CN102107887A - Ammonia gas recovery method, ammonium sulfate solution concentration measurement method and ammonium sulfate solution concentration control method - Google Patents
Ammonia gas recovery method, ammonium sulfate solution concentration measurement method and ammonium sulfate solution concentration control method Download PDFInfo
- Publication number
- CN102107887A CN102107887A CN 201010622614 CN201010622614A CN102107887A CN 102107887 A CN102107887 A CN 102107887A CN 201010622614 CN201010622614 CN 201010622614 CN 201010622614 A CN201010622614 A CN 201010622614A CN 102107887 A CN102107887 A CN 102107887A
- Authority
- CN
- China
- Prior art keywords
- ammonium sulfate
- sulfate solution
- concentration
- value
- ammonia
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 title claims abstract description 155
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 title claims abstract description 154
- 229910052921 ammonium sulfate Inorganic materials 0.000 title claims abstract description 154
- 235000011130 ammonium sulphate Nutrition 0.000 title claims abstract description 154
- 238000000034 method Methods 0.000 title claims abstract description 74
- 238000011084 recovery Methods 0.000 title claims abstract description 36
- 238000000691 measurement method Methods 0.000 title claims abstract description 9
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims abstract description 117
- 238000006243 chemical reaction Methods 0.000 claims abstract description 81
- 239000000376 reactant Substances 0.000 claims abstract description 58
- 229910021529 ammonia Inorganic materials 0.000 claims abstract description 50
- 239000007789 gas Substances 0.000 abstract description 34
- 239000002440 industrial waste Substances 0.000 abstract description 17
- 239000003337 fertilizer Substances 0.000 abstract description 6
- 239000002994 raw material Substances 0.000 abstract description 6
- 239000000126 substance Substances 0.000 abstract description 5
- 230000007547 defect Effects 0.000 abstract description 3
- 238000004519 manufacturing process Methods 0.000 abstract description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 2
- 238000003672 processing method Methods 0.000 abstract 1
- 239000002912 waste gas Substances 0.000 description 15
- 238000010586 diagram Methods 0.000 description 9
- 239000007788 liquid Substances 0.000 description 4
- 238000005507 spraying Methods 0.000 description 4
- 239000003153 chemical reaction reagent Substances 0.000 description 3
- 238000005259 measurement Methods 0.000 description 3
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 3
- 239000002351 wastewater Substances 0.000 description 3
- MGWGWNFMUOTEHG-UHFFFAOYSA-N 4-(3,5-dimethylphenyl)-1,3-thiazol-2-amine Chemical compound CC1=CC(C)=CC(C=2N=C(N)SC=2)=C1 MGWGWNFMUOTEHG-UHFFFAOYSA-N 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- JCXJVPUVTGWSNB-UHFFFAOYSA-N nitrogen dioxide Inorganic materials O=[N]=O JCXJVPUVTGWSNB-UHFFFAOYSA-N 0.000 description 2
- 238000011088 calibration curve Methods 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 238000005057 refrigeration Methods 0.000 description 1
- 238000001223 reverse osmosis Methods 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
Images
Landscapes
- Treating Waste Gases (AREA)
Abstract
Description
技术领域technical field
本发明系有关于一种氨气回收方法、硫酸铵溶液的浓度测量方法及硫酸铵溶液的浓度控制方法,特别是一种将氨气溶于高浓度硫酸产生高浓度硫酸铵的氨气回收方法、硫酸铵溶液的浓度测量方法及利用测量pH值或是pH值与导电度以获知硫酸铵溶液的浓度的方法。The present invention relates to an ammonia gas recovery method, a method for measuring the concentration of ammonium sulfate solution and a method for controlling the concentration of ammonium sulfate solution, in particular to a method for recovering ammonia gas by dissolving ammonia gas in high-concentration sulfuric acid to produce high-concentration ammonium sulfate , the method for measuring the concentration of ammonium sulfate solution and the method for obtaining the concentration of ammonium sulfate solution by measuring pH value or pH value and electrical conductivity.
背景技术Background technique
氨是许多产业及工业上的基础原料,包括石化业、冷冻业及肥料制造业,氨具有刺激性,且在工业安全卫生及环境保护均具有危险性,因此氨的妥善处理方式是极为重要的。Ammonia is a basic raw material in many industries and industries, including petrochemical industry, refrigeration industry and fertilizer manufacturing industry. Ammonia is irritating and dangerous in industrial safety, health and environmental protection. Therefore, proper handling of ammonia is extremely important .
目前,工业排放的含氨废气常以溶于水的方式处理,这是因为氨具有极高的溶解度,然而含氨的废水对环境有极大的污染性,并未完全解决问题。如需回收含氨废水,仍需繁琐的后续处理,如以高背压及逆渗透膜浓缩,虽达到环保目的,但所需的机台及支出不符成本。At present, ammonia-containing waste gas discharged from industry is often treated by dissolving in water, because ammonia has a very high solubility. However, ammonia-containing wastewater has great pollution to the environment and has not completely solved the problem. If it is necessary to recycle ammonia-containing wastewater, cumbersome follow-up treatment is still required, such as concentration with high back pressure and reverse osmosis membrane. Although the purpose of environmental protection is achieved, the required equipment and expenditure are not in line with the cost.
台湾专利申请号274057:含有氨气之废气的无害化处理方法,其揭露一种以氧化触媒将氨气分解成氮氧化物的处理方法,然而其分解出的二氧化氮是光化学烟雾的主反应物,排放出二氧化氮经再次反应可能造成空气的二次污染。Taiwan Patent Application No. 274057: Harmless treatment method for waste gas containing ammonia, which discloses a treatment method for decomposing ammonia gas into nitrogen oxides with an oxidation catalyst. However, the decomposed nitrogen dioxide is the main source of photochemical smog. The reactant, the nitrogen dioxide emitted by the reaction again may cause secondary pollution of the air.
发明内容Contents of the invention
有鉴于此,本发明之目的就是在于提供一种氨气回收方法、硫酸铵溶液的浓度测量方法及硫酸铵溶液的浓度控制方法,以提供一种将氨气合成为高浓度硫酸铵的氨气回收方法、硫酸铵溶液的浓度测量方法及硫酸铵溶液的浓度控制方法,以解决习知技艺中产生大量含氨废水或回收处理过程繁琐的问题。In view of this, the purpose of the present invention is exactly to provide a kind of ammonia recovery method, the concentration measurement method of ammonium sulfate solution and the concentration control method of ammonium sulfate solution, to provide a kind of ammonia gas that ammonia gas is synthesized into high-concentration ammonium sulfate The recovery method, the concentration measurement method of the ammonium sulfate solution and the concentration control method of the ammonium sulfate solution are used to solve the problems in the prior art that a large amount of ammonia-containing waste water is generated or the recycling process is cumbersome.
根据本发明的目的,提出一种氨气回收方法,其包含以下步骤:According to the purpose of the present invention, propose a kind of ammonia recovery method, it comprises the following steps:
步骤一:提供重量百分浓度介于1%~98%的第一硫酸溶液作为反应剂;及Step 1: providing a first sulfuric acid solution with a concentration of 1% to 98% by weight as a reactant; and
步骤二:使氨气与该反应剂反应,产生重量百分浓度介于1%~73%的硫酸铵溶液。Step 2: making ammonia gas react with the reactant to produce an ammonium sulfate solution with a weight percent concentration of 1% to 73%.
上述步骤二所述使氨气与该反应剂反应,系先使氨气与该反应剂反应产生硫酸铵,直至硫酸铵的pH值达一设定值,然后再持续导入氨气与反应剂,并维持硫酸铵的pH值为该设定值,同时硫酸铵持续导出,以形成一连续式反应。The reaction of the ammonia gas and the reactant described in the
其中,本发明的氨气回收方法较佳为可包含步骤三:于反应剂中分次添加一第二硫酸溶液。产生的硫酸铵溶液的重量百分浓度较佳为25%。硫酸铵的pH值可作为控制反应终了的判断依据,较佳为在pH值为7时到达反应终点。Wherein, the method for recovering ammonia gas of the present invention preferably includes step 3: adding a second sulfuric acid solution to the reactant in batches. The weight percent concentration of the resulting ammonium sulfate solution is preferably 25%. The pH value of ammonium sulfate can be used as the basis for judging the end of the control reaction, preferably reaching the end of the reaction when the pH value is 7.
根据本发明的另一目的,提出一种硫酸铵溶液的浓度测量方法,其藉由测量硫酸铵溶液的pH值以判断硫酸铵溶液的重量百分浓度是否符合一默认值,硫酸铵溶液系以氨气与重量百分浓度介于1%~98%的硫酸溶液反应生成。According to another object of the present invention, a kind of concentration measuring method of ammonium sulfate solution is proposed, and it judges whether the weight percent concentration of ammonium sulfate solution meets a default value by measuring the pH value of ammonium sulfate solution, and ammonium sulfate solution is The ammonia gas reacts with a sulfuric acid solution with a concentration of 1% to 98% by weight to form it.
根据本发明的再一目的,提出一种硫酸铵溶液的浓度测量方法,系先测量或控制硫酸铵溶液的pH值,使其符合一设定值,然后藉由测量硫酸铵溶液的导电度以判断硫酸铵溶液的重量百分浓度,其中硫酸铵溶液系以氨气与重量百分浓度介于1%~98%的硫酸溶液反应生成。According to another object of the present invention, a kind of concentration measurement method of ammonium sulfate solution is proposed, system measures or controls the pH value of ammonium sulfate solution earlier, makes it meet a set value, then by measuring the conductivity of ammonium sulfate solution with Judging the weight percent concentration of the ammonium sulfate solution, wherein the ammonium sulfate solution is formed by reacting ammonia gas with a sulfuric acid solution with a weight percent concentration ranging from 1% to 98%.
根据本发明的再一目的,提出一种硫酸铵溶液的浓度控制方法,其硫酸铵溶液系以氨气与重量百分浓度介于1%~98%的硫酸溶液反应生成,藉由控制硫酸溶液中之硫酸量,以控制该硫酸铵溶液的浓度。According to still another object of the present invention, a kind of concentration control method of ammonium sulfate solution is proposed, and its ammonium sulfate solution is generated by the reaction of ammonia gas and a sulfuric acid solution with a concentration of 1% to 98% by weight. The amount of sulfuric acid in the solution to control the concentration of the ammonium sulfate solution.
承上所述,因依本发明的氨气回收方法、硫酸铵溶液的浓度测量方法及硫酸铵溶液的浓度控制方法,具有以下功效:Succeeding from the above, because of the concentration measurement method and the concentration control method of ammonium sulfate solution according to ammonia recovery method of the present invention, ammonium sulfate solution, have following effect:
(1)本发明的氨气回收方法,其回收处理所产生的硫酸铵可作为化学肥料的原料,藉此能达到避免含氨污染物排放之目的。(1) In the ammonia recovery method of the present invention, the ammonium sulfate produced by its recovery process can be used as a raw material for chemical fertilizers, thereby avoiding the discharge of ammonia-containing pollutants.
(2)本发明的氨气回收方法,其可包含分次添加第二硫酸溶液的步骤,藉此可维持硫酸浓度不至于太高而造成硫酸逸散之问题。(2) The ammonia gas recovery method of the present invention may include the step of adding the second sulfuric acid solution in stages, thereby maintaining the concentration of sulfuric acid so as not to cause the problem of sulfuric acid escape.
(3)本发明的氨气回收方法,其可包含将反应剂分散为细小液滴的步骤,藉此可增加反应剂及氨气的接触面积,加速反应。(3) The ammonia gas recovery method of the present invention may include the step of dispersing the reactant into fine droplets, thereby increasing the contact area between the reactant and the ammonia gas and accelerating the reaction.
(4)本发明的硫酸铵溶液的浓度测量方法,藉由测量硫酸铵溶液的pH值即可判断硫酸铵溶液的重量百分浓度,测量简单快速且准确。(4) The concentration measuring method of the ammonium sulfate solution of the present invention can judge the weight percent concentration of the ammonium sulfate solution by measuring the pH value of the ammonium sulfate solution, and the measurement is simple, fast and accurate.
(5)本发明的硫酸铵溶液的浓度测量方法,藉由先测量或控制硫酸铵溶液的pH值在一设定值范围内(例如pH值介于3~11),然后再测量硫酸铵溶液的导电度,利用导电度与重量百分浓度间的线性对应关系,即可准确判断硫酸铵溶液的重量百分浓度,其测量同样简单快速且准确。(5) the concentration measuring method of ammonium sulfate solution of the present invention, by measuring or controlling the pH value of ammonium sulfate solution earlier in a set value range (for example, pH value is between 3~11), then measure ammonium sulfate solution Conductivity, using the linear correspondence between conductivity and weight percent concentration, can accurately determine the weight percent concentration of ammonium sulfate solution, and its measurement is also simple, fast and accurate.
(6)本发明的硫酸铵溶液的浓度控制方法,藉由控制硫酸溶液中的硫酸量,即可控制该硫酸铵溶液的浓度,其控制方法简单方便、容易实施。(6) The concentration control method of ammonium sulfate solution of the present invention can control the concentration of this ammonium sulfate solution by controlling the amount of sulfuric acid in the sulfuric acid solution, and its control method is simple and convenient, easy to implement.
附图说明Description of drawings
图1为本发明的氨气回收方法的流程图;Fig. 1 is the flow chart of ammonia recovery method of the present invention;
图2为本发明的氨气回收方法的实施方法流程图;Fig. 2 is the implementation method flowchart of ammonia recovery method of the present invention;
图3为本发明的硫酸铵溶液的浓度测量方法的硫酸铵浓度与导电度关系图;Fig. 3 is the ammonium sulfate concentration and electrical conductivity diagram of the concentration measuring method of ammonium sulfate solution of the present invention;
图4为本发明的硫酸铵溶液的浓度测量方法的溶液pH值与导电度关系图;Fig. 4 is the solution pH value of the concentration measuring method of ammonium sulfate solution of the present invention and conductivity relation figure;
图5为依本发明的氨气回收方法的第一实施装置示意图;Fig. 5 is according to the first implementation device schematic diagram of ammonia recovery method of the present invention;
图6为依本发明的氨气回收方法的第二实施装置示意图;Fig. 6 is according to the second implementing device schematic diagram of ammonia recovery method of the present invention;
图7为依本发明的氨气回收方法的氨气回收装置结构图。Fig. 7 is a structural diagram of an ammonia recovery device according to the ammonia recovery method of the present invention.
附图标记说明:Explanation of reference signs:
(31)、(41):反应槽(31), (41): reaction tank
(32)、(42):气体导入口(32), (42): gas inlet
(33)、(43):反应剂(33), (43): Reactant
(34):搅拌器(34): agitator
(44)、(77):循环泵(44), (77): circulation pump
(35)、(45):气体导出口(35), (45): gas outlet
(46):循环管路(46): Circulation pipeline
(48)、(78):填充床(48), (78): packed bed
(71)、(81):废气处理腔体(71), (81): Exhaust gas treatment chamber
(72):废气进入管线(72): Exhaust gas enters the pipeline
(73):硫酸铵排放管线(73): Ammonium sulfate discharge line
(74):处理后废气排放管线(74): Exhaust gas discharge pipeline after treatment
(75):反应剂循环管线(75): Reactant circulation line
(76):硫酸添加管线。(76): Sulfuric acid addition pipeline.
具体实施方式Detailed ways
请参阅图1,其系为本发明的氨气回收方法的流程图。图中,氨气回收方法包含以下步骤:Please refer to Fig. 1, which is a flow chart of the ammonia recovery method of the present invention. Among the figure, the ammonia recovery method comprises the following steps:
步骤一:提供重量百分浓度介于1%~98%的第一硫酸溶液作为反应剂;选择高浓度的第一硫酸作为反应剂能提高反应速率及提高产物浓度。Step 1: providing a first sulfuric acid solution with a concentration of 1%-98% by weight as a reactant; choosing a high-concentration first sulfuric acid as a reactant can increase the reaction rate and increase the product concentration.
步骤二:使氨气与反应剂反应,产生重量百分浓度介于1%~73%的硫酸铵溶液;通入氨气并使之与第一硫酸反应,其反应方程式如下式所示:Step 2: React ammonia gas with the reactant to produce an ammonium sulfate solution with a concentration of 1% to 73% by weight; feed ammonia gas and react it with the first sulfuric acid, the reaction equation is as follows:
NH3(g)+H2O(aq)→NH4OH(aq) NH 3 (g) +H 2 O (aq) →NH 4 OH (aq)
2NH4OH(aq)+H2SO4(aq)→(NH4)2SO4(aq)+2H2O(aq) 2NH 4 OH (aq) +H 2 SO 4(aq) →(NH 4 ) 2 SO 4(aq) +2H 2 O (aq)
净反应:2NH3(g)+H2SO4(aq)→(NH4)2SO4(aq) Net reaction: 2NH 3(g) +H 2 SO 4(aq) →(NH 4 ) 2 SO 4(aq)
式中显示,当完全反应后,反应剂第一硫酸的初始摩尔浓度与产物硫酸铵的最终摩尔浓度相同,藉此提供高浓度硫酸铵作为化学肥料的原料,同时解决习知技艺中氨气回收的缺陷。It is shown in the formula that after the complete reaction, the initial molar concentration of the first sulfuric acid of the reactant is the same as the final molar concentration of the product ammonium sulfate, thereby providing high-concentration ammonium sulfate as a raw material for chemical fertilizers, and simultaneously solving the problem of ammonia recovery in the prior art Defects.
其中,硫酸铵溶液的重量百分浓度较佳为25%,本发明的氨气回收方法的硫酸铵的pH值可作为控制反应终了的判断依据,反应终点的硫酸铵pH值较佳为1~13,更佳为3~11,最佳为7。Wherein, the weight percent concentration of ammonium sulfate solution is preferably 25%, and the pH value of the ammonium sulfate of the ammonia gas recovery method of the present invention can be used as the judging basis that the control reaction ends, and the ammonium sulfate pH value at the end of the reaction is preferably 1~20%. 13, more preferably 3-11, most preferably 7.
请参阅图2,其系为本发明的氨气回收方法的实施方法流程图。图中,氨气回收方法包含以下步骤:Please refer to Fig. 2, which is a flow chart of the implementation method of the ammonia gas recovery method of the present invention. Among the figure, the ammonia recovery method comprises the following steps:
步骤一:提供重量百分浓度介于1%~98%的第一硫酸溶液作为反应剂;选择高浓度的第一硫酸作为反应剂能提高反应速率及提高产物浓度。Step 1: providing a first sulfuric acid solution with a concentration of 1%-98% by weight as a reactant; choosing a high-concentration first sulfuric acid as a reactant can increase the reaction rate and increase the product concentration.
步骤二:将反应剂分散成细小液滴;将反应剂分散成细小液滴能增加反应剂与氨气的接触面积,提高反应速率,实际实施上能以循环管路搭配喷洒装置来实现。Step 2: Dispersing the reactant into fine droplets; dispersing the reactant into fine droplets can increase the contact area between the reactant and ammonia gas and increase the reaction rate. In practice, it can be realized with a circulating pipeline and a spraying device.
步骤三:使氨气与反应剂反应,产生重量百分浓度介于1%~73%的硫酸铵溶液;通入氨气并使之与第一硫酸反应,其反应方程式如下式所示:Step 3: react ammonia gas with the reactant to produce an ammonium sulfate solution with a concentration of 1% to 73% by weight; feed ammonia gas and react it with the first sulfuric acid, the reaction equation is as follows:
NH3(g)+H2O(aq)→NH4OH(aq) NH 3 (g) +H 2 O (aq) →NH 4 OH (aq)
2NH4OH(aq)+H2SO4(aq)→(NH4)2SO4(aq)+2H2O(aq) 2NH 4 OH (aq) +H 2 SO 4(aq) →(NH 4 ) 2 SO 4(aq) +2H 2 O (aq)
净反应:2NH3(g)+H2SO4(aq)→(NH4)2SO4(aq) Net reaction: 2NH 3(g) +H 2 SO 4(aq) →(NH 4 ) 2 SO 4(aq)
式中显示,当完全反应后,反应剂第一硫酸的初始摩尔浓度与产物硫酸铵的最终摩尔浓度相同,藉此提供高浓度硫酸铵作为化学肥料的原料,同时解决习知技艺中氨气回收的缺陷。It is shown in the formula that after the complete reaction, the initial molar concentration of the first sulfuric acid of the reactant is the same as the final molar concentration of the product ammonium sulfate, thereby providing high-concentration ammonium sulfate as a raw material for chemical fertilizers, and simultaneously solving the problem of ammonia recovery in the prior art Defects.
步骤四:分次添加第二硫酸溶液于反应剂中,且第二硫酸溶液的重量百分浓度高于第一硫酸溶液;浓硫酸具有高蒸气压,易挥发,因此在本实施例中选择较低浓度的硫酸作为第一硫酸,随着反应进行,再分次逐渐添加浓度较高的第二硫酸,藉此可维持硫酸浓度不至于太高而造成硫酸逸散之问题,如使用重量百分浓度低于第一硫酸溶液的第二硫酸溶液,亦可驱使反应加速进行。Step 4: Add the second sulfuric acid solution in batches in the reactant, and the weight percent concentration of the second sulfuric acid solution is higher than that of the first sulfuric acid solution; concentrated sulfuric acid has a high vapor pressure and is volatile, so in this embodiment, a higher sulfuric acid solution is selected. Low-concentration sulfuric acid is used as the first sulfuric acid. As the reaction progresses, the second sulfuric acid with higher concentration is gradually added in stages, so as to maintain the concentration of sulfuric acid from being too high and cause the problem of sulfuric acid escape. For example, use weight percent The second sulfuric acid solution having a lower concentration than the first sulfuric acid solution can also accelerate the reaction.
其中,硫酸铵溶液的重量百分浓度较佳为25%,本发明的氨气回收方法的硫酸铵之pH值可作为控制反应终了的判断依据,反应终点的硫酸铵pH值较佳为1~13,更佳为3~11,最佳为7。Wherein, the weight percent concentration of ammonium sulfate solution is preferably 25%, and the pH value of the ammonium sulfate of the ammonia gas recovery method of the present invention can be used as the judging basis that the control reaction ends, and the ammonium sulfate pH value at the end of the reaction is preferably 1~ 13, more preferably 3-11, most preferably 7.
本发明的硫酸铵溶液的浓度测量方法,是藉由测量硫酸铵溶液的pH值以判断硫酸铵溶液的重量百分浓度是否符合一默认值,硫酸铵溶液是以氨气与重量百分浓度介于1%~98%的硫酸溶液反应生成,当氨气与硫酸溶液反应时,溶液中硫酸含量减少,整体pH值上升,利用硫酸铵溶液的pH值与重量百分浓度建立一校正曲线后,即可以硫酸铵溶液的pH值判断硫酸铵溶液的重量百分浓度是否符合一默认值,该默认值是为了使反应产生的硫酸铵溶液能直接供应作为化学肥料的原料而无需另外浓缩处理步骤,默认值较佳为1%以上,硫酸铵溶液的重量百分浓度较佳为介于1%~73%,更佳为25%。The concentration measuring method of ammonium sulfate solution of the present invention is to judge whether the weight percent concentration of ammonium sulfate solution meets a default value by measuring the pH value of ammonium sulfate solution, and ammonium sulfate solution is based on ammonia gas and weight percent concentration. It is formed by the reaction of 1% to 98% sulfuric acid solution. When ammonia gas reacts with sulfuric acid solution, the sulfuric acid content in the solution decreases and the overall pH value increases. After establishing a calibration curve using the pH value and weight percent concentration of the ammonium sulfate solution, That is, the pH value of the ammonium sulfate solution can be used to determine whether the weight percent concentration of the ammonium sulfate solution meets a default value, and the default value is to make the ammonium sulfate solution produced by the reaction directly supply as a raw material for chemical fertilizers without additional concentration treatment steps, The default value is preferably above 1%, and the weight percent concentration of the ammonium sulfate solution is preferably between 1% and 73%, more preferably 25%.
其中,较佳为硫酸铵溶液的pH值介于1~13时,氨气与硫酸溶液的反应接近反应终点,更佳为硫酸铵溶液的pH值介于3~11时,氨气与硫酸溶液的反应接近反应终点,最佳为硫酸铵溶液的pH值为7时,氨气与硫酸溶液的反应到达反应终点。Among them, when the pH value of the ammonium sulfate solution is preferably between 1 and 13, the reaction of ammonia gas and sulfuric acid solution is close to the end of the reaction, more preferably when the pH value of the ammonium sulfate solution is between 3 and 11, the reaction between ammonia gas and sulfuric acid solution The reaction is close to the end of the reaction, when the pH value of the ammonium sulfate solution is optimally 7, the reaction of ammonia and sulfuric acid solution reaches the end of the reaction.
本发明的硫酸铵溶液的浓度测量方法,是藉由测量硫酸铵溶液的导电度以判断硫酸铵溶液的重量百分浓度,硫酸铵溶液是以氨气与重量百分浓度介于1%~98%的硫酸溶液反应生成,当氨气与硫酸溶液反应时,随着溶液中硫酸含量减少,硫酸铵逐渐生成,整体pH值上升,当反应进行至系统溶液的pH值高于3时,系统溶液的导电度主要来自硫酸铵解离出的自由离子,此时只要测量硫酸铵的导电度,即可获知硫酸铵的重量百分浓度。亦即,本发明以导电度进行硫酸铵的浓度测量,如搭配测量或控制硫酸铵的pH值,可以增加正确性。上述的测量或控制硫酸铵的pH值,系指硫酸铵的pH值介于1~13,或是pH值介于3~11,较佳为pH值为7。The concentration measuring method of ammonium sulfate solution of the present invention is to judge the weight percent concentration of ammonium sulfate solution by measuring the conductivity of ammonium sulfate solution, and ammonium sulfate solution is between 1%~98% with ammonia gas and weight percent concentration. % of sulfuric acid solution reacts to generate, when ammonia reacts with sulfuric acid solution, ammonium sulfate is gradually generated as the sulfuric acid content in the solution decreases, and the overall pH value rises, when the reaction proceeds until the pH value of the system solution is higher than 3, the system solution The electrical conductivity of ammonium sulfate mainly comes from the free ions dissociated from ammonium sulfate. At this time, as long as the conductivity of ammonium sulfate is measured, the weight percent concentration of ammonium sulfate can be known. That is to say, the present invention measures the concentration of ammonium sulfate with electrical conductivity, such as matching with measuring or controlling the pH value of ammonium sulfate, which can increase the accuracy. The above-mentioned measurement or control of the pH value of ammonium sulfate means that the pH value of the ammonium sulfate is between 1-13, or the pH value is between 3-11, preferably the pH value is 7.
上述硫酸铵溶液的浓度测量方法,利用硫酸铵溶液的导电度与重量百分浓度间的线性关系,在硫酸铵的pH值符合一默认值的前提下,以硫酸铵溶液的导电度判断硫酸铵溶液的重量百分浓度,硫酸铵浓度与导电度的关系图系如图3所示,硫酸溶液pH值与导电度关系图系如图4所示,而该硫酸铵溶液的重量百分浓度,其默认值较佳为1%以上,硫酸铵溶液的重量百分浓度较佳为介于1%~73%,更佳为25%。The concentration measuring method of the above-mentioned ammonium sulfate solution utilizes the linear relationship between the conductivity of the ammonium sulfate solution and the weight percent concentration, and under the premise that the pH value of the ammonium sulfate meets a default value, the conductivity of the ammonium sulfate solution is used to judge the ammonium sulfate The weight percent concentration of solution, the relationship diagram of ammonium sulfate concentration and conductivity is as shown in Figure 3, the sulfuric acid solution pH value and conductivity relationship diagram is as shown in Figure 4, and the weight percent concentration of this ammonium sulfate solution, Its default value is preferably above 1%, and the weight percent concentration of the ammonium sulfate solution is preferably between 1% and 73%, more preferably 25%.
本发明的硫酸铵溶液的浓度控制方法,其硫酸铵溶液系以氨气与重量百分浓度介于1%~98%的硫酸溶液反应生成,藉由控制硫酸溶液中的硫酸量,以控制该硫酸铵溶液的浓度。The concentration control method of the ammonium sulfate solution of the present invention, its ammonium sulfate solution is generated by the reaction of ammonia gas and a sulfuric acid solution with a concentration of 1% to 98% by weight, by controlling the amount of sulfuric acid in the sulfuric acid solution, to control the concentration of ammonium sulfate solution.
其中,较佳为硫酸铵溶液的重量百分浓度介于1%~73%,更佳为硫酸铵溶液的重量百分浓度为25%。较佳为硫酸铵溶液的pH值介于1~13时,氨气与硫酸溶液的反应接近反应终点,更佳为硫酸铵溶液的pH值介于3~11时,氨气与硫酸溶液的反应接近反应终点,最佳为硫酸铵溶液的pH值为7时,氨气与硫酸溶液的反应到达反应终点。Among them, preferably the weight percent concentration of the ammonium sulfate solution is between 1% and 73%, more preferably the weight percent concentration of the ammonium sulfate solution is 25%. Preferably when the pH value of the ammonium sulfate solution is between 1 and 13, the reaction of ammonia gas and sulfuric acid solution is close to the end of the reaction, more preferably when the pH value of the ammonium sulfate solution is between 3 and 11, the reaction of ammonia gas and sulfuric acid solution Near the end of the reaction, preferably when the pH of the ammonium sulfate solution is 7, the reaction of ammonia gas and sulfuric acid solution reaches the end of the reaction.
请参阅图5,其系为依本发明的氨气回收方法的第一实施装置示意图,系一利用「批次反应」以进行氨气回收的实施方式,意即持续排入的氨气与反应剂33在反应告一段落后予以清空反应槽31,再重新填入新的反应剂33以与后续排入的氨气进行下一批次的反应。图中,第一实施装置包含反应槽31、气体导入口32、反应剂33、搅拌器34及气体导出口35。含氨工业废气由气体导入口32导入反应槽31中,气体导入口32位于反应槽31之一侧面下方,且高度位于反应剂33液面之下,当含氨工业废气进入反应槽31时接触到反应剂33即开始产生反应,反应槽31底部具有一搅拌器34,浸于反应剂33内,用于搅拌反应剂33加速含氨工业废气及反应剂33的反应,并使其反应完全,无法溶于反应剂33的其余工业废气由气体导出口35排出反应槽31。Please refer to Fig. 5, which is a schematic diagram of the first implementing device according to the ammonia gas recovery method of the present invention, which is an embodiment of using "batch reaction" to carry out ammonia gas recovery, that is, the continuously discharged ammonia gas and the reaction The
请参阅图6,其系为依本发明的氨气回收方法的第二实施装置示意图,亦为一利用「批次反应」以进行氨气回收的实施方式。图中,第二实施装置包含反应槽41、气体导入口42、反应剂43、循环泵44、气体导出口45、循环管路46、喷洒装置47及填充床48。含氨工业废气由气体导入口42导入反应槽41中,气体导入口42位于反应槽41的一侧面下方,且高度位于反应剂43液面之上,循环管路46位于反应槽41的另一侧面下方,且高度位于反应剂43液面之下,使反应剂43经循环管路46及循环泵44加压后,由反应槽41顶端的喷洒装置47分散成细小液滴向下洒落,并藉由填充床48增加与含氨工业废气的接触面积,当含氨工业废气进入反应槽41时接触到由喷洒装置47洒落的反应剂43即开始产生反应,设置于反应槽41内且位于反应剂43液面之上的填充床48增加反应剂43及含氨工业废气接触面积提升反应速率,而无法溶于反应剂43之其余工业废气由气体导出口45排出反应槽41。Please refer to FIG. 6 , which is a schematic diagram of the second implementation device of the ammonia gas recovery method according to the present invention, and is also an embodiment of utilizing "batch reaction" for ammonia gas recovery. In the figure, the second implementation device includes a
请参阅图7,其系为依本发明的氨气回收方法的氨气回收装置结构图,其系一利用「连续式反应」以进行氨气回收之方法,意即在反应之初,先将硫酸充填于废气处理腔体71,然后持续导入含氨工业废气已进行第一阶段的反应,直至硫酸铵的pH值达一设定值,例如pH值为3,此后,含氨工业废气持续导入废气处理腔体71,而反应剂(即硫酸)亦持续导入废气处理腔体71,以维持硫酸铵的pH值为3,此时,硫酸铵即可持续排放而形成「连续式反应」。图中,氨气回收装置包含废气处理腔体71、废气进入管线72、硫酸铵排放管线73、处理后废气排放管线74、反应剂循环管线75、硫酸添加管线76、循环泵77及填充床78。含氨工业废气由废气进入管线72导入废气处理腔体71中,废气进入管线72位于废气处理腔体71的一侧面下方,反应剂循环管线75位于废气处理腔体71的另一侧面下方,使反应剂经反应剂循环管线75由废气处理腔体71上方向下洒落,并藉由填充床78增加与含氨工业废气的接触面积,当含氨工业废气进入废气处理腔体71时接触到洒落的反应剂即开始产生反应,设置于废气处理腔体71内的填充床78更进一步增加反应剂及含氨工业废气接触面积以提升反应速率,反应经过一段时间后可由硫酸添加管线76加入硫酸,使反应加速进行,当硫酸铵浓度到达默认值,可让硫酸铵从硫酸铵排放管线73排出,其余工业废气由处理后废气排放管线74排出。Please refer to Fig. 7, which is a structural diagram of an ammonia gas recovery device according to the ammonia gas recovery method of the present invention, which is a method for utilizing "continuous reaction" to carry out ammonia gas recovery, that is, at the beginning of the reaction, the Sulfuric acid is filled in the waste gas treatment chamber 71, and then the ammonia-containing industrial waste gas is continuously introduced to carry out the first-stage reaction until the pH value of ammonium sulfate reaches a set value, for example, the pH value is 3. After that, the ammonia-containing industrial waste gas is continuously introduced The exhaust gas treatment chamber 71, and the reactant (ie sulfuric acid) is continuously introduced into the exhaust gas treatment chamber 71 to maintain the pH value of the ammonium sulfate at 3. At this time, the ammonium sulfate can be continuously discharged to form a "continuous reaction". In the figure, the ammonia gas recovery device includes a waste gas treatment chamber 71, a waste gas inlet pipeline 72, an ammonium sulfate discharge pipeline 73, a treated waste gas discharge pipeline 74, a reactant circulation pipeline 75, a sulfuric acid addition pipeline 76, a circulation pump 77 and a packed bed 78 . Ammonia-containing industrial waste gas is introduced into the waste gas treatment chamber 71 through the waste gas inlet pipeline 72, the waste gas inlet pipeline 72 is located under one side of the waste gas treatment chamber 71, and the reactant circulation pipeline 75 is located under the other side of the waste gas treatment chamber 71, so that The reactant is sprayed down from the top of the waste gas treatment chamber 71 through the reactant circulation pipeline 75, and the contact area with the ammonia-containing industrial waste gas is increased by the packed bed 78. When the ammonia-containing industrial waste gas enters the waste gas treatment chamber 71, it is exposed The reactant immediately starts to react, and the packed bed 78 arranged in the waste gas treatment cavity 71 further increases the contact area between the reactant and the ammonia-containing industrial waste gas to increase the reaction rate. After a period of time, sulfuric acid can be added through the sulfuric acid addition pipeline 76, The reaction is accelerated, and when the ammonium sulfate concentration reaches the default value, the ammonium sulfate can be discharged from the ammonium sulfate discharge pipeline 73, and the remaining industrial waste gas is discharged from the treated waste gas discharge pipeline 74.
以上所述仅为举例性,而非为限制性者。任何未脱离本发明之精神与范畴,而对其进行之等效修改或变更,均应包含于后附之申请专利范围中。The above descriptions are illustrative only, not restrictive. Any equivalent modification or change made without departing from the spirit and scope of the present invention shall be included in the scope of the appended patent application.
Claims (18)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 201010622614 CN102107887A (en) | 2010-12-16 | 2010-12-16 | Ammonia gas recovery method, ammonium sulfate solution concentration measurement method and ammonium sulfate solution concentration control method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 201010622614 CN102107887A (en) | 2010-12-16 | 2010-12-16 | Ammonia gas recovery method, ammonium sulfate solution concentration measurement method and ammonium sulfate solution concentration control method |
Publications (1)
Publication Number | Publication Date |
---|---|
CN102107887A true CN102107887A (en) | 2011-06-29 |
Family
ID=44172185
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN 201010622614 Pending CN102107887A (en) | 2010-12-16 | 2010-12-16 | Ammonia gas recovery method, ammonium sulfate solution concentration measurement method and ammonium sulfate solution concentration control method |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN102107887A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102328936A (en) * | 2011-09-07 | 2012-01-25 | 四川明晶光电科技有限公司 | Method for treating ammonia gas wastewater |
EP2980066A4 (en) * | 2013-03-29 | 2016-11-23 | Asahi Kasei Chemicals Corp | PROCESS FOR PRODUCING ISOCYANATE |
CN113230833A (en) * | 2021-05-28 | 2021-08-10 | 中冶华天工程技术有限公司 | Novel ammonia absorption and crystallized salt separation method |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1172070A (en) * | 1997-07-11 | 1998-02-04 | 王天伦 | Method for producing ammonium sulfate by using waste ammonia water |
CN101734813A (en) * | 2009-12-21 | 2010-06-16 | 山东大明消毒科技有限公司 | Technology for recovering ammonium sulfate by waste acid pickle generated in process of producing cyanuric acid and equipment therefor |
-
2010
- 2010-12-16 CN CN 201010622614 patent/CN102107887A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1172070A (en) * | 1997-07-11 | 1998-02-04 | 王天伦 | Method for producing ammonium sulfate by using waste ammonia water |
CN101734813A (en) * | 2009-12-21 | 2010-06-16 | 山东大明消毒科技有限公司 | Technology for recovering ammonium sulfate by waste acid pickle generated in process of producing cyanuric acid and equipment therefor |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102328936A (en) * | 2011-09-07 | 2012-01-25 | 四川明晶光电科技有限公司 | Method for treating ammonia gas wastewater |
CN102328936B (en) * | 2011-09-07 | 2012-11-21 | 四川明晶光电科技有限公司 | Method for treating ammonia gas wastewater |
EP2980066A4 (en) * | 2013-03-29 | 2016-11-23 | Asahi Kasei Chemicals Corp | PROCESS FOR PRODUCING ISOCYANATE |
US9714215B2 (en) | 2013-03-29 | 2017-07-25 | Asahi Kasei Chemicals Corporation | Method for producing isocyanate |
EP3838892A1 (en) * | 2013-03-29 | 2021-06-23 | Asahi Kasei Kabushiki Kaisha | Method for producing isocyanate |
CN113230833A (en) * | 2021-05-28 | 2021-08-10 | 中冶华天工程技术有限公司 | Novel ammonia absorption and crystallized salt separation method |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN102378736B (en) | The method and apparatus of preparation molecular bromine | |
EP3126544B1 (en) | Oxidation of copper in a copper etching solution by the use of oxygen and/or air as an oxidizing agent | |
CN104445751A (en) | Method for recycling and treating cyanide waste water | |
JP2009209041A (en) | Method of purifying phosphoric acid, and high-purity polyphosphoric acid | |
CN102107887A (en) | Ammonia gas recovery method, ammonium sulfate solution concentration measurement method and ammonium sulfate solution concentration control method | |
CN104193058B (en) | A kind of gold mine cyanide wastewater comprehensive processing method | |
CN104529013A (en) | Cyanide-containing waste water recovery and treatment method | |
KR20210034091A (en) | System and method for measuring the composition of water | |
JP4793407B2 (en) | Method and apparatus for treating waste gas containing chloropolysilane | |
CN106219853A (en) | The continuous treatment process of cyanide wastewater | |
TW201226310A (en) | Ammonia gas recovery method, concentration measurement method of ammonium sulfate solution, and concentration control method of ammonium sulfate solution | |
TWI517894B (en) | Ammonia recovery method, concentration measurement method of monoammonium phosphate solution and concentration control method of monoammonium phosphate solution | |
KR101529048B1 (en) | The Method of Removing Residual Dissolved Ozone Treated Water for Ozone and the Device thereof | |
CN104986743A (en) | Bleaching process and device used in nitric acid preparation process | |
CN106241890A (en) | A kind of production method of bodied ferric sulfate | |
EP0432250B1 (en) | Process for reducing the cyanide content of a solution | |
CN105668761B (en) | A kind of method and apparatus removing organic matter and intermediate valence state metal ion in the high acid system of high temperature | |
CN104193040B (en) | A kind of gold mine cyanide wastewater integrated conduct method | |
JP2010162437A (en) | Detoxification apparatus and detoxification method of fluorine-containing waste liquid | |
CN210559875U (en) | Waste acid recovery processing device | |
CN108290113A (en) | The processing method of exhaust gas containing fluorine element | |
CN108348850A (en) | The processing method of exhaust gas containing fluorine element | |
Chen et al. | Dynamic model of ozone contacting process with oxygen mass transfer in bubble columns | |
US20240149210A1 (en) | Combination carbon monoxide and nitrogen dioxide scrubber treatment and process | |
CN219098874U (en) | Break point chlorination reactor |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C02 | Deemed withdrawal of patent application after publication (patent law 2001) | ||
WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20110629 |