之硫酸銨廢液(NH4 )2 SO4 ,將濃度調至30%,稱取1000g且濃度為30%的硫酸銨廢液加入容量為1.5L的反應槽內,接著加入190g且純度為95%的氫氧化鈣,進行複分解反應,反應溫度控制在95-100℃之間,反應約2小時,反應時產生的氨汽使用冷凝器收集下來,反應期間,一方面補充水進入反應器以維持反應槽內的溶液體積,一方面將反應器內產生的氨趕出去,等產生的氨全部趕出後,加入飽和濃度98%硫酸溶液至反應槽內,調整反應槽內之溶液的PH值至6左右,然後在水化槽35中降低溫度至50℃~60℃之間,並且加入5g二水石膏當作晶種,維持50-60℃進行二水石膏的水化反應,水化反應結束後,進行過濾水洗,得到白色的二水石膏,利用600倍的光學顯微鏡,看到呈菱柱狀的二水石膏結晶型態,測定CaSO4. 2H2 O純度為95.1%。Example 1: Ammonium sulfate waste liquid (NH 4 ) 2 SO 4 produced from the semiconductor industry, the concentration was adjusted to 30%, and 1000 g of ammonium sulfate waste liquid having a concentration of 30% was weighed into a reaction tank having a capacity of 1.5 L. Then, 190 g of calcium hydroxide having a purity of 95% is added to carry out a metathesis reaction, the reaction temperature is controlled between 95 and 100 ° C, and the reaction is carried out for about 2 hours. The ammonia vapor generated during the reaction is collected by using a condenser during the reaction. In addition, the supplementary water enters the reactor to maintain the volume of the solution in the reaction tank. On the one hand, the ammonia generated in the reactor is driven out, and after the ammonia generated is completely driven out, a saturated concentration of 98% sulfuric acid solution is added to the reaction tank to adjust the reaction. The pH of the solution in the tank is about 6, then the temperature is lowered to between 50 ° C and 60 ° C in the hydration tank 35, and 5 g of dihydrate gypsum is added as a seed crystal, and the dihydrate gypsum is maintained at 50-60 ° C. After the hydration reaction and the hydration reaction, the mixture was filtered and washed with water to obtain white dihydrate gypsum. The crystal form of the dihydrate gypsum in the shape of a column was observed by a 600-fold optical microscope, and the purity of CaSO 4. 2H 2 O was measured . It is 95.1%.
實施例2:來自半導體產業產生之硫酸銨廢液(NH4 )2 SO4 ,將濃度調至20%,稱取1000g濃度為20%的硫酸銨廢液加入容量為1.5L的反應槽內,接著加入純度為95%氫氧化鈣125g,進行複分解反應,反應溫度控制在95-100℃之間,反應約2小時,反應時產生的氨汽使用冷凝器收集下來,等產生的氨全部趕出後,加入濃度為98%硫酸溶液至反應槽內,調整反應槽內的溶液PH值至6左右之後,再加入300g的水,然後在水化槽35中降低溫度至50℃~60℃之間,並且加入3g二水石膏當作晶種,維持50-60℃進行二水石膏的水化反應,水化反應結束後,進行過濾水洗,得到白色的二水石膏,利用600倍的光學顯微鏡,看到菱柱狀的二水石膏結晶型態,測定CaSO4. 2H2 O純度為96.2%。Example 2: Ammonium sulfate waste liquid (NH 4 ) 2 SO 4 produced from the semiconductor industry, the concentration was adjusted to 20%, and 1000 g of a 20% ammonium sulfate waste liquid was weighed into a reaction tank having a capacity of 1.5 L. Then, 125 g of calcium hydroxide having a purity of 95% is added to carry out a metathesis reaction, the reaction temperature is controlled between 95 and 100 ° C, and the reaction is carried out for about 2 hours. The ammonia vapor generated during the reaction is collected by using a condenser, and the ammonia generated is all driven out. Thereafter, a 98% sulfuric acid solution is added to the reaction tank, and the pH of the solution in the reaction tank is adjusted to about 6, and then 300 g of water is added, and then the temperature is lowered in the hydration tank 35 to between 50 ° C and 60 ° C. And adding 3 g of dihydrate gypsum as a seed crystal, maintaining the hydration reaction of dihydrate gypsum at 50-60 ° C, and after hydration reaction, washing with water to obtain white dihydrate gypsum, using a 600-fold optical microscope, The crystal form of the rhombohedral dihydrate gypsum was observed, and the purity of CaSO 4. 2H 2 O was determined to be 96.2%.
實施例3:來自半導體產業產生之硫酸銨廢液(NH4 )2 SO4 ,調至濃度為20%,稱取1000g濃度為20%的硫酸銨廢液加入容量為1.5L的反應槽內,接著加入純度95%氫氧化鈣110g,及濃度為45%氫氧化鈉20g,進行複分解反應,反應溫度控制在95-100℃,反應約2小時,反應時產生的氨汽使用冷凝器收集下來,等產生的氨全部趕出後,加入濃度為98%硫酸溶液至反應槽內,調整反應槽內的溶液PH值至5左右之後,再加入250g的水,然後在水化槽35中降低溫度至50℃~60℃之間,並且加入3g二水石膏當作晶種,維持50-60℃進行二水石膏的水化反應,水化反應結束後,進行過濾水洗,得到白色的二水石膏,利用600倍的光學顯微鏡,看到菱柱狀的二水石膏結晶型態,測定CaSO4. 2H2 O純度為95.4%。Example 3: Ammonium sulfate waste liquid (NH 4 ) 2 SO 4 produced from the semiconductor industry was adjusted to a concentration of 20%, and 1000 g of a 20% ammonium sulfate waste liquid was weighed into a reaction tank having a capacity of 1.5 L. Then, 110 g of purity 95% calcium hydroxide and 20 g of 45% sodium hydroxide were added to carry out a metathesis reaction, the reaction temperature was controlled at 95-100 ° C, and the reaction was carried out for about 2 hours, and the ammonia vapor generated during the reaction was collected using a condenser. After all the ammonia generated is ejected, a 98% sulfuric acid solution is added to the reaction tank, and the pH of the solution in the reaction tank is adjusted to about 5, and then 250 g of water is added, and then the temperature is lowered in the hydration tank 35. Between 50 ° C and 60 ° C, and adding 3 g of dihydrate gypsum as a seed crystal, maintaining the hydration reaction of dihydrate gypsum at 50-60 ° C, after the hydration reaction is finished, filtering and washing with water to obtain white dihydrate gypsum. The crystal form of the columnar dihydrate gypsum was observed by a 600-fold optical microscope, and the purity of CaSO 4. 2H 2 O was determined to be 95.4%.
本創作自硫酸銨中製造二水石膏的方法,可以得到純度高的二水石膏,而且依據能夠控制乾燥時間而獲得不同結晶狀態的石膏(二水石膏、半水石膏或無水石膏),以及獲得高純度二水石膏的同時能夠回收氨水,如此提高回收硫酸銨廢液的經濟價值。The method for producing dihydrate gypsum from ammonium sulfate can obtain dihydrate gypsum with high purity, and obtain gypsum (dihydrate gypsum, hemihydrate gypsum or anhydrite gypsum) of different crystal state according to the drying time, and obtain High-purity dihydrate gypsum can recover ammonia water at the same time, thus improving the economic value of recovering ammonium sulfate waste liquid.
本創作的基本教導已加以說明,對具有本領域通常技能的人而言,許多延伸和變化將是顯而易知者。舉例言之,例如本創作製造二水石膏的方法可以不包括乾燥步驟,也就是說,在分離步驟所得之含有游離水的高純度二水石膏就能夠直接被應用,乾燥步驟只是進一步去除游離水或結晶水,使二水石膏的水分更低,或者進一步將含有游離水的高純度二水石膏製成半水石膏或無水石膏。The basic teachings of this creation have been described, and many extensions and variations will be apparent to those of ordinary skill in the art. For example, for example, the method for producing dihydrate gypsum may not include a drying step, that is, the high-purity dihydrate gypsum containing free water obtained in the separation step can be directly applied, and the drying step is only to further remove free water. Or crystallizing water to make the water of dihydrate gypsum lower, or further to make high-purity dihydrate gypsum containing free water into hemihydrate gypsum or anhydrite gypsum.
本說明書揭示內容,可在未脫離本創作精神或大體特徵的其它特定程序來實施,且這些特定程序的一些形式已經被指出,所以,本說明書揭示的實施例應視為舉例說明而非限制。本創作的範圍是由所附之申請專利範圍界定,而不是由上述說明所界定,對於落入申請專利範圍的均等意義與範圍的所有改變仍將包含在其範圍之內。
The disclosure of the present invention may be embodied in other specific forms without departing from the spirit and scope of the invention. The scope of the present invention is defined by the scope of the appended claims, and is not intended to be limited by the scope of the invention.
R1‧‧‧反應步驟 R1‧‧‧ reaction steps
R2‧‧‧調均步驟 R2‧‧‧ adjustment steps
R3‧‧‧二水石膏水化步驟 R3‧‧‧dihydrate gypsum hydration step
S1‧‧‧二水石膏分離步驟 S1‧‧‧ Dihydrate gypsum separation step
D1‧‧‧二水石膏乾燥步驟 D1‧‧‧ Dihydrate gypsum drying step
Claims (22)
反應步驟,將硫酸銨或硫酸銨溶液在20。 C~120。 C的溫度下與鈣的氧化物及/或氫氧化物及進行複分解反應,生成氨與石膏的混合物,然後利用物理方法將氨自氨與石膏的混合物中分離出來並加以收集而得到氨水與去除氨之石膏混合液;
調均步驟,在去除氨之石膏混合溶液加入硫酸或其他酸,將去除氨之石膏混合溶液中未反應之鈣的氧化物及/或氫氧化物,轉化成石膏或可溶性鈣鹽;
水化步驟,將調均後溶液在20。 C~120。 C且低於反應步驟之溫度的條件下進行石膏的水化反應,生成純度高的二水石膏,進一步獲得含高純度二水石膏的溶液;
分離步驟,將含高純度二水石膏的溶液,利用分離設備,分離出含有游離水的高純度二水石膏。A method for recovering dihydrate gypsum from ammonium sulfate, comprising:
In the reaction step, the ammonium sulfate or ammonium sulfate solution is at 20 . C~120 . At a temperature of C, it reacts with calcium oxides and/or hydroxides to form a mixture of ammonia and gypsum, and then physically separates ammonia from the mixture of ammonia and gypsum and collects it to obtain ammonia water and remove it. A mixture of ammonia gypsum;
Adjusting the average step, adding sulfuric acid or other acid in the ammonia-removing gypsum mixed solution, and removing the unreacted calcium oxides and/or hydroxides in the ammonia-gypsum mixed solution to be converted into gypsum or soluble calcium salt;
In the hydration step, the solution will be adjusted to 20 after homogenization . C~120 . And hydrating the gypsum under conditions of a temperature lower than the temperature of the reaction step to form a dihydrate gypsum having a high purity, and further obtaining a solution containing high-purity dihydrate gypsum;
In the separation step, a solution containing high-purity dihydrate gypsum is separated into high-purity dihydrate gypsum containing free water by using a separation device.
反應步驟,回收硫酸銨或硫酸銨溶液與鈣的氧化物、氫氧化鈉或氫氧化鉀的其中任意至少一種進行複分解反應,生成氨與石膏的混合物,然後利用物理方法將氨自混合溶液中分離出來得到氨水與去除氨之石膏混合液,並將去除氨之石膏混合液中硫酸銨或硫酸銨溶液之濃度調整為5%-40%之後,加入純度90%以上之鈣的氧化物及/或氫氧化物,硫酸銨相較於與 鈣的氧化物、氫氧化鈉或氫氧化鉀的其中任意至少一種進行複分解反應的理論摩爾比為1:1~1:1.2之間反應溫度為20℃至120℃,反應時間為0.5-4小時,反應壓力一般為常壓以上;
調均步驟,在去除氨之石膏混合液中加入硫酸、硝酸、鹽酸、磷酸的其中任意一種,而將PH值控在1~10之間,將溶液中未反應之鈣的氧化物轉化成石膏,或者將氫氧化鈉或氫氧化鉀轉化成可溶性鈣鹽而獲得調均後溶液;
水化步驟,在20℃~120℃且較反應步驟低5℃~30℃之間的溫度將調均後溶液重量之0.5%~5%的二水石膏晶種加入調均後溶液中,對調均後溶液進行石膏的水化反應,水化反應時間為0.5-4小時;
分離步驟,將含二水石膏的溶液,利用離心機或壓濾機,分離出含有游離水的二水石膏。
A method for recovering dihydrate gypsum from ammonium sulfate, comprising:
In the reaction step, the ammonium sulfate or ammonium sulfate solution is recovered and metathesized with at least one of calcium oxide, sodium hydroxide or potassium hydroxide to form a mixture of ammonia and gypsum, and then the ammonia is physically separated from the mixed solution. After obtaining a mixture of ammonia water and ammonia-removing gypsum, and adjusting the concentration of the ammonium sulfate or ammonium sulfate solution in the ammonia-removing gypsum mixture to 5%-40%, adding calcium oxide having a purity of 90% or more and/or The theoretical molar ratio of the hydroxide, ammonium sulfate phase to the metathesis reaction with any of the calcium oxide, sodium hydroxide or potassium hydroxide is 1:1 to 1:1.2 and the reaction temperature is 20 ° C to 120 ° C, the reaction time is 0.5-4 hours, the reaction pressure is generally above normal pressure;
In the adjustment step, any one of sulfuric acid, nitric acid, hydrochloric acid and phosphoric acid is added to the ammonia-removing gypsum mixture, and the pH is controlled between 1 and 10, and the unreacted calcium oxide in the solution is converted into gypsum. Or converting sodium hydroxide or potassium hydroxide into a soluble calcium salt to obtain a solution after adjustment;
The hydration step, in the temperature range of 20 ° C ~ 120 ° C and lower than the reaction step 5 ° C ~ 30 ° C, the average weight of the solution after the weight of 0.5% ~ 5% of the dihydrate gypsum seed crystals added to the solution after the adjustment, the adjustment The solution is subjected to hydration reaction of gypsum, and the hydration reaction time is 0.5-4 hours;
In the separation step, the solution containing dihydrate gypsum is separated from the gypsum containing free water by a centrifuge or a filter press.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
TW103114127A TWI535662B (en) | 2014-04-18 | 2014-04-18 | Method for recovering dihydrate gypsum from ammonium sulfate |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
TW103114127A TWI535662B (en) | 2014-04-18 | 2014-04-18 | Method for recovering dihydrate gypsum from ammonium sulfate |
Publications (2)
Publication Number | Publication Date |
---|---|
TW201540668A true TW201540668A (en) | 2015-11-01 |
TWI535662B TWI535662B (en) | 2016-06-01 |
Family
ID=55220357
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
TW103114127A TWI535662B (en) | 2014-04-18 | 2014-04-18 | Method for recovering dihydrate gypsum from ammonium sulfate |
Country Status (1)
Country | Link |
---|---|
TW (1) | TWI535662B (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN111569559A (en) * | 2020-05-23 | 2020-08-25 | 河北化工医药职业技术学院 | Waste gas purification dust-free environment-friendly gas leakage monitoring system of dihydrate gypsum production line |
CN111569526A (en) * | 2020-05-25 | 2020-08-25 | 河北化工医药职业技术学院 | Automatic lifting and filtering product system of dihydrate gypsum production line |
CN114262109A (en) * | 2021-11-03 | 2022-04-01 | 青川县青云上锰业有限公司 | Ammonia recovery method of low-concentration ammonium sulfate solution |
-
2014
- 2014-04-18 TW TW103114127A patent/TWI535662B/en active
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN111569559A (en) * | 2020-05-23 | 2020-08-25 | 河北化工医药职业技术学院 | Waste gas purification dust-free environment-friendly gas leakage monitoring system of dihydrate gypsum production line |
CN111569559B (en) * | 2020-05-23 | 2022-03-25 | 河北化工医药职业技术学院 | Waste gas purification dust-free environment-friendly gas leakage monitoring system of dihydrate gypsum production line |
CN111569526A (en) * | 2020-05-25 | 2020-08-25 | 河北化工医药职业技术学院 | Automatic lifting and filtering product system of dihydrate gypsum production line |
CN111569526B (en) * | 2020-05-25 | 2022-03-11 | 河北化工医药职业技术学院 | An automatic lifting and filtering product system of a dihydrate gypsum production line |
CN114262109A (en) * | 2021-11-03 | 2022-04-01 | 青川县青云上锰业有限公司 | Ammonia recovery method of low-concentration ammonium sulfate solution |
Also Published As
Publication number | Publication date |
---|---|
TWI535662B (en) | 2016-06-01 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN103874658B (en) | By the calcite of use gypsum production of high purity in next life and the method for ammonium sulfate | |
US4981664A (en) | Method of production of high purity silica and ammonium fluoride | |
CN101508447B (en) | Method for processing phosphogypsum | |
CN101870494A (en) | Method for recrystallization and purification of desulfurized gypsum | |
CN105600763B (en) | A kind of method that fluoride salt method of purification produces industrial monoammonium phosphate | |
WO1999065823A1 (en) | Method of procucing potassium sulfate | |
US5165907A (en) | Method of production of high purity silica and ammonium fluoride | |
CN101486481A (en) | Method for producing superfine light calcium carbonate and co-producing ammonium sulfate by using fluorgypsum | |
CN108455647B (en) | Method for producing calcium fluoride and by-products of white carbon black and ammonium sulfate by phosphoric acid by-product phosphogypsum and fluosilicic acid | |
TWI535662B (en) | Method for recovering dihydrate gypsum from ammonium sulfate | |
CN103663499B (en) | The method of Potassium monofluoride co-production of ultrafine white carbon black is prepared with phosphate fertilizer by-product ammonium silicofluoride | |
CN105002521B (en) | A kind of method that impurity magnesium in electrolytic manganese system is removed using fluorine-containing mineral | |
CN105000539A (en) | Method for producing potassium dihydrogen phosphate and potassium-ammonium dihydrogen phosphate through wet process phosphoric acid | |
CN1234596C (en) | Process for preparing fluorine compound and SiO2 from sodium fluosilicate | |
CN115676788B (en) | High-purity potassium dihydrogen phosphate and preparation method thereof | |
US2920938A (en) | Method for manufacture of aluminum fluoride | |
EP3126290A2 (en) | High purity synthetic fluorite and process for preparing the same | |
JP2864617B2 (en) | Process for producing hydrosilicofluoric acid, ammonium silicofluoride and high-purity silica | |
CN106241761B (en) | A kind of processing method of useless concentrated phosphoric acid | |
CN102869609B (en) | Preparation KNO 3polyhalite IMI method | |
CN111847384B (en) | Preparation method of anhydrous hydrogen fluoride | |
JPH0692247B2 (en) | Method for producing magnesium silicofluoride | |
CN115724453B (en) | Purification and recovery method of ferric phosphate mother liquor | |
KR20220169337A (en) | Recycling process of mixed acid containing hydrogen fluoride and acetic acid | |
CN107721464A (en) | A kind of phosphorus ore acid hydrolysis fluorinated tail gas is applied to the method for the high water-soluble rate fertilizer grade MAP of production |